Heat recovery system and power generation system

Abstract: In an improved system for recovering heat from a combustion gas produced by burning combustibles, said combustion gas or a gas produced by partial burning of combustibles is subjected to dust removal in a temperature range of 450 - 650°C at a filtration velocity of 1 - 5 cm/sec under a pressure of from -5 kPa (gage) to 5 MPa before heat recovery is effected. The dust removal is preferably performed using a filter medium which may or may not support a denitration catalyst. The heat recovery is preferably effected using a steam superheater. The dust-free combustion gas may partly or wholly be superheated with an auxiliary fuel or a gasified product to a sufficiently high temperature to permit heat recovery. The combustion furnace may be a gasifying furnace which, in turn, may be combined with a hot melting furnace. If desired, the superheating to a higher temperature may be performed under pressure and the obtained hot combustion gas is supplied to a gas turbine to generate electricity, followed by introduction of the exhaust gas from the turbine gas into a steam superheater for further heat recovery. The system can raise the temperature of superheated steam to a sufficient level to enhance the efficiency of power generation without potential for the corrosion of heat transfer pipes by the combustion gas.

Description: This invention relates to a system for recovering heat from combustion gases or gases produced by partial burning of combustibles, i.e. combustible gases in particular, the invention relates to a heat recovery system that can be applied to the treatment of municipal solid wastes (so-called "municipal wastes" or MW) or waste plastics. The reduction of dioxins and the rendering of soot and dust innocuous are two essential requirements that must be met by recent waste incineration systems. In addition, it has been proposed that new thermal recycling systems be established that can treat wastes not only as materials to be disposed of but also as alternative energy sources. Advanced power generation systems using municipal wastes have been developed with a view to generating electricity at a higher rate of efficiency than conventional systems in the process of burning solid wastes. According to a modified version of this system that utilizes superheating. The steam produced in a waste heat boiler is superheated to a higher temperature with a clean hot combustion gas produced by the combustion of a high-grade fuel of different origin, for example, kerosine or natural gas, and by burning combustion gas from a combustion furnace. Such an independent superheater is used for the purpose of enhancing the efficiency of power generation with steam turbines. The advanced system of power generation from municipal waste utilizing superheating is under active development as being suitable for incineration facilities of a comparatively small scale. Gases produced in the combustion of municipal wastes generally contain HCl which is generated by the combustion of polyvinyl chloride, and if the surface temperature of heat transfer pipes for heat recovery exceeds about 400°C, corrosion of these pipes due to HCl becomes pronounced. To avoid this problem, the temperature of superheated steam must be held lower 400°C but as a result increased efficiency of power generation with steam turbines cannot be achieved by adopting higher temperatures. However, a recent study has revealed that the main cause of corrosion of heat transfer pipes is in fact the deposit of molten salts on the pipes. Municipal wastes have high concentrations of salts such as NaCl (m.p. 800°C) and KCl (m.p. 776°C) and, as the combustion proceeds, these salts form a fume that is deposited on the heat transfer pipes which are low-temperature parts. Since this deposit accelerates the corrosion of the heat transfer pipes, the maximum temperature of the superheated steam that can be tolerated in the existing power generation systems using municipal wastes has been about 300°C, which is such that the surface temperature of heat transfer pipes can be held below about 320°C. Table 1 compares the features of various thermal recycling systems. Obviously, for successful high-efficiency power generation and RDF (refuse-derived fuel) power generation, the use of higher-grade materials is not sufficient and the maintenance of non-corrosive conditions must first be realized. The advanced systems of power generation from MW such as a re-powering system and a combined cycle power generation system involve huge construction and fuel costs and hence require thorough preliminary evaluation of process economy. Deregulation of electric utilities is a pressing need in Japan but, on the other hand, the selling price of surplus electricity is regulated to be low (particularly at night). Under these circumstances, a dilemma exists in that efforts toward fuel-intensive high-efficiency power generation could increase the deficit in corporate's balance sheet. Seeking an ideal is meaningful on its own but some compromise seems necessary from a practical viewpoint. Therefore, what is needed is the creation of an economical and rational power generation system that involves the least increase in construction cost and which also consumes less of fuels other than MW, namely, a new power generation system that can avoid the corrosion problem. The mechanism of corrosion is complicated and various factors are involved in the reaction. However, it can at least be said that the key factor in corrosion is not the concentration of HCl but whether or not NaCl (m.p. 800°C) and KCl (m.p. 776°C) are in such an environment whereby take the form of a fume (molten mist). These salts are fused to deposit on heat transfer pipes and thereby accelerate the progress of corrosion. The molten salts will eventually become complex salt which solidify at temperatures as low as 550 - 650°C and their solidification temperatures vary with the nature (or location) of municipal wastes which, in turn, would be influenced by the quantity and type of the salts. These are major causes of the difficulties involved in the commercial implementation of advanced or high-efficiency power generation systems using MW. Table 2 lists representative causes of corrosion and methods of avoiding it. Causes of Corrosion Corrosion-Preventing Method 1. Acceleration of corrosion due to high-temperature exhaust gases Operation in the medium-temperature exhaust gas region 2. Chlorine-induced corrosion FeO + 2HCl → FeCl 2 + H 2 O Fe 3 C (decomposes) → 3Fe+ C Fe + Cl 2 → FeCl 2 Creating an environment with low levels of HCl, Cl 2 and installing the superheated steam pipes in low-chlorine zones 3. CO-induced corrosion CO reacts with the protective layer on the with heat transfer surfaces with reduction of the ferric oxide (making up this layer). Creating an environment with low CO levels (that is, creating an oxidizing atmosphere) and installing the superheater in these low-CO zones. 