Patent Application
20050132883
The present invention relates to an acid gas scrubbing apparatus and method, and more particularly to an acid gas scrubbing apparatus and method in which a gas, to be scrubbed, containing carbon dioxide is brought into contact with a gas scrubbing liquid containing alkaline agent and cooled, and acid gases in the gas are removed.
In the case where combustible wastes are combusted or gasified, a combustion gas or a produced gas generated by combustion or gasification (hereinafter referred to as “gas to be scrubbed”) contains acid gases such as hydrogen chloride, sulfur oxides, nitrogen oxides and hydrogen sulfide. In many cases, the gas to be scrubbed contains a trace amount of these acid gases in the order of ppm. However, even the trace amount of acid gases are toxic to the human body, and such acid gases are corrosive to gas treatment facilities and poisonous to various catalysts, and hence it is necessary to remove such acid gases.
As a means for removing acid gases, a general treatment method is that acid gases are neutralized and absorbed by bringing acid gases into contact with solid or liquid alkaline agent. In a wet-type scrubbing method in which the gas to be scrubbed is brought into contact with alkaline solution, as a pH of alkaline solution is kept higher, the absorption and removal capability of acid gases becomes higher. In many cases, a combustion gas or a produced gas obtained by combustion or gasification of combustible wastes contains carbon dioxide, and the concentration of carbon dioxide is in the range from several percent to ten plus several percent or more and is much higher than the concentration of acid gases of several ppm. Therefore, when acid gases are neutralized by alkaline agent, because carbon dioxide reacts with alkaline agent and consumes alkaline agent, a large amount of alkaline agent is necessary to maintain a pH high enough to remove acid gases. Therefore, conventionally, an absorption and removal capability of acid gases must be sacrificed for the economical reason.
In the wet-scrubbing method, since heat exchange between a gas to be scrubbed and a scrubbing liquid is carried out, in the case of scrubbing a high-temperature gas, it is necessary to cool the scrubbing liquid. However, when a high-temperature gas is scrubbed in a wet-type scrubber operated at atmospheric pressure, heat recovered by the scrubbing liquid from the gas to be scrubbed is low temperature heat having a temperature of 100° C. or lower, and hence in most cases, such recovered heat is discharged to the atmosphere in a cooling tower or the like, and is not utilized effectively.
In recent years, dioxins generated in incinerators are one of society's problems, and it is said that the main cause of the generation of dioxins is a resynthesis reaction of dioxins in the temperature range of 250 to 500° C. in the presence of catalytic incineration ash. Therefore, a system in which gases are rapidly cooled from a temperature equal to or higher than that of dioxins resynthesis to a desired temperature is expected to be widespread in the future, and there is a high possibility that a wet-type scrubbing method will be employed as this rapid cooling system. In this case, since a large quantity of low-temperature waste heat is generated, a means for effectively utilizing this low-temperature waste heat has been desired.
On the other hand, for the reason of generation of dioxins or shortage of landfill sites, as a treatment method of combustible wastes, a gasification and melting system in which combustibles are pyrolyzed and gasified, and a produced gas and fly ash are supplied to a high-temperature melting furnace and melted into slag therein is becoming widespread. In such gasification and slagging combustion system, steam or a gas such as carbon dioxide is necessary as a diluent of oxygen for partial combustion.
Particularly, in the case of using a fluidized-bed furnace as a gasification furnace, it is necessary to supply a certain amount of fluidizing gas for the purpose of maintaining fluidization of a fluidized medium. Because such fluidizing gas is also used as an oxidizing agent, in some cases where air is used as a fluidizing gas and combustible wastes having a high calorific value are raw materials, oxygen becomes excessive even in a minimum amount of air supplied for maintaining fluidization of the fluidized medium, and hence a gas serving as a regulator of oxygen concentration in the fluidizing gas is necessary.
Further, an attempt to gasify combustible wastes without complete combustion and utilize a produced gas as a fuel gas is being made at present, and hence there is an increasing demand for steam and carbon dioxide as a supply source for a gasifying agent, i.e., hydrogen atoms and oxygen atoms. Further, in recent years, an attempt to produce hydrogen by further refining the fuel gas obtained by the above process and generate electricity by supplying the produced hydrogen to a fuel cell has been made. In this case, if an amount of carbon dioxide and nitrogen contained in the fuel gas is increased, power consumption required for refining the fuel gas is increased, and hence how to reduce the amount of carbon dioxide and nitrogen contained in the produced gas is becoming an important subject.
Because a large amount of low-temperature waste heat is generated in the wet-type scrubber, if there is a load, such as a regional heat supply, then such low-temperature waste heat can be effectively utilized. However, in general, an incineration plant of wastes is located away from residential areas, and there is no effective place for utilizing such waste heat. Thus, in the actual circumstances, such low-temperature waste heat is utilized by constructing a heated pool or a green house deliberately adjacent to the incineration plant.
On the other hand, because a gas treatment requires a highly advanced treatment year by year, consumption of energy is increasing in actuality as in the case where a high-quality steam is used as a diluting gas of oxygen gas as described above.
The present invention has been made in view of the above, and it is therefore an object of the present invention to provide an acid gas scrubbing apparatus and method which can increase energy efficiency and improve an acid gas removal capability in a wet-type scrubber greatly by effectively utilizing low-temperature waste heat of the wet-type scrubber to generate steam and carbon dioxide.
Another object of the present invention is to provide a gasification system of combustibles which combines the above acid gas scrubbing apparatus and a gasification apparatus, an incineration system of combustibles which combines the above acid gas scrubbing apparatus and an incinerator, and a fuel cell power generation system by gasification of combustibles which combines the above gasification system of combustibles and a fuel cell power generation system.
In order to achieve the above object, an acid gas scrubbing apparatus according to the present invention comprises a gas scrubber which brings a gas to be scrubbed into contact with alkaline solution, and a regenerator having a cooling function of alkaline solution and a regeneration function of alkalis.
According to the present invention, in a method for removing acid gases in a gas, to be scrubbed, containing carbon dioxide by bringing the gas to be scrubbed into contact with a gas scrubbing liquid containing alkaline agent, an acid gas scrubbing method is characterized in that: the gas scrubbing liquid is regenerated by bringing the gas scrubbing liquid into contact with a regenerating gas having components different from the gas to be scrubbed, and the regenerated gas scrubbing liquid is used as a scrubbing liquid of the gas, to be scrubbed, containing carbon dioxide.
A gas, to be scrubbed, supplied to a gas scrubber is brought into contact with a scrubbing liquid comprising alkaline solution in a countercurrent flow, and acid gases and carbon dioxide in the gas to be scrubbed are absorbed in the scrubbing liquid. Dust components in the gas to be scrubbed are also entrapped into the scrubbing liquid, and the scrubbed gas becomes a clean gas composed mainly of oxygen, carbon monoxide, hydrogen, and saturated steam which have a small solubility in alkaline solution, and carbon dioxide which has not been dissolved in alkaline solution.
The alkaline scrubbing liquid which has absorbed acid gases and carbon dioxide is sent into a regenerator where the scrubbing liquid is brought into contact with a regenerating gas, such as air, having different components from the gas to be scrubbed to generate steam until a pressure in the regenerator reaches a saturated aqueous vapor pressure at a temperature in the regenerator.
The saturated aqueous vapor pressure is shown in Table 1.
For example, when the regenerator is operated at an atmospheric pressure (about 0.1 PMa (1 bar)) and a temperature of 80° C., a regenerator vent gas discharged from the regenerator accompanies 47% of steam. With vaporization of steam, the scrubbing liquid is deprived of latent heat of vaporization and is cooled. It should be noted that when the regenerating gas accompanies steam whose amount is equal to or greater than the amount corresponding to saturated aqueous vapor pressure in the regenerator, water will not vaporize and the scrubbing liquid will not be cooled in the regenerator.
Further, if a gas containing no carbon dioxide is used as a regenerating gas or an operating pressure of the regenerator is lower than that of the gas scrubber, then carbon dioxide is desorbed and released from alkaline scrubbing liquid in the regenerator due to the difference of partial pressure of carbon dioxide in a gas-phase section of the regenerator. The pH of alkaline scrubbing liquid is increased by releasing of carbon dioxide, and an absorbing capability of acid gases in the alkaline scrubbing liquid is recovered again.
The regenerator vent gas which accompanies steam and desorbed carbon dioxide can be used as a gasifying agent for gasifying the above combustibles and a diluting gas of an oxidizing agent. Further, if air or oxygen is used as a regenerating gas, then the regenerator vent gas can be utilized as a mixed gas of an oxidizing agent and a gasifying agent as it is.
The alkaline scrubbing liquid which has recovered an acid gas absorption function is sent again to the gas scrubber. In the case of using air as a regenerating gas, if water is vaporized from the scrubbing liquid in the regenerator, or a part of the scrubbing liquid is always blown, then it is necessary to replenish a gas scrubbing liquid. This make-up liquid should be a clean liquid which is cleaner than the circulating scrubbing liquid, and hence it is desirable that such make-up liquid is supplied together with make-up alkaline agent to the uppermost section of the gas scrubber, i.e., the most downstream location of stream of the gas to be scrubbed for thereby enhancing the gas scrubbing effect.
With the progress of gas scrubbing, since salts produced by an absorption reaction of acid gases are gradually concentrated in the gas scrubbing liquid, it is necessary to blow the gas scrubbing liquid to prevent salts from being concentrated. Further, also, in the case where the rate of steam accompanied by the gas to be scrubbed is high and the amount of the scrubbing liquid increases, it is necessary to blow the scrubbing liquid. However, if the scrubbing liquid is blown as it is, alkaline agent is also discharged together with the scrubbing liquid, and hence care, such as disposal of the scrubbing liquid after concentration, should be taken.
In order to enhance the gas scrubbing effect by enhancing a regeneration degree of alkali of the scrubbing liquid as much as possible, it is effective to provide regenerators in a multistage manner, such as in a series connection. This is because when a chemical reaction is continuously caused, if reaction time is the same, then the rate of reaction in multistage reactors in which reactions are sequentially caused is higher than that in a single perfect-mixing reactor. If the gas to be scrubbed is brought into contact with a scrubbing liquid in a countercurrent flow in a regenerator, the effect in the regenerator comparable to the multistage regenerators can be obtained. However, since mixing of the scrubbing liquid in a flow direction cannot be avoided, the regeneration degree of alkali in the regenerator is lower than that in the multistage regenerators.
If plural kinds of gases having different gas components from each other can be utilized as a regenerating gas, then individual regenerators serve as regenerators having different purposes by providing independent regenerators which can deal with respective regenerating gases. Further, by using the respective regenerators sequentially in a fully worked-out order, a high-quality regeneration can be achieved.
