US20090050076A1 - Boiler producing steam from flue gases with high electrical efficiency and improved slag quality - Google Patents
Boiler producing steam from flue gases with high electrical efficiency and improved slag quality Download PDFInfo
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- US20090050076A1 US20090050076A1 US12/067,968 US6796806A US2009050076A1 US 20090050076 A1 US20090050076 A1 US 20090050076A1 US 6796806 A US6796806 A US 6796806A US 2009050076 A1 US2009050076 A1 US 2009050076A1
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- boiler
- steam
- boiler according
- corrosive gas
- reactor
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Links
- 239000003546 flue gas Substances 0.000 title claims abstract description 22
- 239000002893 slag Substances 0.000 title claims description 21
- 239000007789 gas Substances 0.000 claims abstract description 66
- 239000000446 fuel Substances 0.000 claims abstract description 16
- 238000010304 firing Methods 0.000 claims abstract description 14
- 238000005245 sintering Methods 0.000 claims abstract description 4
- 238000001035 drying Methods 0.000 claims abstract description 3
- 239000002699 waste material Substances 0.000 claims description 11
- 229910001385 heavy metal Inorganic materials 0.000 claims description 9
- 229910052725 zinc Inorganic materials 0.000 claims description 9
- 229910052745 lead Inorganic materials 0.000 claims description 7
- 239000012633 leachable Substances 0.000 claims description 6
- 230000005855 radiation Effects 0.000 claims description 6
- 229910021654 trace metal Inorganic materials 0.000 claims description 6
- 229910052801 chlorine Inorganic materials 0.000 claims description 4
- 239000003245 coal Substances 0.000 claims description 4
- 229910052700 potassium Inorganic materials 0.000 claims description 4
- 238000000926 separation method Methods 0.000 claims description 4
- 229910052708 sodium Inorganic materials 0.000 claims description 4
- 239000002028 Biomass Substances 0.000 claims description 3
- 239000003570 air Substances 0.000 claims description 3
- 229910052785 arsenic Inorganic materials 0.000 claims description 3
- 229910052793 cadmium Inorganic materials 0.000 claims description 3
- 229910052802 copper Inorganic materials 0.000 claims description 3
- 230000005611 electricity Effects 0.000 claims description 3
- 229910052759 nickel Inorganic materials 0.000 claims description 3
- 239000003921 oil Substances 0.000 claims description 3
- 238000007664 blowing Methods 0.000 claims description 2
- 238000001704 evaporation Methods 0.000 claims description 2
- 230000008020 evaporation Effects 0.000 claims description 2
- 239000002956 ash Substances 0.000 description 14
- 239000010882 bottom ash Substances 0.000 description 10
- 238000000034 method Methods 0.000 description 10
- 238000002485 combustion reaction Methods 0.000 description 9
- 239000000463 material Substances 0.000 description 7
- 239000007787 solid Substances 0.000 description 7
- UGFAIRIUMAVXCW-UHFFFAOYSA-N Carbon monoxide Chemical compound [O+]#[C-] UGFAIRIUMAVXCW-UHFFFAOYSA-N 0.000 description 4
- 239000010808 liquid waste Substances 0.000 description 4
- 239000000203 mixture Substances 0.000 description 4
- 230000007797 corrosion Effects 0.000 description 3
- 238000005260 corrosion Methods 0.000 description 3
- 230000007613 environmental effect Effects 0.000 description 3
- 238000002386 leaching Methods 0.000 description 3
- 239000007788 liquid Substances 0.000 description 3
- 238000002156 mixing Methods 0.000 description 3
- 230000009972 noncorrosive effect Effects 0.000 description 3
- 239000002245 particle Substances 0.000 description 3
- 239000002910 solid waste Substances 0.000 description 3
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 3
- 238000010276 construction Methods 0.000 description 2
- 239000010881 fly ash Substances 0.000 description 2
- 239000002440 industrial waste Substances 0.000 description 2
- 238000002347 injection Methods 0.000 description 2
- 239000007924 injection Substances 0.000 description 2
- 239000003039 volatile agent Substances 0.000 description 2
- 238000004056 waste incineration Methods 0.000 description 2
- 235000002918 Fraxinus excelsior Nutrition 0.000 description 1
- 239000000956 alloy Substances 0.000 description 1
- 229910045601 alloy Inorganic materials 0.000 description 1
- 239000011449 brick Substances 0.000 description 1
- 230000005587 bubbling Effects 0.000 description 1
- 238000004140 cleaning Methods 0.000 description 1
- 239000002826 coolant Substances 0.000 description 1
- 238000001816 cooling Methods 0.000 description 1