4. Alkali-containing accretion depositing on the pipe walls Acceleration of corrosion due to accretion (deposits) of alkali metal salts such as sodium and potassium salts. 1. Do not permit deposits to accrete → In other words, wipe the pipe surfaces with the flow of the fluidizing medium (maintain a weakly fluidized layer). 2. Utilize the heat of the fluidizing medium which has a temperature at which the alkali salts do not melt. 3. Exhaust dust particles in the exhaust gas having a temperature at which the alkali salts are solid and remove the chlorine salts (chlorides) and then use the cleaned exhaust gas. Referring to Table 2 under item 1), the utilization of a medium-temperature region of exhaust gases is a fairly established technology. However, in the stage of the art, a superheated steam temperature of 400°C would be a tolerable limit that can be attained in an exhaust gas temperature region of about 600°C at which the salts will solidify. Hence, the method based on heat recovery from exhaust gases would not be commercially applicable to the high-efficiency thermal recycling systems unless the corrosion problem of molten salts is effectively solved. The methods of avoidance of corrosion which are listed in Table 2 under items 2), 3) and 4-1) and 4-2) are considered to be effective if they are implemented by an internally circulating fluidized-bed boiler system in which a combustion chamber is separated from a heat recovery chamber by a partition wall. The internal circulating fluidized-bed boiler system is attracting the attention of commercial plants since "the fluidized beds can be controlled below temperatures at which alkali salts will melt". However, this method is incapable of avoiding the resynthesis of dioxins. As is well known, dioxins are resynthesized in the boiler sections. Studies on the method of treating shredder dust and its effective use have established a relationship between residual oxygen concentration in exhaust gases and the generation of HCl in fluidized-bed combustion at 800°C. According to the reported data, the generation of HCl was at about 8,000 ppm (almost equivalent to the theoretical) when the residual oxygen concentration was zero but with the increasing residual oxygen concentration, the HCl generation decreased sharply until it was less than 1,000 ppm at 11% O 2 (in a typical state of combustion). The "shredder dust" is a collective term for the rejects of air classification that is performed to recover values from shredded scrap automobiles and the like; the shredder dust is thus a mixture of plastics, rubber, glass, textile scarp, etc. The present inventors conducted a combustion test on shredder wastes using a test apparatus of 30 t·d -1 and found that the concentration of HCl generated was comparable to 1,000 ppm. To investigate the materials balance for the chlorine content, the inventors also analyzed the ash in the bag filter and found that it contained as much as 10.6% chloride ions, with Cu taking the form of CuCl 2 . With regard to CuCl 2 , it has been reported that this compound is a source of the generation of PCDD/PCDF in the incineration process and serves as a catalyst for dioxin resynthesis which is several hundred times as potent as other metal chlorides (ISWA 1988 Proceedings of the 5th Int. Solid Wastes Conference, Andersen, L., Möller, J (eds.), Vol. 1, p. 331, Academic Press, London, 1988). Two of the data in the report are cited here and reproduced in Fig. 5 which shows the effect of Cu concentration on the generation of PCDD (o) and PCDF (Δ) and in Fig. 6 which shows the generation of PCDD (o) and PCDF (Δ) in fly ash as a function of carbon content. The report shows that CuCl 2 and unburnt carbon cause significant effects on the resynthesis of dioxins. It should be noted that carbon tends to remain unburnt in the incineration process since temperatures higher than 1,000°C cannot be attained. EP-A-0 507 422 discloses a combined power generation system in which power generation is achieved by using a combination of a gas turbine and a steam turbine. In the system fuel such as coal and heavy oil is gasified at high temperature and high pressure in a gasification furnace, and the resulting gas is cooled and purified by a heat exchanger, a dust collector and a gas separation apparatus, and then supplied to a gas turbine. Further, attention is drawn to DE 43 421 65 C1, which discloses a combined power generation system using an externally circulating fluidized bed furnace as a gasification furnace. In this system, wastes or coal is crushed in a shredder, and dried and pyrolyzed in a heater which is oil-heated. The resulting pyrolyzed gas is burned in a combustion chamber, and the resulting combustion gas is used as fluidizing gas for the gasification furnace. Pyrolyzed char is directly supplied to the gasification furnace, where it is gasified. Resulting product gas from the gasification furnace is subjected to heat-exchange with compressed product gas from a gas-compressor in a recuperator and then with oil in another recuperator. Then it is subjected to dust-filtration in a dust-collector, and thereafter cooled and washed in a scrubber. The present invention has been accomplished under these circumstances and has as an object the provision of a heat recovery system and a power generation system that can enhance the efficiency of power generation by sufficiently increasing the temperature of superheated steam without inducing the corrosion of heat transfer pipes by combustion gases and which yet is capable of suppressing the resynthesis of dioxins in the latter stage. This object of the invention can be attained by a system for recovering heat from combustion gases produced by complete or partially burning of combustibles, in which either of said gases (i.e. combustion gases by complete burning or combustion gases by partial burning; the latter gases being also called combustible gases) is subjected to dust removal in a temperature range of 450- 650°C at a filtration velocity of 1 - 5 cm/sec under a pressure of from -5 kPa (gage) to 5 MPa before heat recovery is effected. In the heat recovery system, dust removal is preferably performed using a filter medium such as a ceramic filter which may or may not support a denitration catalyst. Heat recovery in the system may be performed using a steam superheater. Thus, in