Further, in an acid gas scrubbing apparatus according to the present invention, a gas scrubber and a scrubbing liquid regenerator may be divided into a two-stage constitution, respectively. Specifically, the acid gas scrubbing apparatus may comprise a first gas scrubbing section in which a gas to be scrubbed is brought into contact with a first gas scrubbing liquid containing first alkaline agent in a countercurrent flow, a second gas scrubbing section in which the scrubbed gas discharged from the first gas scrubbing section is brought into contact with a second gas scrubbing liquid containing second alkaline agent in a countercurrent flow, a first -scrubbing liquid regenerator in which a first regenerating gas having different components from those of the gas to be scrubbed is brought into contact with the first gas scrubbing liquid, a second scrubbing liquid regenerator in which a second regenerating gas having different components from those of the gas to be scrubbed is brought into contact with the second gas scrubbing liquid, a circulating means provided between the first gas scrubbing section and the first scrubbing liquid regenerator for circulating the first scrubbing liquid, and a circulating means provided between the second gas scrubbing section and the second scrubbing liquid regenerator for circulating the second scrubbing liquid.
An embodiment of the present invention will be described with reference to
In the case where the gas to be scrubbed is exhaust gas generated by incineration of wastes containing chlorine such as municipal wastes, the temperature of the gas, to be scrubbed, supplied to the gas scrubber A is normally about 200° C. However, this temperature has passed through the temperature range of resynthesis of dioxins, i.e., around 300° C. and around 470° C., and hence there is a high possibility that the gas to be scrubbed contains dioxins, and dioxins are transferred to the scrubbing liquid and condensed therein. Therefore, in the case of scrubbing exhaust gas generated by incineration of wastes containing chlorine such as municipal wastes, the temperature of the gas 30, to be scrubbed, supplied to the gas scrubber A is 480° C. or higher, preferably 500° C. or higher for the purpose of avoiding the temperature range of resynthesis of dioxins.
In the case where the gas to be scrubbed is a gasified gas obtained by pyrolysis and gasification of wastes containing chlorine such as municipal wastes, the possibility of resynthesis of dioxins is extremely low because of a reducing atmosphere. Therefore, the gas to be scrubbed may be supplied to the gas scrubber A at a temperature of about 200° C., preferably 300° C. or higher, more preferably 350° C. or higher, and still more preferably 500° C. or higher.
Although both of organic alkali and inorganic alkali may be supplied to the scrubbing liquid as alkaline agent, it may be better to use an inorganic alkaline compound from the viewpoint of thermal stability. Particularly, hydroxide of alkali metal, such as sodium hydroxide or potassium hydroxide, is desirable. Further, carbonate of alkali metal, such as sodium carbonate or potassium carbonate, may be used. As an example, in the case of using K2CO3 as alkaline agent, absorption reaction formulas in the gas scrubber are expressed as follows:
K2CO3+H2S→KHS+KHCO3 (1)
K2CO3+H2O+COS→KHS+KHCO3+CO2 (2)
K2CO3+HCl→KHCO3+KCl (3)
K2CO3+SO2+H2O→KHCO3+KHSO3 (4)
K2CO3+NO2+H2O→KHCO3+KHNO3 (5)
K2CO3+H2O+CO2→2KHCO3 (6)
Since the above absorption reaction is an exothermic reaction, the lower the temperature of the scrubbing liquid is, the more advantageous absorption is. For example, if a gas pressure is atmospheric pressure (1 atmosphere), it is sufficient for the temperature TLAI of the scrubbing liquid at the inlet of the gas scrubber A to be 100° C. or lower. However, the temperature TLAI of the scrubbing liquid at the inlet of the gas scrubber A is preferably 80° C. or lower, more preferably in the range of 60 to 75° C. so that steam which has been brought by the gas to be scrubbed is condensed as much as possible. As a result, partial pressure of carbon dioxide in gas-phase is kept high, and as much carbon dioxide as possible is absorbed in the scrubbing liquid.
The temperature TLAE of the scrubbing liquid at the lower part of the gas scrubber A is naturally higher than the temperature of the scrubbing liquid at the upper part of the gas scrubber A because the scrubbing liquid is heated by the gas to be scrubbed, and the temperature difference between TLAE and TLAI is 20° C. or lower, preferably 10° C. or lower. The reason why there is a limit to this temperature difference is that if TLAE is excessively high, carbon dioxide which has been absorbed by the scrubbing liquid is desorbed again in the lower part of the gas scrubber A, and an absorption capability of carbon dioxide in the gas scrubber A is lowered. The control of this temperature difference is performed by adjusting the amount of the circulating scrubbing liquid. In the lower part of the gas scrubber A, steam contained in the gas 30 to be scrubbed is rapidly cooled by contact with the scrubbing liquid and is condensed, and then further condensed due to temperature drop while flowing upward. Therefore, even if absorption of CO2 proceeds in the absorption tower, lowering of the partial pressure of CO2 is small and the partial pressure of CO2 is kept high. Thus, CO2 absorption, the driving force of the scrubbing liquid, is kept high, and the absorption effect is enhanced.
In this manner, by condensation of steam contained in the gas in the gas scrubber A, latent heat of steam can be recovered and CO2 absorption effect in the gas scrubber A can be increased. Therefore, it is important to keep the temperature TLAI of the scrubbing liquid at the inlet of the gas scrubber A, the temperature TLAE of the scrubbing liquid at the lower part of the gas scrubber A, and the temperature difference between TLAE and TLAI, in a proper range, respectively. As it is known from the above description, with regard to components of the gas 30 to be scrubbed, if CO2 content is constant, as steam content is higher, i.e., the rate of carbon dioxide in a dry gas is higher, absorption condition of CO2 in the gas scrubber of the present invention is more advantageous. The scrubbed gas 30 is further scrubbed by a make-up scrubbing liquid 41a, comprising a relatively clean make-up liquid 45a and alkaline agent 46 added to the make-up liquid 45a, which is supplied as a make-up liquid, and then mist in the gas 30 is removed in a mist separator 6a, resulting in a clean scrubbed gas 31. In the case where the gas 30 to be scrubbed is incineration exhaust gas, prevention of white plume emission, such as removal of condensed water by cooling, is applied to the scrubbed gas 31, and then the scrubbed gas 31 is released to the atmosphere. If the gas 30 to be scrubbed is a useful gas containing combustible gas components, the scrubbed gas 31 can be utilized in various ways including as a fuel gas.
In order to increase the efficiency of contact of the gas to be scrubbed with the scrubbing liquid, it is desirable that the scrubbing liquid is supplied by a spraying system so that a contacting surface area in the liquid side which contacts gas is increased and the scrubbing liquid is spread over the entire surface of the gas passage within the gas scrubber A. However, the efficiency of gas-liquid contact may be increased by charging the gas scrubber A with a packing 5a for promotion of contact without a special means for supplying a scrubbing liquid. Naturally, it is more preferable that the scrubbing liquid is supplied by the spraying system and the packing 5a for promotion of contact is used.
The scrubbing liquid 40a, which is withdrawn from the lower part of the gas scrubber A, is supplied to a regenerator B by a circulating pump 4a. If dust is contained in the gas to be scrubbed, it is necessary to take measures so as to accompany as little dust as possible when the scrubbing liquid is withdrawn from the gas scrubber. For example, the scrubbing liquid may be withdrawn from the side of the lower part of the gas scrubber A, and a settling tank 8 for precipitating and separating solid content such as dust may be provided at the location below the gas scrubber A in a vertical direction. If a concentration of dust in the gas 30 to be scrubbed is high and a load of dust flowing into the gas scrubber A is excessively large, then it is desirable that a dry-type dust collector 7 such as a cyclone, a bag filter, or a ceramic filter is provided upstream of the gas scrubber A to reduce the load of dust on the gas scrubber.
A regenerating gas 35b is supplied into the regenerator B from the lower part thereof, and a gas-liquid contact between the regenerating gas 35b and the scrubbing liquid is carried out in the same manner as the gas scrubber A. Heat exchange between the regenerating gas 35b and the scrubbing liquid is performed, and various gas components which had been contained in the gas to be scrubbed and have been dissolved in the scrubbing liquid, and steam contained in the scrubbing liquid is released so as to keep gas-liquid equilibrium, i.e., saturated state in the gas temperature at the outlet of the regenerator B, and hence the regenerating gas accompanied by such gases is discharged as a regenerator vent gas 36b. The regenerating gas 35b is brought into contact with the scrubbing liquid, and then further purified by the make-up scrubbing liquid 41b. Further, mist in the regenerator vent gas 36b is removed by a mist separator 6b. Because the regenerator vent gas 36b accompanies a large amount of steam, if an amount of evaporation in the regenerator B is large and the scrubbing liquid is liable to be decreased, then, if necessary, a cooler 80 and a condensed water separator 81 may be provided to condense steam and reutilize the condensed water as a scrubbing liquid. Because the condensed water is much cleaner than the scrubbing liquid, such condensed water may be utilized as a make-up liquid 45a.
Steam and carbon dioxide are desorbed and released from the scrubbing water (scrubbing liquid) in the regenerator B. If the residence time of the regenerating gas in the regenerator B is sufficiently long, water is vaporized to generate steam until the steam reaches saturation concentration in the operating temperature of the regenerator B, and as dry gas components, the components of the gas, to be scrubbed, which are dissolved in alkaline scrubbing water (scrubbing liquid) are desorbed and released until such components of the gas reach desorption and absorption equilibrium concentration with the regenerating gas flowing in the regenerator B. The main component of dry gas desorbed and released in the regenerator B is carbon dioxide, and a pH of the scrubbing liquid is rapidly recovered by the releasing of carbon dioxide. Thus, acid gases absorbed in the scrubbing liquid are hardly desorbed and released.
An alkaline regeneration reaction in the regenerator B is represented by the following formula (7). Further, in order to prevent the absorbed acid gases from being desorbed, an oxidizing agent is injected into the scrubbing liquid to oxidize reductants such as sulfur compounds. As an oxidizing agent, chlorine-based oxidizing agent, such as sodium hypochlorite or chlorine dioxide, bromine-based oxidizing agent such as sodium hypobromite, and active oxygen-based oxidizing agent such as hydrogen peroxide or ozone, may be used. In the case where sodium hypochlorite (NaClO) is used as an oxidizing agent, the reaction is represented by the formulas (8) to (10).
2KHCO3→K2CO3+H2O+CO2 (7)
KHS+4NaClO→KHSO4+4NaCl (8)
KHSO3+NaClO→KHSO4+NaCl (9)
2KHNO3+NaClO→2KNO3+NaCl+H2O (10)
Vaporization of water content from the scrubbing liquid in the regenerator B deprives the scrubbing liquid of latent heat of vaporization to cool the scrubbing liquid.
Further, because carbon dioxide is desorbed and released from the scrubbing water (scrubbing liquid) in the regenerator B, alkaline agent in the scrubbing liquid which has combined with carbon dioxide is released again, and alkalinity of the scrubbing liquid is recovered. Therefore, release of acid gas components, such as hydrogen sulfide, carbonyl sulfide, hydrogen chloride, sulfur oxides, and nitrogen oxides in the regenerator B, which are dissolved in the scrubbing liquid can be suppressed, and the scrubbing liquid whose alkalinity is recovered is circulated again in the gas scrubber A, and hence alkaline agent can be circulated and utilized.