- 230000003247 decreasing effect Effects 0.000 description 1
- 239000012530 fluid Substances 0.000 description 1
- 238000010438 heat treatment Methods 0.000 description 1
- 206010022000 influenza Diseases 0.000 description 1
- 239000010813 municipal solid waste Substances 0.000 description 1
- 239000011819 refractory material Substances 0.000 description 1
- 230000002787 reinforcement Effects 0.000 description 1
- 230000000630 rising effect Effects 0.000 description 1
- 150000003839 salts Chemical class 0.000 description 1
- 229920006395 saturated elastomer Polymers 0.000 description 1
- 238000012216 screening Methods 0.000 description 1
- 239000000725 suspension Substances 0.000 description 1
- 238000003466 welding Methods 0.000 description 1
Images
Classifications
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- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23G—CREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
- F23G5/00—Incineration of waste; Incinerator constructions; Details, accessories or control therefor
- F23G5/44—Details; Accessories
- F23G5/46—Recuperation of heat
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F22—STEAM GENERATION
- F22B—METHODS OF STEAM GENERATION; STEAM BOILERS
- F22B31/00—Modifications of boiler construction, or of tube systems, dependent on installation of combustion apparatus; Arrangements or dispositions of combustion apparatus
- F22B31/04—Heat supply by installation of two or more combustion apparatus, e.g. of separate combustion apparatus for the boiler and the superheater respectively
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23G—CREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
- F23G5/00—Incineration of waste; Incinerator constructions; Details, accessories or control therefor
- F23G5/08—Incineration of waste; Incinerator constructions; Details, accessories or control therefor having supplementary heating
- F23G5/14—Incineration of waste; Incinerator constructions; Details, accessories or control therefor having supplementary heating including secondary combustion
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23G—CREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
- F23G5/00—Incineration of waste; Incinerator constructions; Details, accessories or control therefor
- F23G5/44—Details; Accessories
- F23G5/48—Preventing corrosion
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23G—CREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
- F23G2202/00—Combustion
- F23G2202/10—Combustion in two or more stages
- F23G2202/103—Combustion in two or more stages in separate chambers
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23G—CREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
- F23G2202/00—Combustion
- F23G2202/10—Combustion in two or more stages
- F23G2202/104—Combustion in two or more stages with ash melting stage
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23G—CREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
- F23G2202/00—Combustion
- F23G2202/10—Combustion in two or more stages
- F23G2202/105—Combustion in two or more stages with waste supply in stages
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23G—CREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
- F23G2206/00—Waste heat recuperation
- F23G2206/20—Waste heat recuperation using the heat in association with another installation
- F23G2206/203—Waste heat recuperation using the heat in association with another installation with a power/heat generating installation
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02E—REDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
- Y02E20/00—Combustion technologies with mitigation potential
- Y02E20/12—Heat utilisation in combustion or incineration of waste
Definitions
- the invention relates to a boiler drying, igniting and combusting refuse and producing steam by heat exchange with flue gases. Subsequently, the steam is utilised to produce electricity.
- the refuse to be burnt can be any mixture of household refuse, bark, industrial waste and hospital refuse and other kinds of waste.
- U.S. Pat. No. 6,269,754 discloses a steam generator for superheated steam for incineration plants with corrosive flue gases. It essentially comprises a radiation section and a convection section, having at least one superheater and having plates arranged on the inside of a wall of the radiation section, a space is being provided between the plates and the wall of the radiation section. At least a part of the superheater is being arranged as a wall superheater in the space in the radiation section.