the present invention, not only the molten salts which will cause corrosion but also CaCl 2 (produced by the reaction CaO + 2HCl → CaCl 2 + H 2 O) are removed as solidified salts by dust removal in the temperature range of 450 - 650°C and this contributes to avoiding the corrosion of heat transfer pipes in the superheater by the molten salts and HCl. Further, the filter medium which may or may not support a denitration catalyst can remove CuO and/or CuCl 2 which are catalysts for dioxin resynthesis and, hence, the heat recovery system of the invention is also capable of suppressing the resynthesis of dioxins in the latter stage. In the invention, the combustion gas or combustible gas may be partly or wholly reburnt with or without an auxiliary fuel to a sufficiently high temperature to permit heat recovery. The reburning of the combustible gas may be performed by supplying air or oxygen-enriched air or pure oxygen. The reburning of the combustion gas with an auxiliary fuel may be performed using the residual oxygen in the combustion gas. The combustible gas may be obtained by partial burning of combustibles. The combustible gas may also be obtained by carrying out a gasification reaction in a low temperature fluidized-bed gasification furnace having a fluidized bed temperature of 450 - 650°C. Thus, according to the present invention, the absence of salts contributes to avoiding the corrosion of heat transfer pipes in the superheater which would otherwise occur at an elevated temperature if molten salts were present and, as a result, steam can be superheated to a sufficiently high temperature. It should be noted that the gasification reaction which is a reducing reaction is not likely to generate CuO. In addition, carbon will hardly remain unburnt if complete combustion is performed at 1,300°C and above in a melting furnace provided at a stage subsequent to the gasification step. Therefore, the gasification and melting system of the invention is the most rational method for suppressing the resynthesis of dioxins. The object of the invention can also be attained by a heat recovery and power generation system which is an extension of the above-described heat recovery system in that combustion, gasification, dust removal and reburning are performed under pressure and that the combustion or combustible gas having an elevated temperature is supplied to a gas turbine for power generation, followed by the introduction of the exhaust gas from the turbine into a steam superheater for heat recovery. In the heat recovery method of the invention, the temperature of the combustion or combustible gas can be lowered to 450 - 650°C by collecting heat in a boiler in a conventional manner, with the temperature of the steam side held below 300°C and the surface temperature of heat transfer pipes held below 320°C. In addition, the temperature of superheated steam can be raised to about 400°C in a gas temperature region below 600°C. If desired, the step of dust removal may be preceded by blowing the powder of limestone, calcium oxide, slaked lime or the like into the combustion or combustible gas so that they are reacted with the HCl in the gas. Thus, HCl can be removed sufficiently to ensure that the corrosive nature of the combustion gas is further reduced by a significant degree. Fig. 1 is a flow sheet for a heat recovery system involving a reburning in one embodiment of the invention; Fig. 2 is a flow sheet for a heat recovery system employing the combination of gasification and melting with a reburning in another embodiment of the invention; Fig. 3 is a flow sheet for a heat recovery system employing the combination of fluidized-bed gasification and melting with the step of reburning by the firing of a combustible gas in accordance with yet another embodiment of the invention; Fig. 4 is a flow sheet for a combined cycle power plant employing a gasifying furnace in accordance with a further embodiment of the invention; Fig. 5 is a graph showing the effect of CuCl 2 concentration on the generation of PCDD and PCDF; Fig. 6 is a graph showing the generation of PCDD and PCDF in fly ash as a function of C content; and Fig. 7 is a flow sheet for a test plant, with test data included, that was operated to evaluate the effectiveness of a medium-temperature filter in preventing the corrosion of heat transfer pipes while suppressing the resynthesis of dioxins. When molten, NaCl (m.p. 800°C) and KCl (m.p. 776°C) occur as complex salts and exhibit a strong corrosive action if they are deposited on heat transfer pipes. On the other hand, the complex salt are solidified at 550 - 650°C, so most of them can be trapped if dust removal is performed at temperatures below the melting points (solidification points) of these complex salts. Therefore, if the combustion gas resulting from the burning of municipal wastes is subjected to dust removal at a temperature lower than the melting points of the complex salts in the combustion gas, the heat transfer pipes installed at the latter stage can be prevented from being corroded by the molten salts. If the temperature of superheated steam is to be increased to 400 - 500°C with a view to improving the efficiency of power generation, the temperature on the combustion gas side is desirably increased to at least 600°C and above in consideration of initial investment. In this connection, the dust-free combustion gas can be used as a satisfactory heat source since it contains no salts. When the gas is reburnt an auxiliary fuel such as natural gas is performed by making use of the residual oxygen in the combustion gas, the consumption of the auxiliary fuel is markedly reduced and so is the amount of the combustion gas as compared with the heretofore proposed method of using an independent reburner and uperheater in the power generating system. The consumption of the auxiliary fuel can be reduced and the increase in the amount of the combustion gas suppressed by branching part of the combustion gas such that the gas to be reburnt is limited to the necessary minimum heat value for superheating the steam. If the content of residual oxygen in the combustion gas is small, combustion air must be added. if oxygenenriched air or pure oxygen is used in place of combustion air, the consumption of the auxiliary fuel can be suppressed and yet the temperature of the combustion gas can be sufficiently increased while preventing the increase in the amount of the combustion gas that need be treated. If the waste is gasified under a deficiency of oxygen to produce combustible gas, such as easily may be reburnt merely by supplying oxygen-containing gas such as air at a later stage instead of using high