As the regenerating gas 35b introduced into the regenerator B, any component may be sufficient as far as such component is gaseous, and mainly air, oxygen, nitrogen, argon, steam, hydrogen, carbon monoxide, carbon dioxide, and a mixture of two or more of the above gases may be selected and used according to the purposes. When the regenerating gas is selected, a gas whose partial pressure of gas components to be desorbed in the regenerator is as low as possible should be selected. For example, for the purpose of desorption of carbon dioxide, the gas having as low content of carbon dioxide as possible should be selected. For the purpose of cooling the scrubbing liquid, or increasing the amount of recovered steam, the gas having as low content of steam as possible should be selected. Further, in the case where the regenerator vent gas is supplied to the gasification step, the gas whose oxygen concentration is as high as possible should be used.
The temperature TLBE of the scrubbing liquid in the lower part of the regenerator B can be set freely according to the purposes. The temperature control of TLBE is determined by the flow rate, temperature and humidity of the regenerating gas 35b, and the flow rate of the circulating scrubbing liquid. If the flow rate, temperature, and humidity of the regenerating gas 35b are constant, the temperature control of TLBE is normally carried out by controlling the flow rate of the scrubbing liquid. If the amount of saturated steam generated and the amount of carbon dioxide desorbed and released should be large, then TLBE should be kept as high as possible. However, since generation of steam deprives the scrubbing liquid of latent heat, TLBE becomes lower than TLBI (temperature of the scrubbing liquid at the inlet of the regenerator B). Therefore, in order to make TLBE be in accordance with desired TLAI, if necessary, a heat exchanger may be provided at the lower part of the regenerator B to heat or cool the scrubbing liquid.
As described above, cooling of the scrubbing liquid by the regenerating gas 35b is performed by direct heat exchange of sensible heat and depriving the scrubbing liquid of latent heat of vaporization of steam accompanied by the regenerator vent gas 36b. If this cooling capability exceeds a calorific value recovered from the gas 30 to be scrubbed, the temperature control of TLBE can be performed just by adjusting the flow rate of circulating scrubbing liquid. If the above cooling capability is smaller than the calorific value recovered from the gas 30 to be scrubbed, the vent gas cooler 80 for cooling the scrubbing liquid is necessary besides the regenerator B.
In the case where the scrubbing liquid is supplied from the gas scrubber A to the regenerator B, a gas-liquid separator 3a is preferably provided to remove the gas components to be scrubbed as much as possible which have been mixed into the scrubbing liquid without being dissolved. Particularly, in the case where the gas to be scrubbed is combustible gas and the regenerating gas is oxygen-containing gas, the function of gas-liquid separator is particularly important for preventing explosion.
The gas components separated by the gas-liquid separator 3a have substantially the same components as the gas components to be scrubbed, and the scrubbing water (scrubbing liquid) flowing from the gas scrubber A into the gas-liquid separator 3a has the lowest pH in the circulating passage of the scrubbing water (scrubbing liquid) due to dissolution of carbon dioxide in the scrubbing liquid. Because acid gases absorbed in the scrubbing liquid tend to be released, the separated gas components should be returned to the most upstream portion of the flow of the gas to be scrubbed in the gas scrubber A and be scrubbed again.
In the regenerator B, carbon dioxide is released from the scrubbing liquid, and the scrubbing liquid is cooled by vaporization of water content, and then the cooled scrubbing liquid is introduced into the gas scrubber A again. However, if dust is contained in the gas to be scrubbed, in some cases, the scrubbing liquid accompanies a large amount of dust components. Thus, it is necessary for the scrubbing liquid to accompany as little dust as possible when the scrubbing liquid is withdrawn from the regenerator B as with the gas scrubber A.
Further, in the case where the scrubbing liquid is returned from the regenerator B to the gas scrubber A, a gas-liquid separator 3b is preferably provided to remove regenerating gas components as much as possible which have been mixed into the scrubbing liquid without being dissolved. Particularly, if the gas to be scrubbed is combustible gas and the regenerating gas is oxygen-containing gas, then the function of the gas-liquid separator is particularly important to prevent mixing of oxygen and the combustible gas.
The gas components separated in the gas-liquid separator 3b comprise regenerating gas components into which steam, and a trace amount of carbon dioxide depending on the condition are mixed, and hence such separated gas components can be mixed with the regenerating gas discharged from the regenerator B as they are.
Operating pressures of the gas scrubber A and the regenerator B according to the present invention can be freely selected according to the processes. In the embodiment shown in
Conversely, if the operating pressure in the gas-phase section of the regenerator B is set to be lower than that in the gas-phase section of the gas scrubber A, although use of the regenerating gas is limited, the difference of partial pressure of carbon dioxide in the respective gas-phase sections of the gas scrubber A and the regenerator B becomes larger. Therefore, if the gas temperature at the outlet of the regenerator B is the same, the amount of released carbon dioxide is larger, and the regenerating function of alkaline agent is advantageously enhanced.
The control of an amount of the make-up liquid 45a comprising alkaline agent supplied to the gas scrubber A is carried out by measuring a pH of the scrubbing liquid to keep the pH of the scrubbing liquid at a given value. In order to perform such control properly, as shown in
The pH of the scrubbing liquid is desirable to be adjusted in the range of 7 to 14, preferably 9 to 12, and more preferably 10 to 11.
In
The embodiment shown in
In
A weir 13a is provided in the gas-liquid-solid separation section A1, and the scrubbing liquid flows into the location near the bottom of the retention liquid, overflows the weir 13a, and then is withdrawn from the gas scrubber A. SS (solid) components contained in the scrubbing liquid settle against an ascending flow of the scrubbing liquid to allow solid-liquid separation to be performed, and high concentration waste sludge 9a is recovered from the bottom of the gas scrubber A. Because the retention liquid level inside the weir 13a is always kept calm, gaseous matter is rapidly separated at the liquid level from the liquid.
The slower an ascending velocity of the scrubbing liquid in the gas-liquid-solid separation section A1 is, the higher a solid-liquid separation capability is, and this is advantageous. However, since a cross-sectional area of the apparatus becomes large, it is necessary to design in a suitable velocity range, and such ascending velocity is normally 50 mm/s or less, preferably 10 mm/s or less, and more preferably 5 mm/s or less. However, because colloidal SS content cannot be separated by a precipitating treatment, if a large amount of such SS content is contained, it is then necessary to provide a solid content removing means, which removes solid content from the scrubbing water (scrubbing liquid) and is different from a precipitating and separating means, such as a filtration treatment for treating a part of the scrubbing liquid using a separation membrane or a filter media.
In order to increase the solid-liquid separation effect, inorganic flocculant or organic and polymeric flocculent may be used for the purpose of flocculating of SS components. Further, when SS load is excessively high and solid-liquid separation cannot be easily performed by the precipitating method, the dry-type dust collector 7, such as a cyclone or a filter, should be provided upstream of the gas scrubber A to remove dust components in the gas to be scrubbed.
The scrubbing liquid withdrawn from the gas scrubber A is supplied to the regenerator B in a gravity flow. At this time, when a sufficient difference of elevation can be ensured, the scrubbing liquid can be supplied to the regenerator B by the spraying system. However, when a sufficient difference of elevation cannot be ensured and a pressure loss of the circulating water is not allowable, the scrubbing liquid may be supplied to the upper part of the packing for promotion of contact provided in the regenerator B without providing a special means.
The gas-phase section pressure Pb [Pa] in the regenerator B is expressed in the following description by using a gas-phase section pressure Pa [Pa] in the gas scrubber A, retention liquid level Ha [m] of the scrubbing liquid after overflowing the weir 13a, inlet level Hbi [m] of the scrubbing liquid in the regenerator B, specific gravity p [kg/M3] of the scrubbing liquid, gravitational acceleration g [m/s2), and pressure loss ΔPab [Pa] of the scrubbing liquid from the gas scrubber A to the regenerator B.
Pb=Pa+ρ*g(Ha−Hbi)−ΔPab (11)
In the case where combustion exhaust gas discharged from a municipal waste incinerator operated at substantially atmospheric pressure is treated, Pa is kept in the range of atmospheric pressure or 2 kPa to 7 kPa, preferably 3 to 6 kPa, and more preferably about 4 to 5 kPa. Further, although Pb is changed according to the use of the regenerator vent gas, if the regenerator vent gas is utilized as a fluidizing gas of a fluidized-bed furnace, then Pb is preferably higher than atmospheric pressure by 20 to 50 kPa. Therefore, if expressed by absolute pressure, Pa is set to be in the range of 94 to 99 kPa, and Pb is set to be in the range of 121 to 151 kPa. If a fluidized-bed furnace is not used in a gasification step, a pressure for fluidization is not required, and hence even if the regenerator vent gas is utilized as a gasifying agent in the gasification step, Pb is such pressure obtained by adding a pressure corresponding to resistance in the supply pipe to the operating pressure in the gasification step.
A regenerating gas 35b having components according to the purposes is supplied to the regenerator B as with the regenerator shown in
A weir 13b is provided in the gas-liquid-solid separation section B1, and the scrubbing liquid flows into the location near the bottom of the retention liquid and overflows the weir 13b, and then is withdrawn from the regenerator B. SS (solid) components contained in the scrubbing liquid settle against an ascending flow of the scrubbing liquid to allow solid-liquid separation to be performed, and high concentration waste sludge 9b is recovered from the bottom of the regenerator B. Because the retention liquid level inside the weir 13b is always kept calm, gaseous matter is rapidly separated at the liquid level from the liquid, thus preventing the gaseous matter from being accompanied by the withdrawn scrubbing liquid.
In the regenerator B as well as the gas scrubber A, the slower an ascending velocity of the scrubbing liquid in the gas-liquid-solid separation section B1 is, the higher a solid-liquid separation capability is, and this is advantageous. However, since a cross-sectional area of the apparatus becomes large, it is necessary to design in a suitable velocity range, and such ascending velocity is normally 50 mm/s or less, preferably 10 mm/s or less, and more preferably 5 mm/s or less.
In order to increase the solid-liquid separation effect, inorganic flocculent or organic and polymeric flocculant may be used for the purpose of flocculating of SS components. Further, when SS load is excessively high and solid-liquid separation cannot be easily performed by the precipitating method, the dry-type dust collector, such as a cyclone or a filter, should be provided upstream of the regenerator B to remove dust components in the regenerating gas as in the gas scrubber A.
If the regenerating gas 35b is a gas containing no dust, solid-liquid separation is not necessary in the regenerator B, and withdrawal of sludge from the lowermost part is not necessary, and hence an internal structure of the regenerator B can be simplified. However, a gas-liquid separation function is necessary, and it is desirable that the regenerator B has such a structure as shown in
The scrubbing liquid withdrawn from the regenerator B is returned to the gas scrubber A by the circulating pump 4b. Here, a method for controlling the amount of the scrubbing liquid is as follows. The liquid level of the scrubbing liquid after overflowing the weir 13b in the regenerator B is measured, the measured liquid level is converted to electrical signals, and then such signals are inputted into the level adjusting device 70b. The level adjusting device 70b outputs, if replenishment of the scrubbing liquid is necessary, signals for opening the make-up liquid control valve 10a and closing the waste liquid control valve 17a so that liquid level becomes a predetermined value. The level adjusting device 70b outputs, if the amount of scrubbing liquid increases and the scrubbing liquid is required to be discharged from the circulating system, signals for closing the make-up liquid control valve 10a and opening the waste liquid control valve 17a.