- This space contains a less-corrosive gaseous atmosphere, which is at a higher pressure than the pressure of the gases in the combustion chamber.
- U.S. Pat. No. 6,269,754 does not provide direct contact between the flues gases and the mentioned superheaters, and accordingly there is a less efficient transfer of energy from the flue gases to the steam.
- EP 0536268 B1 discloses a method and apparatus for incinerating different kinds of solid and possibly liquid waste material.
- Solid and possibly liquid waste material is incinerated by a) partial combustion on the stepped grates of the solid waste material, the latter being delivered to a rotary kiln at such a high temperature that a liquid slag is formed at the inlet of the rotary kiln, b) possibly adding liquid waste material to the solid waste material being incinerated on the stepped grates, and c) collecting the ash products from the combustion process, such as grate screenings, boiler ash, fly ash, and residual products from flue-gas cleaning, and returning these products to the input end of the rotary kiln, at which input end these products are introduced into the liquid slag.
- the slag, fly ash and other harmful residual products from the combustion process are fused into a glass-like mass, from which salts and heavy metals cannot be leached out.
- EP 0536268 B1 does not provide for an optimised, electrical efficient output from the incineration of the solid and liquid waste material.
- the boiler comprises a reactor, positioned downstream of the moving bed furnace and possibly co-fired with firing a secondary fuel, for generating a less-corrosive gas flow and an end superheater located in the flow of said less-corrosive gas.
- the boiler dries, ignites and combusts refuse and produces steam by heat exchange with flue gases.
- the invention has the advantages that the lifetime of the end superheater of the boiler is increased and that the boiler also provides a high and efficient electrical power output due to the increased steam temperature in the end superheater.
- end superheater can be applied at a higher temperature when subjected to cleaner gases, i.e. less-corrosive gas and ash particles.
- FIG. 1 shows an embodiment of the boiler using a reactor in combination with a burner applied to generate a non-corrosive gas
- FIG. 2 shows an embodiment of the boiler using a reactor in combination with a burner applied to generate a non-corrosive gas with a separator element.
- the terms “superheater” or “end superheater” refers to a device that heats the steam generated by the boiler further, thereby increasing the thermal energy in the steam and decreasing the likelihood that said steam condenses.
- Steam, which has been superheated is logically known as superheated steam; conversely non-superheated steam is called saturated steam or wet steam. It is important to avoid the latter steam and thus primarily to use the superheated steam.
- this latter steam is fed into a steam turbine driving a generator, it will provide a high and efficient electrical power output, especially if the temperature and the pressure of the steam are sufficiently high.
- Bottom ash In general bottom ash is called slag.
- Bottom ash or slag is defined as the ash removed from the bottom part of the combustion zone of the boiler. Ashes are defined as the residual products from the combustion process.
- FIG. 1 shows an embodiment of the boiler using a reactor in combination with a burner applied to generate a less-corrosive gas.
- the boiler ( 1 ) dries, ignites and combusts refuse.
- a gaseous atmosphere, i.e. flue gases ( 3 ) is in the first place the result of incineration of refuse ( 9 ).
- the reactor ( 16 ) can be a sintering reactor, a rotary kiln, a fluidised bed or a spouted bed.
- the reactor sinters the bottom ash such that the leaching of heavy metals is reduced and the possibilities of utilising the bottom ash are improved.
- the sintering reactor is a reactor that heats the ash/slag so that leaching properties are improved. This means that the leaching of heavy metals from the ash/slag is reduced.
- Said reactor ( 16 ) in general burns the refuse and turns it into slag and/or ash.
- the refuse to be burnt can be any mixtures of household refuse, bark, industrial waste and hospital refuse and other kinds of waste.
- the refuse is supplied to the reactor—from the left to the right in the figure—by means of grate blocks, e.g. reciprocable grates ( 21 ).
- the grates can be combined with one or more conveyors.
- the reactor is located—in the direction of the flow of the refuse—after the grate arrangement ( 21 ).
- the reactor is fired from the left-hand side with a secondary fuel ( 18 ).