quality auxiliary fuel, thus partly or completely eliminating the need to use the auxiliary fuel. If the wastes contain copper (Cu), their gasification offers a further benefit because in the reducing atmosphere, copper (Cu) is not likely to form copper oxide (CuO) which is known to work as a catalyst for accelerating dioxin synthesis and, hence, is capable of reducing the potential of dioxin synthesis in the latter stage. If a fluidized-bed furnace is used in the gasification stage, the occurrence of a local hot zone can be prevented and a system operation in the low-temperature range of 450 - 650°C can be realized to accomplish a highly effective prevention of copper oxidation. It should be noted, here, that if the gasified i.e. combustible gas has only a low heat value, oxygen-enriched air or pure oxygen rather than combustion air may be employed so as to restrict the consumption of the auxiliary fuel and yet increase the temperature of the gas while suppressing the increase in the amount of the combustion gas to be treated. It should also be noted that the product gas from the gasifying furnace contains a large amount of solids in an ungasified and unburnt state. If such a gas is directly passed through a filter, a clogging trouble may occur on account of the solid unburnt content and tar. To avoid this problem, part or all of the combustible gas may be burnt in a high temperature furnace provided downstream of the gasification furnace before it is passed through the filter, so that the temperature of the gas is elevated to a level that causes decomposition of the solid unburnt content and the tar content in the combustion gas. This is effective in solving the filter problem associated with the solid unburnt content and tar. In addition, the combustion gas is heated to a sufficiently high temperature to enable the decomposition of dioxins and other organochlorines in the combustion gas. If the temperature elevation is performed in a melting furnace such that the produced gas is heated to a temperature that causes the melting of the ash content, the latter can be recovered as molten slag and, at the same time, the load on the filter can be reduced. Another advantage of using a melting furnace is that any copper oxide (CuO) that may be generated in the gasification furnace can be converted to molten slag, thereby further reducing the potential of dioxins resynthesis in the latter stage. Ceramic filters are suitable for use as dust removers in the temperature range of 450 - 650°C at a filtration velocity of 1 - 5 cm/sec under a pressure of from -5 kPa (gage) to 5 MPa. For use at elevated temperatures, ceramic filters of tube, candle and honeycomb types are currently under development but those for use in the temperature range of 450 - 650°C which is contemplated by the invention are already in the stage of commercialization. The honeycomb-type filter has the particular advantage that it provides a sufficiently large filtration area per unit volume to enable the fabrication of a small filter unit. A problem with this type of filter is that if the diameter of honeycomb cells is small, the chance of the formation of adjust bridge will increase, causing the need to perform frequent backwashing. If such a problem is anticipated, a system capable of reducing the load on the filter and the combination of the aforementioned gasifying and melting furnaces will be an effective system. Needless to say, this system is also effective in the case of municipal wastes having a high ash content. If the honeycomb-type filter is used to remove the aforementioned copper chloride (CuCl 2 ) and copper oxide (CuO) to a fine dust level, the potential of dioxin resynthesis at the latter stage can be reduced to an infinitesimally small level. The ceramic filters for use in the invention may be made of alumina-based compounds such as mullite and cordierite, or highly corrosion-resistant titanium dioxide. For operations in a reducing atmosphere, filters made of highly corrosion-resistant non-oxide base ceramics such as silicon carbide and silicon nitride may be used. If catalysts such as vanadium pentoxide and platinum are supported on the surfaces of the ceramic filters, not only the dust component of the combustion gas but also nitrogen oxides and dioxins can be reduced. The thus prepared dust-free combustion or combustible gas is not only low in corrosive nature, but also the potential of "ash cut", or wear by dust, is sufficiently reduced to achieve a significant increase in the gas flow rate on the combustion or combustible gas inside a heat exchanger; as a result, the pitch of heat transfer pipes can be reduced and yet the heat transfer coefficient that can be achieved is improved, whereby the size of the heat exchanger is sufficiently reduced to realize a substantial decrease in the initial investment. If combustion or gasification is performed under pressure and dust removal in the temperature range of 450 650°C is followed by introduction of the hot combustion or combustible gas into a gas turbine, combined cycle power generation is realized, leading to the construction of a high-efficiency power recovery system. The present invention will now be described in greater detail with reference to the accompanying drawings. Fig. 1 is a flow sheet for a heat recovery system involving a superheating and reburning step in one embodiment of the invention. A combustion furnace 1 is supplied with municipal wastes 10, which are combusted to generate a combustion exhaust gas. The gas is then supplied to a waste heat boiler 2, where it is cooled to 450 - 650°C with heated water 19 coming from an economizer 6. Recovered from the waste heat boiler 2 is saturated steam 20 having a temperature of about 300°C and a pressure of about 80 kgf/cm 2 . Subsequently, the combustion exhaust gas is freed of dust in a temperature range of 450 - 650°C at a filtration velocity of 1 - 5 cm/sec under a pressure of from -5 kPa (gage) to +2 kPa (gage) by means of a medium-temperature filter 3. In addition to the feed waste, the combustion furnace 1 may be charged with a neutralizing agent 13 such as limestone for the purpose of desalting. If necessary, a neutralizing agent 13 such as slaked lime may be introduced into a flue 12 connecting to the filter so as to remove the HCl in the exhaust gas absorption. Stream 14 which is part or all of the combustion exhaust gas exiting the medium-temperature filter 3 is supplied to a heating furnace 4, where it is reburnt to a higher temperature with an auxiliary fuel 15. The thus-heated exhaust gas 16 is sent to a steam superheater 5, where saturated steam 20 coming from the waste heat boiler 2 is superheated