The make-up liquid may be supplied to the regenerator B and the waste liquid may be discharged. Particularly, in the case of producing reaction precipitate in the regenerator, withdrawal of waste liquid and sludge from the regenerator B is not necessary. Further, in the regenerator B as well as the gas scrubber A, a fresh make-up liquid is supplied to the most downstream side of a regenerating gas flow in the regenerator, and hence the cleaning effect of the regenerating gas discharged from the regenerator B is enhanced, and utility value of this gas is further increased.
When the make-up liquid is supplied to the regenerator B, and the waste liquid is discharged from the regenerator B, the level control signals are sent from the level adjusting device 70b to the make-up liquid control valve 10b and the waste liquid control valve 17b, and the make-up liquid control valve 10b and the waste liquid control valve 17b are operated in the same manner as the make-up liquid control valve 10a and the waste liquid control valve 17a, thereby controlling the amount of the circulating scrubbing liquid. In
By constructing the system in a gravity flow manner as in the embodiment shown in
In
The embodiment shown in
In
The gas-phase section pressure Pc [Pa] in the second regenerator C is expressed in the following description by using a gas-phase section pressure Pb [Pa] in the first regenerator B, retention liquid level Hb [m] of the scrubbing liquid after overflowing the weir 13b, inlet level Hci [m] of the scrubbing liquid in the second regenerator C, specific gravity ρ [kg/M3] of the scrubbing liquid, gravitational acceleration g [m/s2], and pressure loss ΔPbc [Pa] of the scrubbing liquid from the regenerator B to the second regenerator C.
Pc=Pb+ρg(Hb−Hci)−ΔPbc (12)
A regenerating gas 35c having components according to the purposes is supplied to the second regenerator C as with the above regenerator B, and is brought into contact with a scrubbing liquid, and discharged. A gas-liquid-solid separation section C1 is provided in the lower part of the second regenerator C as with the regenerator B. The scrubbing liquid which has contacted the regenerating gas 35c is collected by a liquid-collecting plate 11c and flows in a gravity flow into a gas-liquid-solid separation section C1 at the lower part of the second regenerator C. The lower end of a down flow pipe 12c connected to the lower part of the liquid-collecting plate 11c is located in the vicinity of the bottom of retention water remaining in the gas-liquid-solid separation section C1, and the scrubbing liquid flowing downwardly is supplied to the location near the bottom of the retention water.
A weir 13c is provided in the gas-liquid-solid separation section C1, and the scrubbing liquid flows into the location near the bottom of the retention liquid, overflows the weir 13c, and then is withdrawn from the second regenerator C. SS (solid) components contained in the scrubbing liquid settle against an ascending flow of the scrubbing liquid to allow solid-liquid separation to be performed, and high concentration waste sludge 9c is recovered from the bottom of the second regenerator C. Because the retention liquid level inside the weir 13c is always kept calm, gaseous matter is rapidly separated at the liquid level from the liquid, thus preventing the gaseous matter from being accompanied by the withdrawn scrubbing liquid.
In the second regenerator C as well as the first regenerator B, the slower an ascending velocity of the scrubbing liquid in the gas-liquid-solid separation section C1 is, the higher a solid-liquid separation capability is, and this is advantageous. However, since a cross-sectional area of the apparatus becomes large, it is necessary to design in a suitable velocity range, and such ascending velocity is normally 50 mm/s or less, preferably 10 mm/s or less, and more preferably 5 mm/s or less. In order to increase the solid-liquid separation effect, inorganic flocculant or organic and polymeric flocculent may be used for the purpose of flocculating of SS components. However, because colloidal SS content cannot be separated by a precipitating treatment, if a large amount of such SS content is contained, then it is necessary to provide a solid content removing means, which removes solid content from the scrubbing water (scrubbing liquid) and is different from a precipitating and separating means, such as a filtration treatment for treating a part of the scrubbing liquid using a separation membrane or a filter media, as with the first regenerator B.
If the regenerating gas 35c is a gas containing no dust, solid-liquid separation is not necessary in the second regenerator C, and withdrawal of sludge from the lowermost part is not necessary, and hence an internal structure of the second regenerator C can be simplified. However, a gas-liquid separation function is necessary, and it is desirable that the second regenerator C has such a structure as in the gas scrubber A and the first regenerator B for the purpose of keeping a liquid surface in a calm state.
The scrubbing liquid withdrawn from the second regenerator C is returned to the gas scrubber A by the circulating pump. Here, a method for controlling the amount of the scrubbing liquid is as follows. The liquid level of the scrubbing liquid after overflowing the weir 13c in the second regenerator C is measured, the measured liquid level is converted to electrical signals, and then such signals are inputted into the level adjusting device 70c. The level adjusting device 70c outputs, if replenishment of the scrubbing liquid is necessary, signals for opening the make-up liquid control valves 10a, 10b and 10c and closing the waste liquid control valves 17a, 17b and 17c so that liquid level becomes a predetermined value. The level adjusting device 70c outputs, if the amount of scrubbing liquid increases and the scrubbing liquid is required to be discharged from the circulating system, signals for closing the make-up liquid control valves 10a, 10b and 10c and opening the waste liquid control valves 17a, 17b and 17c. In
As with the first and second regenerators, regenerators can be sequentially connected in a three-stage or more.
The regenerator vent gas 36b is preferably heated by heat exchange with a high-temperature produced gas after the gasification step. In the present embodiment, the regenerator vent gas 36b is led to a high-temperature heat exchanger 121 where a medium to be heated is adapted to be heated to a temperature of 500° C. or higher, and the regenerator vent gas 36b is heated to a temperature of 500° C. or higher, preferably 600° C. or higher, and more preferably 700° C. or higher in the high-temperature heat exchanger 121, and then the heated vent gas 37 is supplied to a gasification furnace. Further, as in the present embodiment, in the case where the gasification step incorporates a plurality of furnaces, and proper oxygen concentrations of the oxidizing agent supplied to the respective furnaces are different from each other, an oxidizing agent should be supplied to a heated vent gas to adjust oxygen concentration of the vent gas. In the present embodiment, the oxidizing agent 50 is supplied to the heated vent gas 37 to be supplied to the high-temperature gasification furnace 114.
In both of the embodiments shown in
Particularly, in the embodiment shown in
The gasification step 110 in
In the embodiment shown in
In the embodiment shown in
It is preferable to employ an amine absorption method in the carbon dioxide absorption apparatus 147. In the amine absorption method, the higher the pressure of gas flowing therein, the larger difference of partial pressure of carbon dioxide between a pressure at the time of absorption and a pressure at the time of regeneration, and this is advantageous. In the present embodiment, the second gas compressor 145 is provided to pressurize the produced gas to 800 kPa or higher and then supply the pressurized gas. If the first gas compressor can pressurize the gas sufficiently, the second gas compressor 145 is not necessary. If the second gas compressor 145 is provided, a gas cooler 80 should be provided downstream of the shift reaction apparatus 142 to condense and remove steam contained in the gas for thereby reducing power consumption of the second gas compressor 145.
A vent gas 67 discharged from the hydrogen purifying and pressurizing apparatus 149 contains methane, nitrogen, argon, and a small amount of hydrogen, and only methane is absorbed by a methane absorption apparatus 170 and the remainder is discharged. The recovered methane gas 68 is supplied to the gasification step 110, and reformed and refined again, thus becoming materials of hydrogen gas.
After the produced gas is purified into pure hydrogen 65 by the hydrogen purifying and pressurizing apparatus 149, such pure hydrogen is supplied to a fuel cell power generation step 160. A fuel cell generates electricity, water and heat by reacting hydrogen with oxygen, and includes four types of fuel cells, a proton exchange membrane fuel cell, a phosphoric acid fuel cell, a molten carbonate fuel cell and a solid electrolyte fuel cell in order of operating temperature from low to high.
In general, air or pure oxygen is used as an oxidizing agent for supplying oxygen to a fuel cell, but any gas may be used as far as such gas contains oxygen basically, and does not contain components poisonous to the fuel cell. In the present embodiment, highly enriched oxygen gas 51 which is purified by a PSA method or the like and has oxygen concentration of 80% or higher, preferably 90% or higher, and more preferably 93% or higher is used. Pure oxygen is better than highly enriched oxygen gas. In the case of oxygen gas produced by the PSA method, gas components other than oxygen are nitrogen and argon. In the embodiment shown in
Saturated aqueous vapor pressure at a temperature of 45 to 60° C. is in the range of 10 to 20 kPa, and the cooled oxygen electrode vent gas contains 10 to 20% of steam at atmospheric pressure and is supplied to the regenerator as a regenerating gas.
Since the oxygen electrode vent gas 55 in the fuel cell does not contain carbon dioxide at all, such vent gas is suitable for alkaline regenerating gas in the regenerator B. In the present invention, the regenerator B is operated so-as to allow the gas-phase section pressure Pb to be kept in the range of 120 to 140 kPa, and the regenerator vent gas 36b can accompany carbon dioxide whose concentration is 5% or more of gas total volume.
The temperature of the scrubbing liquid which flows into the regenerator is in the range of 70 to 99° C., and the oxygen electrode vent gas 55 is brought into contact with the scrubbing liquid in a countercurrent flow and heated by direct heat exchange to a temperature of 70 to 99° C. Saturated aqueous vapor pressure at a temperature of 70 to 99° C. is in the range of 31 to 99 kPa. If the gas-phase section pressure Pb in the regenerator is 130 kPa, then the rate of steam in the regenerator vent gas is in the range of 24 (=31/130) to 76% (=99/130). Therefore, the oxygen electrode vent gas of the fuel cell which has been supplied as a regenerating gas carries away steam based on the difference of the rate of steam between the inlet of the regenerator and the outlet of the regenerator from the scrubbing water (scrubbing liquid), and the scrubbing water (scrubbing liquid) is cooled. Further, a hydrogen electrode of the fuel cell releases a hydrogen electrode vent gas 5b which is mixed with the purified hydrogen 65 by a gas mixer 20.
As described above, the regenerator vent gas components vary somewhat depending on the operating temperature of the regenerator, and contains about 5 to 10% of carbon dioxide, approximately the same amount of nitrogen and argon, 15 to 45% of oxygen, and 24 to 76% of steam. The gas having the above components is suitable for a mixed gas of an oxidizing agent and a gasifying agent supplied to the gasification step, and such gas may be supplied to the gasification step as it is, or the gasification step after adjustment of components suitable for the gasification step by adding steam or oxygen as necessary. Specifically, in the embodiment shown in
By applying the present invention to the fuel cell power generation process by gasification, the following great effects can be obtained.
1. Because the gas scrubbing liquid supplied to the gas scrubber can be kept to a high pH by an alkaline regenerating function in the regenerator without consuming a large amount of alkaline agent, an acid gas absorption function in the gas scrubbing step is greatly enhanced, and durability of apparatuses constituting a hydrogen production step provided in the downstream side can be improved.
2. Because scrubbing water (scrubbing liquid) can be cooled in the regenerator, just a small part of waste heat is supplied to a cooling tower, consumption of a make-up cooling water is reduced, and problems such as white plume and rainfall (mist fall to neighborhood) are reduced.
3. Since steam used as a gasifying agent in the gasification step can be recovered from the scrubbing liquid, high-quality steam is not required, and consumption of water and energy required for a water treatment can be reduced.
4. Compared with the conventional technology in which latent heat of low-pressure steam has been disposed in the cooling tower as waste heat, such heat can be returned to the gasification step, thus improving energy efficiency in the present invention.
5. Carbon dioxide is desorbed and recovered from the scrubbing liquid and supplied to the gasification step as a gasifying agent, and carbon dioxide has specific heat smaller than steam, and hence heat for temperature rising in the gasification step is small and cold gas efficiency is improved.
6. In the case where carbon dioxide is used as a gasifying agent, a gas containing a large amount of carbon monoxide having a higher utility value than hydrogen is produced, and hence the use of the produced gas is widened.
In the present embodiment, purified hydrogen is used as a fuel in a fuel cell, but the purified hydrogen is not limited to the fuel in the fuel cell, and the system in this embodiment from which the fuel cell power generation step is removed can be provided as a hydrogen production system for other use.
Therefore, even if the oxidizing agent in the fuel cell is air, highly enriched oxygen gas whose oxygen concentration is 80% or higher, preferably 90% or higher, and more preferably 93% or higher, or pure oxygen gas should be used as an oxidizing agent in the gasification step 110. In this case, gases which can be used as regenerating gases in regenerators include the oxidizing agent in the gasification step and the oxygen electrode vent gas in the fuel cell. Thus, it is preferable that the regenerator is provided in a two-stage configuration, and the respective gases are used as a regenerating gas for the first regenerator B and the second regenerator C. Next, an embodiment shown in
In the embodiment shown in
Therefore, in the embodiment shown in
Therefore, in the present embodiment, it is important to discharge carbon dioxide as much as possible together with the second regenerator vent gas 36c to the outside of the system. The method to obtain the maximum effect is that by lowering operating temperature of the gas scrubber A as much as possible, an absorption ability of carbon dioxide into the scrubbing liquid in the gas scrubber is enhanced, and desorption and releasing of carbon dioxide is suppressed in the first regenerator B as much as possible and saturated steam is generated. Further, the second regenerator C is operated at as high temperature as possible, and a gas-liquid contact with a regenerating gas is intensively made, and desorption and releasing of carbon dioxide is promoted. The purpose for suppressing the amount of carbon dioxide discharged from the first regenerator B is that keeping carbon dioxide absorbed in the scrubbing liquid as much as possible and releasing it at a stretch in the second regenerator C, the amount of carbon dioxide discharged to the outside of the system is increased as much as possible. Therefore, if necessary, a heat exchanger is provided to heat the scrubbing liquid. In this case, for this heating, steam generated in the heat recovery step or steam which has been generated in the heat recovery step and utilized to heat carbon dioxide absorption liquid in the carbon dioxide absorption step should be utilized.
Pure oxygen or highly enriched oxygen which is a regenerating gas in the first regenerator does not contain steam, and is suitable for a regenerating gas in the case where steam is generated as a gasifying agent. An oxygen electrode vent gas in the fuel cell which is a regenerating gas in the second regenerator has a temperature of about 75 to 90° C. and contains saturated steam at the outlet of the fuel cell. Therefore, when the oxygen electrode vent gas in the fuel cell is used as a regenerating gas as it is, fresh steam is hardly generated in the second regenerator, and hence the cooling effect is hardly obtained. This is very advantageous to keep operating temperature of the second regenerator as high as possible. In the case where the cooling effect of the scrubbing water (scrubbing liquid) in the second regenerator is enhanced, the oxygen electrode vent gas should be cooled to condense steam contained therein. The condensed water is substantially pure water, and has high utility value and various uses. Further, when the oxygen electrode vent gas in the fuel cell has higher pressure than necessary, an aspirator may be provided to suck air, so as to increase the amount of regenerating gas, and enhance the regenerating effect.
If the first regenerator B is a complete mixing-type regenerator shown in
The vertical position of the first regenerator B relative to the gas scrubber A is determined based on the pressure required as a gasifying agent. The higher the pressure required as a gasifying agent, the lower the position of the first regenerator B relative to the gas scrubber A is. The scrubbing liquid which has flowed into the first regenerator B is fed to the second regenerator C, and if the second regenerator C is disposed at a location lower than the gas scrubber A, the scrubbing liquid is allowed to flow into the second regenerator C in a gravity flow without providing a circulating pump at the outlet of the first regenerator B in a scrubbing liquid circulating path. However, if the pressure Pb becomes a predetermined pressure or lower, there is a possibility that the scrubbing liquid flows backward, and hence such care as to provide a check valve in the scrubbing liquid circulating path should be taken as necessary. A pump for circulating a scrubbing liquid may be provided. Further, by providing a bypass line having a scrubbing liquid bypass valve 19ac to suppress the amount of the scrubbing liquid which flows in the first regenerator B, the control of Pb can be easily made, or consumption of steam for heating can be reduced. If the first regenerator is a complete mixing-type regenerator as with the embodiments shown in
By employing a two-stage regeneration-type acid gas removing apparatus shown in
It can be said that the embodiment shown in
In optimum conditions in the embodiment which have been found by the present inventors, when the operating pressure in the gasification step is atmospheric pressure, the temperature of the gas flowing into the gas scrubber A is 500° C., and calorific value of materials is about 13 MJ/kg, the operating condition having the highest efficiency is as follows:
Therefore, the oxygen electrode vent gas in the fuel cell is used as a regenerating gas of the first regenerator, and a first regenerator vent gas is discharged to the outside of the system and the scrubbing liquid after carbon dioxide desorption is supplied to the second regenerator.
Therefore, the second regenerator vent gas obtained by supplying pure oxygen or highly enriched oxygen to the second regenerator as a regenerating gas, i.e., a mixing gas of a gasifying agent and an oxidizing agent for supplying the gasification step contains carbon dioxide whose concentration is much lower than that in the embodiment shown in
In the embodiment of the present invention, the first regenerator and the second regenerator may be a countercurrent flow-type regenerator shown in
In optimum conditions in the embodiment which have been found by the present inventors, when the operating pressure in the gasification step is atmospheric pressure, the temperature of the gas flowing into the gas scrubber A is 500° C., and calorific value of materials is about 13 MJ/kg, the operating condition having the highest efficiency is as follows:
On the other hand, the first scrubbing liquid 82b which has absorbed strong acid gases such as hydrogen chloride and whose temperature has increased is sent to the first regenerator B via the gas-liquid separator 3a, and is brought into contact with the first regenerating gas 35b, for example, enriched oxygen gas having different components from the gas to be scrubbed and containing oxygen to generate steam in the first regenerator B until a pressure in the first regenerator B reaches saturated aqueous vapor pressure at a temperature in the first regenerator B.
For example, when the regenerator is operated at an atmospheric pressure (about 0.1 PMa (1 bar)) and a temperature of 80° C., a first regenerator vent gas 36b discharged from the first regenerator accompanies 47% of steam. At the same time, the first scrubbing liquid 82b is deprived of latent heat of vaporization and is cooled. It should be noted that when the first regenerating gas 35b accompanies steam whose amount is equal to or greater than the amount corresponding to saturated aqueous vapor pressure in the first regenerator B, water will not vaporize and the first scrubbing liquid will not be cooled in the first regenerator B. Therefore, it is more preferable that steam content in the first regenerating gas 35b is smaller, i.e., dew point is lower.
Further, because the first scrubbing liquid 82b absorbs strong acid gases in the first gas scrubbing section A′, a pH of the first scrubbing liquid 82b is lowered, and because water content of the first scrubbing liquid 82b is vaporized in the first scrubbing liquid regenerator B, it is necessary to replenish first alkaline agent and water. Further, in the case where dust is contained in the gas to be scrubbed and is entrapped in the first scrubbing liquid 82b, it is necessary to separate dust from the first scrubbing liquid 82b. In the present invention, a chemical adding apparatus and a filtration apparatus are provided in a circulating passage of the first scrubbing liquid, respectively, whereby the pH of the first scrubbing liquid 82b is adjusted by adding first alkaline agent and a diluting water for diluting alkaline agent to the first scrubbing liquid 82b, and the whole or part of the first scrubbing liquid 82b is always filtrated to remove solid components. Any alkaline substance may be used as alkaline agent, but sodium hydroxide or potassium hydroxide is preferable. If the pH of the first scrubbing liquid 82b to be adjusted, i.e., the pH of the first scrubbing liquid 82b at the inlet of the first gas scrubbing section A′ is 4 or more, then the first scrubbing liquid 82b has an absorption capability for absorbing hydrogen chloride gas and is preferable. However, if the pH of the first scrubbing liquid 82b is 11 or more, the first scrubbing liquid 82b absorbs carbon dioxide besides strong acid gases and is not preferable because of an increased consumption of the first alkaline agent. Therefore, the pH of the first scrubbing liquid 82b at the inlet of the first gas scrubbing section A′ is preferably in the range of 4 to 11, more preferably 5 to 10. Salts produced by neutralization reaction of the first alkaline agent and strong acid gases are gradually accumulated in the first scrubbing liquid 82b, and a part of the first scrubbing liquid is required to be discharged at all times in order to prevent harmful effect caused by excessive condensation of salts.
On the other hand, the first regenerator vent gas 36b which accompanies saturated steam can be used as a diluting gas of a gasifying agent for gasifying combustibles. Further, when enriched oxygen gas or PSA oxygen (enriched oxygen produced by a pressure swing adsorption method) is used as the first regenerating gas 35b, the first regenerating vent gas 36b may be utilized as a gasifying agent as it is.
With regard to temperature of the first scrubbing liquid 82b, the temperature T1out of the first scrubbing liquid at the outlet of the first gas scrubbing section should be in the range of the boiling point to the boiling point minus 20° C., preferably in the range of the boiling point to the boiling point minus 10° C., and more preferably in the range of the boiling point to the boiling point minus 5° C. Further, the temperature T1in of the first scrubbing liquid at the inlet of the first gas scrubbing section A′ should be in the range of the temperature T1out of the first scrubbing liquid to the temperature T1out minus 20° C., preferably in the range of the saturation temperature of steam in the gas to be scrubbed to the saturation temperature minus 5° C.