to about 500°C. The combustion exhaust gas 17 goes to the economizer 6 and an air heater 7 for heat recovery; thereafter, the exhaust gas passes through an induced blower 8 to be discharged from a stack 9. The steam 21 superheated in the steam superheater 5 is sent to a steam turbine 22 for generation electricity 28. If the saturated steam 20 is directed into a region in the waste heat boiler 2 where the exhaust gas temperature is below about 600°C such that said steam is heated to a temperature about 400°C which is the temperature of the superheated steam, saving of the auxiliary fuel 15 can be accomplished. Denoted by 11 and 18 in Fig. 1 are noncombustibles and water. Fig. 2 is a flow sheet for a heat recovery system employing a reburning that is combined with gasification and melting which are performed to insure complete combustion. As shown, municipal wastes 10 are gasified in a gasification furnace 23 to generate a combustible gas, which is oxidized at high temperature in the subsequent melting furnace 24 together with char, whereby the solid unburnt content is decomposed and the ash content is converted to molten slag 25. The hot combustion gas is fed into a waste heat boiler 2, where it is cooled to 450 - 650°C with heated water 19 coming from an economizer 6, thereby recovering saturated steam 20 having a temperature of about 300°C and a pressure of about 80 kgf/cm 2 . Subsequently, the combustion gas is supplied to a medium-temperature filter 3 for dust removal in a temperature range of 450 - 650°C at a filtration velocity of 1 - 5 cm/sec under a pressure of from -5 kPa (gage) to +2 kPa (gage). A neutralizing agent 13 such as slaked lime is introduced into a flue 12 connecting to the medium-temperature filter 3 so that the HCl in the combustion gas is removed by absorption. Stream 14 which is part or all of the combustion gas exiting the medium-temperature filter 3 is supplied to a heating furnace 4, where it is reburnt with an auxiliary fuel 15 and thereby heated to a higher temperature. The thus-heated combustion gas 16 is directed to a steam superheater 5, where the saturated steam 20 coming from the waste heat boiler 2 is superheated to about 500°C. The combustion gas 17 exiting the steam superheater 5 goes to the economizer 6 and an air heater 7 for further heat recovery. Thereafter, the combustion gas passes through an induced blower 8 to be discharged from a stack 9. The steam 21 superheated in the steam superheater 5 is sent to a steam turbine 22 for use in generating electricity 28. The auxiliary fuel can be saved by the same method as described in connection with the system shown in Fig. 1. Denoted by 11 and 18 in Fig. 2 are noncombustibles and water, respectively. Fig. 3 is a flow sheet for a heat recovery system employing the combination of fluidized-bed gasification and melting with reburning by firing of a combustible gas in accordance with yet another embodiment of the invention. A fluidized-bed gasification furnace 30 has a small air ratio and the temperature of the fluidized bed is held as low as 450 - 650°C such that the gasification reaction will proceed at a sufficiently slow rate to produce a homogeneous gas. In the conventional incinerator, the combustion temperature is so high that aluminum (m.p. 660°C) will melt and accompany the exhaust gas to produce fly ash, whereas iron and copper are oxidized to yield materials which, when recycled, have only low commercial value. In contrast, the fluidized-bed gasification furnace 30 has a sufficiently low fluidized-bed temperature and yet is filled with a reducing atmosphere so that metals such as iron, copper and aluminum can be recovered unoxidized and in a clean state with the combustible deposit having been gasified away to make those metals suitable for materials recycling. A swirl melting furnace 31 has a drum consisting of vertical primary combustion chamber, an inclined secondary combustion chamber and a slag separating section. A charcontaining gas blown into the furnace is burnt at high temperature as it swirls together with combustion air whereas molten slag 25 descends the inside surface of the furnace wall to drop into the secondary combustion chamber and thence flows down the inclined bottom surface. In the slag separating section, a radiation plate maintains the slag temperature and thereby enables a consistent slag flowout 25. Thus, the ie. combustible gas and char that have been generated in the gasification furnace 30 are gasified at a high temperature of about 1,350°C and thereby convert the ash content to molten slag while ensuring complete decomposition of dioxins and the like. The hot gas exiting the melting furnace 31 enters a waste heat boiler 32; containing unburnt gases such as hydrogen and methane, the hot gas is cooled to 450 - 650°C in the boiler 32 whereby steam is recovered. Thereafter, the gas is passed through a medium-temperature filter 33 to remove dust such as solidified salts in a temperature range of 450 - 650°C at a filtration velocity of 1 - 5 cm/sec under a pressure of from -5 kPa (gage) to +2 kPa (gage). The dust-free gas then enters a heater 34, which is supplied with air, oxygen or the like to return the gas without feeding any external fuel. It should be noted that the applicability of the method shown in Fig. 3 is limited to municipal wastes 10 having high heat value. Denoted by 35, 36 and 37 respectively are an economizer, an air heater and a steam turbine for high-efficiency power generation. Fig. 4 is a flow sheet for a combined cycle power plant employing a gasifying furnace in accordance with a further embodiment of the invention. As shown in Fig. 4, municipal wastes 10 are gasified in a gasifying furnace 23 to generate combustible gas which, together with char, is oxidized at high temperature in the subsequent melting furnace 24, where the ash content is converted to molten slag 25. The hot combustible gas is supplied to a waste heat boiler 2, where it is cooled to 450 - 650°C with heated water 19 coming from an economizer 6 so as to recover saturated steam having a temperature of about 300°C and a pressure of about 80 kgf/cm 2 . The combustible gas is then passed through a medium-temperature filter 3 for dust removal in a temperature range of 450 - 650°C at a filtration velocity of 1 - 5 cm/sec under a pressure of from 102 kPa (gage) to 5 MPa. A neutralizing agent 13 such as slaked lime is introduced into a flue 12 connecting to the medium-temperature filter 3 such that the HCl in the gas is removed by absorption. All of the steps described up to here are performed within a pressure vessel 26. Stream 14 of the combustible gas exiting the filter 3 is supplied, together with combustion air 15, into a gas turbine 27 for generating electricity 28. Exhaust gas 16 from the gas turbine 27 is fed into a steam superheater 5, where the steam 20 coming from the waste heat boiler 2 is superheated to 500°C and is thence supplied to the economizer 6 and an air heater 7 for heat recovery; thereafter, the exhaust gas is passed through an induced blower 8 and discharged from a stack 9. The steam 21 exiting the steam superheater 5 is sent to a steam turbine 22 for generating electricity 28. Denoted by 18 in Fig. 4 is water. Fig. 7 is a flow sheet for a test plant, with test data included, that was operated to evaluate the effectiveness of a medium-temperature filter in preventing the corrosion of heat transfer pipes while suppressing dioxin (DXN) resynthesis. When the medium-temperature filter 3 was to be used, it was in the form of a honeycomb filter made of an alumina-based ceramic material and the combustion gas was passed through this filter to remove dust at 500°C. When no medium-temperature filter was used, the steam temperature was 500°C and the service life of the heat transfer pipes in the steam superheater 5 was 2,000 hours. By allowing the combustion gas having a temperature of 900°C to pass through a radiation boiler 2, the DXN concentration was reduced by about 35%; on the other hand, passage through the steam superheater + boiler (5 + 2), economizer 6 and air heater 7, DXN was resynthesized to have its concentration increased by a factor of at least 200; therefore, the DXN was removed together with dust by passage through a bag filter 38 and a scrubber 39 before the combustion gas was discharged from a stack 9. When the medium-temperature filter 3 was used, the steam temperature was 500°C and the service life of the heat transfer pipes in the steam superheater 5 was 4,000 hours, accompanied by a 0.1 mm reduction in wall thickness. There was no detectable DXN resynthesis. In the prior art, if one attempts to increase the steam temperature with a view to improving the efficiency of power generation by a steam turbine, the corrosion by molten salts and the like in the combustion gas is accelerated at a heat transfer pipe temperature in excess of about 400°C and, hence, the steam temperature must be heat below 400°C. In contrast, by using the medium-temperature filter to remove the molten salts in the combustion or combustible gas before it enters the steam superheater, the corrosion of the heat transfer pipes is sufficiently suppressed that the steam temperature can be raised to about 500°C, thereby improving the efficiently of power generation. In accordance with the present invention, the salts in a combustion or combustible gas are removed by performing a dust removal step at a temperature of 450 - 650°C which enables the solidification of molten salts; therefore, the dust-free combustion or combusticle gas can be sufficiently reburnt and heated without causing the corrosion of heat transfer pipes in a superheater. This contributes to an improvement in the efficiently of power generation using combustion gases produced by burning municipal waste and/or RDF. If this technology is combined with a dechlorination method using neutralizing agents, the corrosive nature of such combustion or combustible gases can be further reduced by a significant degree. In addition, the resynthesis of dioxins can be suppressed.

Claims: A method of recovering heat and generating power from wastes (10), said method comprising: burning said wastes (10) to thereby produce combustion gas containing at least one of alkali metal chlorides, calcium chloride, copper oxide and copper chloride; cooling said combustion gas in a waste heat boiler (2) to produce steam (20); subjecting the thus cooled combustion gas to dust filtration at a temperature of from 450-650°C to thereby remove any said alkali metal chlorides, said calcium chloride, said copper oxide and said copper chloride as solidified materials, and thereby producing cooled and filtered combustion gas; reburning said cooled and filtered combustion gas with auxiliary fuel (15) to thereby reheat the combustion gas to a temperature sufficient to permit heat recovery therefrom; introducing the thus reheated combustion gas into a steam superheater (5), and passing said steam (20) through said steam superheate (5), thereby recovering heat from said combustion gas (16) and superheating said steam (20); and introducing the thus superheated steam (21) into a steam turbine (22) and therein generating power. A method as claimed in claim 1, wherein said filtration is conducted by a ceramic filter (3). A method as claimed in claim 2, wherein said filter (3) supports a denitration catalyst. A method as claimed in claim 1, wherein said filtration is conducted by a filter supporting a denitration catalyst. A method as claimed in claim 1, further comprising discharging said combustion gas from said steam superheater (5), passing the thus discharged combustion gas through at least one of an economizer (6) and a preheater (7) to recover heat from said combustion gas to form cooled gas, and passing said cooled gas to the atmosphere, A method as claimed in claim 1, further comprising introducing neutralizing agent (13) into at least one of said wastes (10) and said combustion gas prior to said filtration. A method as claimed in claim 6, wherein said neutralizing agent (13) comprises limestone or slaked lime. A method of recovering heat and generating power from wastes (10), said method comprising: gasifying said wastes (10) at a low temperature to thereby produce combustible gas; burning said combustible gas at high temperature to produce combustion gas containing at least one of alkali metal chlorides, calcium chloride, copper oxide and copper chloride; cooling said combustion gas in a waste heat boiler (2) to produce steam (20); subjecting the thus cooled combustion gas to dust filtration at a temperature of from 450-650°C to thereby remove any said alkali metal chlorides, said calcium chloride, said copper oxide and said copper chloride as solidified materials, and thereby producing filtered combustion gas; reburning said filtered combustion gas with auxiliary fuel (15) to thereby reheat the combustion gas to a temperature sufficient to permit heat recovery therefrom; introducing the thus reheated combustion gas into a steam superheater (5), and passing said steam through said steam superheater (5), thereby recovering heat from said combustion gas and superheating said steam (20); and introducing the thus superheated steam (21) into a steam turbine (22) and therein generating power, A method as claimed in claim 8, wherein said filtration is