The amount of the first scrubbing liquid 82b to be circulated should be determined on the basis of flow rate, temperature and specific heat of the gas to be scrubbed so that the temperature of the first scrubbing liquid meets the temperatures required in the first scrubbing liquid at the outlet and inlet of the first gas scrubbing section A′.
The first scrubbing liquid 82b withdrawn from the first regenerator B is returned to the first gas scrubbing section A′ via the gas-liquid separator 3b.
Further, the second scrubbing liquid 82c which has absorbed carbon dioxide and weak acid gases such as hydrogen sulfide and whose temperature has increased by condensation of steam is sent to the second regenerator C via the gas-liquid separator 3c, and is brought into contact with the second regenerating gas 35c, for example, air or a fuel cell vent gas having different components from the gas to be scrubbed to generate steam in the second regenerator C until a pressure in the second regenerator C reaches the saturated aqueous vapor pressure at a temperature in the second regenerator C, and to perform regeneration of alkali by decarbonation.
In the present invention, a chemical adding apparatus and a filtration apparatus may be provided in a circulating passage of the second scrubbing liquid 82c to add a proper amount of an oxidizing agent to the second scrubbing liquid 82c according to the amount of absorbed reducing acid gas such as hydrogen sulfide. Further, the pH of the second scrubbing liquid 82c is preferably in the range of 7 to 12. The second alkaline agent and the oxidizing agent are the same as alkaline agent and the oxidizing agent described in the first embodiment.
On the other hand, the second regenerator vent gas 36c which accompanies desorbed carbon dioxide and saturated steam is discharged through a condenser 80c and a condensed water separator 81c. The condensed water recovered in the condensed water separator 81c is returned to the system as a diluting water of the first alkaline agent or a diluting water of the first scrubbing liquid 82b.
With regard to a temperature of the second scrubbing liquid 82c, the temperature T2out of the second scrubbing liquid at the outlet of the second gas scrubbing section A2 should be in the range of the temperature T1in of the first scrubbing liquid at the inlet of the first gas scrubbing section A′ to the temperature T1in minus 20° C., and preferably in the range of the temperature T1in of the first scrubbing liquid at the inlet of the first gas scrubbing section A′ to the temperature T1in minus 10° C. Further, the temperature T2in of the second scrubbing liquid at the inlet of the second gas scrubbing section A2 should be lower than the temperature T2out of the second scrubbing liquid at the outlet of the second gas scrubbing section A2 by 5° C. or more, preferably 10° C. or more, and more preferably 20° C. or more.
The amount of the second scrubbing liquid 82c to be circulated should be determined on the basis of flow rate, temperature and specific heat of the gas to be scrubbed so that the temperature of the second scrubbing liquid meets the temperatures required in the second scrubbing liquid at the outlet and inlet of the second gas scrubbing section A2.
The second scrubbing liquid 82c withdrawn from the second regenerator C is returned to the second gas scrubbing section A2 via the gas-liquid separator 3d. In the case where the temperature of the second scrubbing liquid at the outlet of the second regenerator C is higher than the temperature of the second scrubbing liquid at the inlet of the second gas scrubbing section, a cooling apparatus is provided in a circulating passage to adjust the temperature of the second scrubbing liquid.
In the present embodiment, as described above, by setting the temperature of the scrubbing liquid at respective locations, among the calorific value possessed by the gas 30 to be scrubbed, sensible heat is cooled and recovered in the first gas scrubbing section A′, and the recovered heat is utilized to generate steam in the first regenerator B. On the other hand, latent heat, i.e., the condensed heat of steam contained in the gas 30 to be scrubbed is cooled and recovered in the second gas scrubbing section A2, and the recovered heat is utilized for decarbonation of the second scrubbing liquid 82c, i.e., regeneration of the second alkaline agent in the second regenerator C. In this manner, according to the present invention, thermal efficiency in the total system and absorption efficiency of the gas to be removed can be improved.
The scrubbed gas 31 obtained in the present embodiment is treated to produce hydrogen gas by one of or an optional combination of a desulfurizing step, a carbon monoxide shift reaction step, a carbon monoxide selective oxidation step, a carbon dioxide absorption step, a methanation step, a hydrogen purifying step using hydrogen-absorbing alloy, and a hydrogen purifying PSA step, and the produced hydrogen gas is supplied to a fuel cell power generation step to generate electricity.
In the case where combustible materials having an irregular shape such as municipal wastes are materials, a raw material feeder shown in
The produced gas, i.e., the gas 30, to be scrubbed, from which sensible heat has been recovered in the waste heat boiler is led to the gas scrubber A of the present invention, and acid gases are removed and the produced gas is cooled to a temperature of 60 to 90° C. If the amount of dust or components contained in the produced gas have a bad influence on the performance of the gas scrubber, then a dry-type dust collector, such as a cyclone or a filter, may be provided upstream of the gas scrubber, whereby the produced gas is led to the gas scrubber A after removing dust therefrom.
In the present embodiment, regeneration of alkaline agent is performed in two stages. In the first regenerator B, highly enriched oxygen gas whose oxygen concentration is 80% or higher, preferably 90% or higher, and more preferably 93% or higher, or pure oxygen gas is used as a regenerating gas 50. The regenerator vent gas 36b discharged from the first regenerator B is heated in the high-temperature heat exchanger 121, and then supplied to the gasification furnace as a gasifying agent and an oxidizing agent for partial oxidization. Because the regenerating gas supplied to the first regenerator B, which is highly enriched oxygen gas or pure oxygen, does not contain steam, the regenerating gas comes to contain a large amount of steam by contacting alkaline agent, and the temperature rise of the regenerating gas is suppressed by latent heat of vaporization, so the amount of carbon dioxide stripped by the regenerating gas is held to be low. Thus, such regenerating gas is suitable for a gas to be supplied to the gasification step. Further, a hydrogen electrode vent gas 161 in the fuel cell and an oxygen electrode vent gas 162 in the fuel cell power generation step 160 are combusted by a vent gas burner 163, and pressure energy and thermal energy are recovered in a turbo-charger 164 and combustion exhaust gas 166 is supplied to the second regenerator C where a wet gas 36c containing a large amount of carbon dioxide is obtained. The gas scrubber A, the first regenerator B and the second regenerator C are not limited to the embodiment shown in
The scrubbed gas 31 which has been scrubbed and cooled is pressurized to a pressure of 200 to 800 kPa in a gas compressor 135, and then supplied to a hydrogen production step 140. The gas compressor 135 is driven by a steam turbine 125 which uses high-pressure steam 123 from the waste heat boiler 122. Low-pressure steam 124 discharged from the steam turbine 125 is supplied to a carbon dioxide absorption apparatus 147 or a shift reaction apparatus 142 in the hydrogen production step to utilize thermal energy effectively.
The hydrogen production step 140 incorporates a desulfurizing reaction apparatus 141 for removing sulfur content in the produced gas; the shift reaction apparatus 142 for converting carbon monoxide and H2O in the produced gas into hydrogen and carbon dioxide by a shift reaction; the carbon dioxide absorption apparatus 147 for absorbing and removing carbon dioxide in the produced gas after the shift reaction; and a CO removing apparatus 150 for removing carbon monoxide remaining in the gas 188 after carbon dioxide absorption, and the produced gas is sequentially processed in the respective apparatuses to obtain highly enriched hydrogen gas 69. In the CO removing apparatus 150, a selective oxidation apparatus for combusting carbon monoxide in the gas selectively, or a methanation reaction apparatus for producing methane by reacting carbon monoxide and carbon dioxide in the gas with hydrogen, or a hydrogen purifying PSA (pressure swing adsorption apparatus) for adsorbing and separating gas components, other than hydrogen, such as carbon monoxide, carbon dioxide, and nitrogen by adsorbent such activated carbon or zeolite is used.
In the fuel cell power generation step 160, the highly enriched hydrogen gas 69 is supplied to a hydrogen electrode of a fuel cell and air 53 is pressurized by a turbo-charger 164 and supplied to an oxygen electrode of the fuel cell, thus generating electricity. The fuel cell may be any fuel cell as far as such fuel cell can use hydrogen as a fuel, and any type of a proton exchange membrane fuel cell, a phosphoric acid fuel cell, a molten carbonate fuel cell and a solid electrolyte fuel cell may be used.
The hydrogen electrode vent gas 161 and the oxygen electrode vent gas 162 are led to the vent gas burner 163 and combusted. Combustion exhaust gas 165 of the vent gas burner 163 is supplied to the turbo-charger 164, and air 53 to be supplied to the oxygen electrode of the fuel cell is pressurized by the turbo-charger 164. Thereafter, the combustion exhaust gas 165 is used as a regenerating gas of the second regenerator C and becomes a wet gas 36c containing a large amount of carbon dioxide.
A conical distributor plate 206 is disposed at the bottom of the cylindrical fluidized-bed furnace. A fluidizing gas supplied through the distributor plate 206 comprises a central fluidizing gas 307 which is supplied from a central portion 304 of the bottom to the interior of the furnace as an upward flow, and a peripheral fluidizing gas 308 which is supplied from a peripheral portion 303 of the bottom to the interior of the furnace as an upward flow.
The central fluidizing gas 307 comprises an oxygen-free gas, and the peripheral fluidizing gas 308 comprises an oxygen-containing gas. The total amount of oxygen in all of the fluidizing gas is set to be 10% or higher and 30% or lower of the theoretical amount of oxygen required for combustion of combustibles. Thus, the interior of the furnace is kept in a reducing atmosphere.
The mass velocity of the central fluidizing gas 307 is set to be smaller than that of the peripheral fluidizing gas 308. The upward flow of the fluidizing gas in an upper peripheral region of the furnace is deflected toward a central region of the furnace by a deflector 306. Thus, a moving bed 309 in which the fluidized medium (silica sand is used) are moved downward and diffused on the distributor plate is formed in the central region of the furnace. In the peripheral region of the furnace, a fluidized bed 310 in which the fluidized medium is actively fluidized is formed. As indicated by the arrows 218, the fluidized medium ascends in the fluidized bed 310 in the peripheral region of the furnace, is deflected by the deflector 306 to an upper portion of the moving bed 309, and descends in the moving bed 309. Then, as indicated by the arrows 212, the fluidized medium moves along the fluidizing gas distributor plate 206 and moves into a lower portion of the fluidized bed 310. In this manner, the fluidized medium circulates in the fluidized bed 310 and the moving bed 309 as indicated by the arrows 218, 212.
While the combustibles 1 supplied to the upper portion of the moving bed 309 by a raw material feeder 201 descend together with the fluidized medium in the moving bed 309, the combustibles are volatilized with heating by the fluidized medium. Because there is no or little oxygen available in the moving bed 309, the pyrolysis gas (produced gas) produced by the gasification, which comprises volatile matter, is not combusted and passes through the moving bed 309 as indicated by the arrows 216. Consequently, the moving bed 309 forms a gasification zone G. The produced gas moves into a freeboard 207 as indicated by the arrow 220, and is discharged from a gas outlet 208 as a produced gas g.
Char (fixed carbon) and tar produced in the moving bed 309 which are not gasified move together with the fluidized medium from the lower portion of the moving bed 309 to the lower portion of the fluidized bed 310 in the peripheral region of the furnace as indicated by the arrows 212, and are partially oxidized by the peripheral fluidizing gas 308 having a relatively large oxygen concentration. Consequently, the fluidized bed 310 forms an oxidization zone S of the combustibles. In the fluidized bed 310, the fluidized medium is heated by the heat of combustion in the fluidized bed. The fluidized medium heated to a high temperature is turned over by the deflector 306 as indicated by the arrows 218, and transferred to the moving bed 309 where it serves as a heat source for gasification. In this manner, the fluidized bed is kept at a temperature ranging from 400 to 1000° C., preferably from 400 to 600° C., thus continuing controlled combustion reaction. A ring-shaped incombustible discharge port 305 is formed at the peripheral portion of the bottom of the fluidized-bed gasification furnace for discharging the incombustibles 222.
According to the fluidized-bed gasification furnace shown in
Next, the swirling-type slagging combustion furnace will be described in more detail. The high-temperature gasification furnace 215 includes a cylindrical primary gasification chamber 215a having a substantially vertical axis, a secondary gasification chamber 215b which is slightly inclined to the horizontal direction, and a tertiary gasification chamber 215c disposed downstream of the secondary gasification chamber 215b and having a substantially vertical axis. A slag discharge port 242 is provided between the secondary gasification chamber 215b and the tertiary gasification chamber 215c. Up to the slag discharge port 242, most of ash content is slagged and discharged through the slag discharge port 242. The produced gas g is supplied via a duct 209 into the swirling-type slagging combustion furnace in the tangential direction so that a swirling flow of the gas is created within the primary gasification chamber 215a. The produced gas supplied into the swirling-type slagging combustion furnace forms a swirling flow, and solid matter contained in the gas is trapped on the circumferential inner wall surface under a centrifugal force. Therefore, advantageously, the percentage of slagging and the percentage of slag collection are high, and slag mist is less likely to be scattered.
Oxygen is supplied into the swirling-type slagging combustion furnace through a plurality of nozzles 234 so as to properly maintain the temperature distribution in the furnace. The temperature distribution is regulated so that the decomposition of hydrocarbons and the slagging of ash are completed in the primary gasification chamber 215a and the secondary gasification chamber 215b. When oxygen is solely supplied, for example, there is a fear of a nozzle being burned. Therefore, oxygen is diluted with steam or the like before supplying, as necessary. Further, steam contributes to steam reforming to reduce the molecular weight of hydrocarbons, and thus should be supplied in a satisfactory amount. This is because the interior of the furnace has a high temperature, and when the amount of the steam is insufficient, condensation polymerization takes place to produce graphite having very low reactivity which leads to unburned fuel loss.
The slag flows down on the lower surface of the secondary gasification chamber 215b, and is discharged as molten slag 226 through the slag discharge port 242. The tertiary gasification chamber 215c serves as a buffer zone which prevents the slag discharge port 242 from being cooled by radiational cooling from a waste heat boiler provided downstream of the tertiary gasification chamber 215c, and serves to reduce the molecular weight of the undecomposed gas. An exhaust port 244 for discharging produced gas is provided at the upper end of the tertiary gasification chamber 215c, and a radiation plate 248 is provided on the lower part of the tertiary gasification chamber 215c. The radiation plate 248 serves to reduce the quantity of heat emitted through the exhaust port 244 by radiation. Reference numeral 232 denotes a start-up burner, and reference numeral 236 denotes a stabilizing burner. Organic matter and hydrocarbons contained in the produced gas are completely decomposed in the high-temperature gasification furnace into hydrogen, carbon monoxide, steam, and carbon dioxide. The gas produced in the high-temperature gasification furnace 215 is discharged from the exhaust gas port 244, and then is cooled to 650° C. or below in the waste heat boiler (not shown) comprising a radiation boiler to solidify molten alkali metal salts. The alkali metal salts after the solidification are then collected by the dust collector (not shown). The high-temperature gasification furnace is not limited to this swirling-type slagging combustion furnace, and may be of other gasification furnace type.
In the raw material feeder 115, the combustibles are in a compressed state within the casings 401, 402 and 403 to thus increase the internal pressure of the feeder 115, and hence air or the like does not enter the raw material feeder 115 from the outside. Further, the squeezing reduces the water content of the combustibles, and thus reduces heat loss caused by the latent heat of vaporization within the low-temperature gasification furnace. The oxygen ratio is lowered by the reduction in heat loss to enhance the cold gas efficiency. The compressed combustibles have relatively uniform density which can reduce a fluctuation in the amount of the supplied materials. Thus, the raw material feeder shown in
By providing another casing (not shown) around the casing 402 so as to have a gap between the casing 402 and this other casing, heating fluid is allowed to flow through the gap to heat the materials 1, thereby performing the squeeze of raw materials effectively. At this time, as a heating fluid, a part of steam from the waste heat boiler 122 or combustion gas from the vent gas burner 163 in
Further, as shown in
Drying and dehydration by heating of materials may be performed by introducing a heating fluid into the casing section of the raw material feeder for thereby introducing heat obtained by a waste heat boiler, heat obtained by combusting hydrogen discharged from a hydrogen electrode of a fuel cell, heat radiated from a fuel cell stack, or heat possessed by a vent gas of a hydrogen electrode or an oxygen electrode of a fuel cell, or by using the above heat as a heat source of an existing material drying apparatus. Specifically, regardless of using a compression-type raw material feeder shown in
Materials 1 which are combustibles are supplied from a raw material feeder 115 to a low-temperature gasification furnace 112 in which the materials 1 are pyrolyzed and gasified at a temperature of 400 to 1000° C., and the produced gas is supplied to a high-temperature gasification furnace 114. Incombustibles 128 in the materials are discharged separately from the low-temperature gasification furnace 112. The produced gas is further gasified at a temperature of 1000 to 1500° C. in the-high-temperature gasification furnace 114 to reduce the molecular weight of the produced gas. The temperature of the high-temperature gasification furnace 114 is maintained at not lower than the temperature in which ash content contained in the produced gas is melted, and 80 to 90% of ash content in the produced gas is slagged and discharged to the outside of the system as molten slag 127. Organic matter and hydrocarbon in the produced gas are completely decomposed into hydrogen, carbon monoxide, carbon, steam, and carbon dioxide in the high-temperature gasification furnace. The produced gas obtained in the high-temperature gasification furnace 114 passes through a high-temperature heat exchanger 121 and a waste heat boiler 122 in which sensible heat is recovered and the temperature of the produced gas is lowered to 200° C., preferably 350° C., and more preferably 500° C. The recovered sensible heat is used for generation of steam, heating of a gasifying agent, or the like.
In the case where combustible materials having an irregular shape such as municipal wastes are materials, the raw material feeder shown in
The produced gas, i.e., the gas 30, to be scrubbed, from which sensible heat has been recovered in the waste heat boiler is led to the first gas scrubbing section A′ of the present invention, and is brought into contact with a first scrubbing liquid 82b in a countercurrent flow. Therefore, the gas 30 to be scrubbed is cooled by the first scrubbing liquid 82b, and strong acid gases such as hydrogen chloride are absorbed in the first scrubbing liquid 82b, and dust components in the gas are entrapped in the first scrubbing liquid 82b. Next, the gas, to be scrubbed, which has been led from the first gas scrubbing section A′ to the second gas scrubbing section A2 is brought into contact with the second scrubbing liquid 82c in a countercurrent flow, and further cooled by the second scrubbing liquid 82c to condense super saturated steam, and weak acid gases such as carbon dioxide and hydrogen sulfide in the gas are absorbed by the second scrubbing liquid 82c. Thus, the scrubbed gas 31 obtained from the second gas scrubbing section A2 becomes a clean gas composed mainly of carbon monoxide and hydrogen having a small solubility in alkaline solution, saturated steam, and carbon dioxide which has not been dissolved in alkaline solution.
On the other hand, the first scrubbing liquid 82b which has absorbed strong acid gases such as hydrogen chloride and whose temperature has increased is sent to the first regenerator B via the gas-liquid separator 3a, and is brought into contact with the first regenerating gas 35b having different components from the gas to be scrubbed and containing oxygen, i.e., a gasifying agent gas 50, for example, an enriched oxygen gas containing oxygen whose oxygen concentration is 80% or more, preferably 90% or more, and more preferably 93% or more, or pure oxygen to generate steam in the first regenerator B until a pressure in the first regenerator B reaches saturated aqueous vapor pressure at a temperature in the first regenerator B.
For example, when the regenerator is operated at an atmospheric pressure (about 0.1 PMa (1 bar)) and a temperature of 80° C., a first regenerator vent gas 36b discharged from the first regenerator accompanies 47% of steam. At the same time, the first scrubbing liquid 82b is deprived of latent heat of vaporization and is cooled. It should be noted that when the first regenerating gas 35b accompanies steam whose amount is equal to or greater than the amount corresponding to saturated aqueous vapor pressure in the first regenerator B, water will not vaporize and the first scrubbing liquid will not be cooled in the first regenerator B. Therefore, it is more preferable that steam content in the first regenerating gas 35b is smaller, i.e., dew point is lower.
Further, because the first scrubbing liquid 82b absorbs strong acid gases in the first gas scrubbing section A′, a pH of the first scrubbing liquid 82b is lowered, and because water content of the first scrubbing liquid 82b is vaporized in the first scrubbing liquid regenerator B, it is necessary to replenish the first alkaline agent and water. Further, in the case where dust is contained in the gas to be scrubbed and is entrapped in the first scrubbing liquid 82b, it is necessary to separate dust from the first scrubbing liquid 82b. In the present invention, a chemical adding apparatus and a filtration apparatus are provided in a circulating passage of the first scrubbing liquid, respectively, whereby the pH of the first scrubbing liquid 82b is adjusted by adding first alkaline agent and a diluting water for diluting alkaline agent to the first scrubbing liquid 82b, and the whole or part of the first scrubbing liquid 82b is always filtrated to remove solid components. Any alkaline substance may be used as alkaline agent, but sodium hydroxide or potassium hydroxide is preferable. If the pH of the first scrubbing liquid 82b to be adjusted, i.e., the pH of the first scrubbing liquid 82b at the inlet of the first gas scrubbing section A′ is 4 or more, then the first scrubbing liquid 82b has an absorption capability for absorbing hydrogen chloride gas and is preferable. However, if the pH of the first scrubbing liquid 82b is 11 or more, the first scrubbing liquid 82b absorbs carbon dioxide besides strong acid gases and is not preferable because of an increased consumption of the first alkaline agent. Therefore, the pH of the first scrubbing liquid 82b at the inlet of the first gas scrubbing section A′ is preferably in the range of 4 to 11, and more preferably 5 to 10. Salts produced by neutralization reaction of the first alkaline agent and strong acid gases are gradually accumulated in the first scrubbing liquid 82b, and a part of the first scrubbing liquid is required to be discharged at all times in order to prevent harmful effect caused by excessive condensation of salts.