conducted by a ceramic filter (3). A method as claimed in claim 9, wherein said filter (3) supports a denitration catalyst. A method as claimed in claim 8, wherein said filtration is conducted by a filter (3) supporting a denitration catalyst. A method as claimed in claim 8, further comprising discharging said combustion gas from said steam superheater (5), passing the thus discharged combustion gas through at least one of an economizer (6) and a preheater (7) to recover heat from said combustion gas to form cooled gas, and passing said cooled gas to the atmosphere. A method as claimed in claim 8, further comprising introducing neutralizing agent (13) into at least one of said wastes (10) and said combustion gas prior to said filtration. A method as claimed in claim 13, wherein said neutralizing agent (13) comprises limestone or slaked lime. A method of recovering heat and generating power from wastes (10), said method comprising: gasifying said wastes (10) at a low temperature to thereby produce low temperature combustible gas; gasifying said said low temperature combustible gas at high temperature to produce high temperature combustible gas containing at least one of alkali metal chlorides, calcium chloride, copper oxide and copper chloride; cooling said high temperature combustible gas in a waste heat boiler (32) to produce steam (20); subjecting the thus cooled combustible gas to dust filtration at a temperature of from 450-650°C to thereby remove any said alkali metal chlorides, said calcium chloride, said copper oxide and said copper chloride as solidified materials, and thereby producing filtered combustible gas; reburning said filtered combustible gas with air, oxygenated air or oxygen to thereby reheat the gas to a temperature sufficient to permit heat recovery therefrom; introducing the thus reheated gas into a steam superheater, and passing said steam through said steam superheater (34), thereby recovering heat from said gas and superheating said steam (20); and introducing the thus superheated steam (21) into a steam turbine (37) and therein generating power. A method as claimed in claim 15, wherein said filtration is conducted by a ceramic filter (33). A method as claimed in claim 16, wherein said filter (33) supports a denitration catalyst. A method as claimed in claim 15, wherein said filtration is conducted by a filter (33) supporting a denitration catalyst. A method as claimed in claim 15, further comprising discharging said gas from said steam superheater (34), passing the thus discharged gas through at least one of an economizer (35) and a preheater (36) to recover heat from said gas to form cooled gas, and passing said cooled gas to the atmosphere. A method as claimed in claim 15, further comprising introducing neutralizing agent (13) into at least one of said wastes (10) and said combustible gas prior to said filtration. A method as claimed in claim 20, wherein said neutralizing agent (13) comprises limestone or slaked lime. A method of recovering heat and generating power from wastes (10), said method comprising: gasifying said wastes (10) at a low temperature to thereby produce low temperature combustible gas; gasifying said low temperature combustible gas at high temperature to produce high temperature combustible gas containing at least one of alkali metal chlorides, calcium chloride, copper oxide and copper chloride; cooling said high temperature combustible gas in a waste heat boiler (2) to produce steam (20); subjecting the thus cooled combustible gas to dust filtration at a temperature of from 450-650°C to thereby remove any said alkali metal chlorides, said calcium chloride, said copper oxide and said copper chloride as solidified materials, and thereby producing filtered combustible gas; introducing said filtered combustible gas and oxygen containing gas into a gas turbine (27) and therein burning said filtered combustible gas, thereby generating power and reheating the gas to a temperature sufficient to permit heat recovery therefrom; introducing the thus reheated gas into a steam superheater (5), and passing said steam through said steam superheater (5), thereby recovering heat from said gas and superheating said steam (20); and introducing the thus superheated steam (21) into a steam turbine (22) and therein generating power. A method as claimed in claim 22, wherein said filtration is conducted by a ceramic filter (3). A method as claimed in claim 23, wherein said filter (3) supports a denitration catalyst. A method as claimed in claim 22, wherein said filtration is conducted by a filter (3) supporting a denitration catalyst. , A method as claimed in claim 22, further comprising discharging said gas from said steam superheater (5), passing the thus discharged gas through at least one of an economizer (6) and a preheater (7) to recover heat from said gas to form cooled gas, and passing said cooled gas to the atmosphere. A method as claimed in claim 22, further comprising introducing neutralizing agent (13) into at least one of said wastes and said combustible gas prior to said filtration. A method as claimed in claim 27, wherein said neutralizing agent (13) comprises limestone or slaked lime. A method as claimed in claim 22, wherein said gasifying at a low temperature, said gasifying at a high temperature and said filtration are conducted at a pressure of from 102 kPa to 5.0 MPa. An apparatus for recovering heat and generating power from wastes (10), said apparatus comprising: a furnace (1) to burn wastes and thereby produce combustion gas containing at least one of alkali metal chlorides, calcium chloride, copper oxide and copper chloride; a waste heat boiler (2) for cooling the combustion gas and for producing steam; a dust filter (3) for filtering the thus cooled combustion gas at a temperature of from 450-650°C to thereby remove therefrom the alkali metal chlorides, calcium chloride, copper oxide and copper chloride as solid materials; a furnace (4) for reburning the thus filtered combustion gas with auxiliary fuel (15) to thereby reheat the combustion gas to a temperature sufficient to permit heat recovery therefrom; a steam superheater (5) to receive the thus reheated combustion gas and the steam and to superheat the steam by recovery of heat from the combustion gas; and a steam turbine (22) to receive the thus superheated steam and thereby to generate power. An apparatus as claimed in claim 30, wherein said dust filter (3) comprises a ceramic filter. An apparatus as claimed in claim 31, wherein said filter (3) supports a denitration catalyst, An apparatus as claimed in claim 30, wherein said filter (3) supports a denitration catalyst. An apparatus as claimed in claim 30, further comprising at least one of an economizer (6) and a preheater (7) to recover heat from combustion gas discharged from said steam superheater (5), and means for then discharging the gas to the atmosphere. An apparatus as claimed in claim 30, further comprising means for introducing neutralizing agent (13) into at least one of the wastes (10) and the combustion gas prior to filtration by said dust filter (3). An apparatus for recovering heat and generating power from wastes, said apparatus comprising: a gasifier (23) for gasifying wastes (10) at a low temperature and thereby produce combustible gas; a furnace (23) for burning the combustible gas at high temperature to produce combustion gas containing at least one of alkali metal chlorides, calcium chloride, copper oxide and copper chloride; a waste heat boiler (2) for cooling the combustion gas and for producing steam; a dust filter (3) for filtering the thus cooled combustion gas at a temperature of from 450-650°C to thereby remove therefrom the alkali metal chlorides, calcium chloride, copper oxide and copper chloride as solid materials; a furnace (4) for reburning the thus filtered combustion gas with auxiliary fuel (15) to thereby reheat the combustion gas to a temperature sufficient to permit heat recovery therefrom: a steam superheater (5) to receive the thus reheated combustion gas and the steam and to superheat the steam by recovery of heat from the combustion gas; and a steam turbine (22) to receive the thus superheated steam and thereby to generate power. An apparatus as claimed in claim 36, wherein said dust filter (3) comprises a ceramic filter. An apparatus as claimed in claim 37, wherein said filter (3) supports a denitration catalyst, An apparatus as claimed in claim 36, wherein said filter (3) supports a denitration catalyst. An apparatus as claimed in claim 36, further comprising at least one of an economizer (6) and a preheater (7) to recover heat from combustion gas discharged from said steam superheater (5), and means for then discharging the gas to the atmosphere. An apparatus as claimed in claim 36, further comprising means for introducing neutralizing agent (13) into at least one of the wastes and the combustion gas prior to filtration by said dust filter (3). An apparatus for recovering heat and generating power from wastes (10), said apparatus comprising: a low temperature gasifier (30) for gasifying wastes at a low temperature and thereby produce low temperature combustible gas; a high temperature furnace (31) for gasifying the low temperature combustible gas at a high temperature to produce high temperature combustible gas containing at least one of alkali metal chlorides, calcium chloride, copper oxide and copper chloride; a waste heat boiler (32) for cooling the high temperature combustible gas and for producing steam; a dust filter (33) for filtering the thus cooled combustible gas at a temperature of from 450-650°C to thereby remove therefrom the alkali metal chlorides, calcium chloride, copper oxide and copper chloride as solid materials; a furnace (34) for reburning the thus filtered combustible gas with air, oxygenated air of oxygen to thereby reheat the gas to a temperature sufficient to permit heat recovery therefrom; a steam superheater to receive the thus reheated gas and the steam and to superheat the steam by recovery of heat from the gas; and a steam turbine (37) to receive the thus superheated steam and thereby to generate power. An apparatus as claimed in claim 42, wherein said dust filter (33) comprises a ceramic filter. An apparatus as claimed in claim 43, wherein said filter supports a denitration catalyst. An apparatus as claimed in claim 42, wherein said filter (33) supports a denitration catalyst. An apparatus as claimed in claim 42, further comprising at least one of an economizer (35) and a preheater (36) to recover heat from the gas discharged from said steam superheater, and means for then discharging the gas to the atmosphere. An apparatus as claimed in claim 42, further comprising means for introducing neutralizing agent into at least one of the wastes and the combustible gas prior to filtration by said dust filter (33). An apparatus for recovering heat and generating power from wastes (10), said apparatus comprising: a low temperature gasifier (23) for gasifying wastes at a low temperature and thereby produce low temperature combustible gas; a high temperature furnace (34) for gasifying low temperature combustible gas at a high temperature to produce high temperature combustible gas containing at least one of alkali metal chlorides, calcium chloride, copper oxide and copper chloride; a waste heat boiler (2) for cooling the high temperature combustible gas and for producing steam; a dust filter (3) for filtering the thus cooled combustible gas at a temperature of from 450-650°C to thereby remove therefrom the alkali metal chlorides, calcium chloride, copper oxide and copper chloride as solid materials; a gas turbine (27) to burn the thus filtered combustible gas with oxygen containing gas, thereby to generate power and to reheat the gas to a temperature sufficient to permit heat recovery therefrom; a steam superheater (5) to receive the thus reheated gas and the steam and to superheat the steam by recovery of heat from the gas; and a steam turbine (22) to receive the thus superheated steam and thereby to generate power. An apparatus as claimed in claim 48, wherein said dust filter (3) comprises a ceramic filter. An apparatus as claimed in claim 49, wherein said filter (3) supports a denitration catalyst. An apparatus as claimed in claim 48, wherein said fliter (3) supports a denitration catalyst. An apparatus as claimed in claim 48, further comprising at least one of an economizer (6) and a preheater (7) to recover heat from the gas discharged from said steam superheater (5), and means for then discharging the gas to the atmosphere. An apparatus as claimed in claim 48, further comprising means for introducing neutralizing agent (13) into at least one of the wastes and the combustible gas prior to filtration by said dust filter (3). An apparatus as claimed in claim 48, wherein said low temperature gasifier (23), said high temperature (24) and said filter (3) are maintained at a pressure of from 102 kPa to 5.0 MPA.

Inventors: FUJINAMI SHOSAKU, HIROSE TETSUHISA, IRIE MASAAKI, MIYOSHI NORIHISA, OSHITA TAKAHIRO, TAKANO KAZUO, FUJINAMI, SHOSAKU, HIROSE, TETSUHISA, IRIE, MASAAKI, MIYOSHI, NORIHISA, OSHITA, TAKAHIRO, TAKANO, KAZUO
Applicants: EBARA CORP, EBARA CORPORATION
Application year: 1996
Main classification: F23J15
IPC codes: F22B31, F23G5, F01K23, F22B1, F23J15