On the other hand, the first regenerator vent gas 36b which accompanies saturated steam is heated in the high-temperature heat exchanger 121, and then supplied to the gasification furnace as a gasifying agent and an oxidizing agent for partial oxidization.
With regard to temperature of the first scrubbing liquid 82b, the temperature T1out of the first scrubbing liquid at the outlet of the first gas scrubbing section should be in the range of the boiling point to the boiling point minus 20° C., preferably in the range of the boiling point to the boiling point minus 10° C., and more preferably in the range of the boiling point to the boiling point minus 5° C. Further, the temperature T1in of the first scrubbing liquid at the inlet of the first gas scrubbing section A′ should be in the range of the temperature T1out of the first scrubbing liquid to the temperature T1out minus 20° C., preferably in the range of the saturation temperature of steam in the gas to be scrubbed to the saturation temperature minus 5° C.
The amount of the first scrubbing liquid 82b to be circulated should be determined on the basis of flow rate, temperature and specific heat of the gas to be scrubbed so that the temperature of the first scrubbing liquid meets the temperatures required in the first scrubbing liquid at the outlet and inlet of the first gas scrubbing section A′.
The first scrubbing liquid 82b withdrawn from the first regenerator B is returned to the first gas scrubbing section A′ via the gas-liquid separator 3b.
Further, the second scrubbing liquid 82c which has absorbed carbon dioxide and weak acid gases such as hydrogen sulfide and whose temperature has increased by condensation of steam is sent to the second regenerator C, and is brought into contact with the second regenerating gas 35c having different components from the gas to be scrubbed, for example, combustion exhaust gas 166, in the fuel cell power generation step, discharged from the turbo-charger 164 to generate steam in the second regenerator C until a pressure in the second regenerator C reaches the saturated aqueous vapor pressure at a temperature in the second regenerator C, and to perform regeneration of alkali by decarbonation.
Further, in the present embodiment, it is desirable that absorption and separation of carbon dioxide in the carbon dioxide absorption apparatus 147 of the hydrogen production step 140 is performed completely. However, in order to reduce the concentration of carbon residue in the gas 188 after the carbon dioxide absorption to, for example, 1% or lower, preferably 0.5% or lower, it is necessary to regenerate the second scrubbing liquid completely in the second regenerator C. In the present embodiment, a reboiler 84 is provided to heat the second scrubbing liquid 82c further by using low-pressure steam 124 discharged from a steam turbine 125, thereby accelerating regeneration of the second scrubbing liquid 82c. The second scrubbing liquid 82c may be regenerated only by the low-pressure steam 124 without using the combustion exhaust gas 166. Condensed water 124a discharged from the reboiler 84 is returned to the waste heat boiler 122.
In the present invention, both of inorganic alkaline agent or organic alkaline agent may be used as second alkaline agent. Alkanolamine absorption solution having a high absorbing ability of carbon dioxide is more preferable. Specific examples of absorbents applicable herein include monoethanolamine (MEA), diethanolamine (DEA), and methyldiethanolamine (MDEA) and the like. An absorption reaction by alkanolamine absorption liquid is represented by the following formula. A regenerating reaction of the absorption liquid is a reverse reaction of the following reaction.
R—NH2+H2O+CO2→R—NH3HCO3 (13)
On the other hand, the second regenerator vent gas 36c which accompanies desorbed carbon dioxide and saturated steam is discharged through a condenser 80c and a condensed water separator 81c. The condensed water recovered in the condensed water separator 81c is returned to the interior of the system as a diluting water of the second scrubbing liquid 82c or a diluting water of first alkaline agent or a diluting water of the first scrubbing liquid 82b.
With regard to temperature of the second scrubbing liquid 82c, the temperature T2out of the second scrubbing liquid at the outlet of the second gas scrubbing section A2 should be in the range of the temperature T1in of the first scrubbing liquid at the inlet of the first gas scrubbing section A′ to the temperature T1in minus 20° C., and preferably in the range of the temperature T1in of the first scrubbing liquid at the inlet of the first gas scrubbing section A′ to the temperature T1in minus 10° C. Further, the temperature T2in of the second scrubbing liquid at the inlet of the second gas scrubbing section A2 should be lower than the temperature T2out of the second scrubbing liquid at the outlet of the second gas scrubbing section A2 by 5° C. or more, preferably 10° C. or more, and more preferably 20° C. or more.
The amount of the second scrubbing liquid 82c to be circulated should be determined on the basis of flow rate, temperature and specific heat of the gas to be scrubbed so that the temperature of the second scrubbing liquid meets the temperatures required in the second scrubbing liquid at the outlet and inlet of in the second gas scrubbing section A2.
The second scrubbing liquid 82c withdrawn from the second regenerator C is returned to the carbon dioxide absorption apparatus 147 in the hydrogen production step 140.
On the other hand, the scrubbed gas 31 which has been scrubbed and cooled is pressurized to a pressure of 200 to 800 kPa in a gas compressor 135, and then supplied to the hydrogen production step 140. The gas compressor 135 is driven by a steam turbine 125 which uses high-pressure steam 123 from the waste heat boiler 122. Low-pressure steam 124 discharged from the steam turbine 125 is supplied to the reboiler 84 where the low-temperature steam 124 serves as a heat source for regeneration of the second scrubbing liquid 82c.
The hydrogen production step 140 incorporates a desulfurizing reaction apparatus 141 for removing sulfur content in the produced gas; a shift reaction apparatus 142 for converting carbon monoxide and H2O in the produced gas into hydrogen and carbon dioxide by a shift reaction; a carbon dioxide absorption apparatus 147 for absorbing and removing carbon dioxide in the produced gas after the shift reaction; and a CO removing apparatus 150 for removing carbon monoxide remaining in the gas 188 after carbon dioxide absorption, and the produced gas is sequentially processed in the respective apparatuses to obtain highly enriched hydrogen gas 69. In the CO removing apparatus 150, a selective oxidation apparatus for combusting carbon monoxide in the gas selectively, or a methanation reaction apparatus for producing methane by reacting carbon monoxide and carbon dioxide in the gas with hydrogen, or a hydrogen purifying PSA (pressure swing adsorption apparatus) for adsorbing and separating gas components, other than hydrogen, such as carbon monoxide, carbon dioxide, and nitrogen by adsorbent such activated carbon or zeolite is used.
In the carbon dioxide absorption apparatus 147 of the present embodiment, the carbon dioxide absorption tower 181, a feed pump 182, a heat exchanger 183 and a cooler 184 are provided. The second scrubbing liquid 82c regenerated in the second regenerator C of the acid gas scrubbing apparatus is introduced by a circulation pump 4d into the upper part of the carbon dioxide absorption tower 181 via the heat exchanger 183 and the cooler 184, and is brought into contact with the gas 143 after the shift reaction introduced into the lower part of the absorption tower in a countercurrent flow to absorb carbon dioxide, and then returned by the feed pump 182 from the bottom of the carbon dioxide absorption tower 181 to the second gas scrubbing section A2 via the heat exchanger 183. The second scrubbing liquid 82c is cooled by the cooler 184 to a temperature suitable for absorption of carbon dioxide, preferably 40 to 70° C., and then introduced into the carbon dioxide absorption tower 181. Both of water-cooling or air-cooling may be used as a cooling method in the cooler 184. Further, the second scrubbing liquid 82c discharged from the carbon dioxide absorption apparatus 147 is adjusted to the temperature T2in of the second scrubbing liquid at the inlet of the second gas scrubbing section A2, and then introduced into the scrubbing section.
Further, in the case where carbon dioxide absorption load in the carbon dioxide absorption apparatus 147 is relatively small, i.e., the flow rate of the second absorption liquid to be supplied to the carbon dioxide absorption tower 181 is smaller than the flow rate of the second scrubbing liquid supplied to the second gas scrubbing section A2, the second scrubbing liquid 82c discharged from the second regenerator C is branched, and a part of the second scrubbing liquid 82c is sent to the carbon dioxide absorption apparatus 147 and the remainder is returned to the second gas scrubbing section A2 directly or via a cooler for temperature adjustment. In this case, the second scrubbing liquid 82c discharged from the carbon dioxide absorption apparatus 147 is sent to the second gas scrubbing section A2 or returned to the second regenerator C.
In the fuel cell power generation step 160, the highly enriched hydrogen gas 69 is supplied to a hydrogen electrode of a fuel cell and air 53 is pressurized by the turbo-charger 164 and supplied to an oxygen electrode of the fuel cell, thus generating electricity. The fuel cell may be any fuel cell as far as such fuel cell can use hydrogen as a fuel, and any type of a proton exchange membrane fuel cell, a phosphoric acid fuel cell, a molten carbonate fuel cell and a solid electrolyte fuel cell may be used.
The hydrogen electrode vent gas 161 and the oxygen electrode vent gas 162 are led to the vent gas burner 163 and combusted. Combustion exhaust gas 165 of the vent gas burner 163 is supplied to the turbo-charger 164, and air 53 to be supplied to the oxygen electrode of the fuel cell is pressurized by the turbo-charger 164. Thereafter, the combustion exhaust gas 165 is used as a regenerating gas of the second regenerator C. Further, if regeneration in the second regenerator C is performed only by the low-pressure steam 124, then the combustion exhaust gas 166 from which steam and heat has been recovered is discharged to the outside of the system.
As described above, according to the acid gas scrubbing apparatus and method of the present invention, the acid gas scrubbing apparatus and method can increase energy efficiency and improve an acid gas removal capability in a wet-type scrubber greatly by effectively utilizing low-temperature waste heat of the wet-type scrubber to generate steam and to absorb and separate carbon dioxide. Further, according to the present invention, a gasification system of combustibles which combines the above acid gas scrubbing apparatus having the above advantages and a gasification apparatus, and an incineration system of combustibles which combines the above acid gas scrubbing apparatus and an incinerator can be constituted. Further, a fuel cell power generation system by gasification of combustibles which combines the gasification system of combustibles and a fuel cell can be constituted.
The present invention relates to an acid gas scrubbing apparatus and method in which a gas, to be scrubbed, containing carbon dioxide is brought into contact with a gas scrubbing liquid containing alkaline agent and cooled, and acid gases in the gas are removed. The present invention can be suitably utilized in a gasification system of combustibles which combines the acid gas scrubbing apparatus and a gasification apparatus, an incineration system of combustibles which combines the acid gas scrubbing apparatus and an incinerator, and a fuel cell power generation system by gasification of combustibles which combines the gasification system of combustibles and a fuel cell.
| Number | Date | Country | Kind |
|---|---|---|---|
| 11-205395 | Jul 1999 | JP | national |
| 11-345271 | Dec 1999 | JP | national |
This application is a continuation application of Ser. No. 10/031,397, filed Jan. 18, 2002, which is a National Stage Application of International Application Serial No. PCT/JP00/04857, filed Jul. 19, 2000.
| Number | Date | Country | |
|---|---|---|---|
| Parent | 10031397 | Jan 2002 | US |
| Child | 10965930 | Oct 2004 | US |