- the firing follows the direction of the transport of refuse in the reactor, and as a result the less-corrosive gas flow as the output from said reactor is co-current, as indicated with the arrow 6 .
- the firing of the reactor can take place by means of a burner ( 19 ), which can be fired with said secondary fuel ( 18 ), i.e. the burner can be fired with any combination of oil, gas, coal, biomass, air and a selected waste or refuse fraction.
- a burner 19
- Said firing may take place by means of a burner ( 19 ) and/or take place in the reactor.
- the burner can be a suspension burner, possibly supplied with coal or a gas, or an oil burner, etc.
- the fuel and air injection into the reactor inlet comes via a separate housing/chute, which is separated from the corrosive flue gas ( 7 ).
- the reactor Since the reactor is fired, it reaches a higher temperature as compared to a reactor with no firing. This heat is needed to burn out the volatiles and to sinter the waste slag, trace and heavy metal species. This can be considered as a post-treatment process, i.e. the boiler or waste incinerator is combined with the reactor. As a result, the final ash and/or slag from the reactor is—due to its low content of leachable trace and heavy metal species, such as one or more of leachable Pb, As, Cd, Cu, Zn, Ni and Zn well-suited for reuse in road construction, etc and/or for disposal. Accordingly, environmental harm from ash and slag are minimised.
- leachable trace and heavy metal species such as one or more of leachable Pb, As, Cd, Cu, Zn, Ni and Zn well-suited for reuse in road construction, etc and/or for disposal. Accordingly, environmental harm from ash and slag are minimised.
- the ash and/or slag is provided from the reactor by means of a bottom ash or slag removal device, which e.g. is a water filled through a piston pusher or belt conveyor.
- an integrated bottom ash treatment and improved electrical plant efficiency may be obtained by the concepts shown in the figure. It is thus advantageous to combine the high-efficient grate firing of e.g. refuse, such as municipal solid waste, with a post-treatment of the bottom ash (by means of the reactor) in a single plant, so that the final bottom-ash and/or slag produced will fulfil the current environmental and technical restrictions necessary for reuse, and at the same time this integrated post-treatment provides a less-corrosive flue gas ( 6 ), which can be applied to increase the end superheater ( 8 ) steam temperature and thereby the electrical efficiency of the waste-fired boiler of the plant.
- the total process is integrated, energy-efficient and contained within a single plant without the need for transporting, storing, and subsequent handling/treatment of the bottom ash and/or slag from the grate in another plant.
- the electrical efficiency of the waste incineration plant is improved significantly due to the generation of the less-corrosive flue gas ( 6 ), which will allow higher steam temperatures (around 500 degrees Celsius) at the outlet 8 b of the end superheater ( 8 ). Furthermore, it makes it possible to dispose of massive amounts of bottom ash and slag from waste incineration due to fixation of otherwise leachable trace and heavy metal fractions.
- Said less-corrosive gas is essentially free from corrosive components, such as Cl, K, Na, Zn, Pb, whereas the corrosive gas comprises corrosive components, e.g. comprises one or more of Cl, K, Na, Zn and Pb.
- less-corrosive gas can be understood as gases that provide less corrosion on the end superheater.
- FIG. 2 shows an embodiment of the boiler using a reactor in combination with a burner ( 19 ) applied to generate a less-corrosive gas with a separator element.
- the reactor is fired from the right-hand side with a secondary fuel ( 18 ).
- the firing does not follow the direction of the transport of refuse in the reactor, and as a result the less-corrosive gas flow as the output from said reactor is counter current, as indicated with the arrow 6 .
- the reactor is located at the end of the transportation direction of the refuse, which is discharged directly from the grate into the reactor.
- the firing of the reactor can take place by means of a burner ( 19 ), which can be fired with said secondary fuel ( 18 ), i.e. the burner can be fired with any combination of oil, gas, coal, biomass, air and a selected waste or refuse fraction.
- a burner 19
- said secondary fuel 18
- the burner can be fired with any combination of oil, gas, coal, biomass, air and a selected waste or refuse fraction.
- the reactor Since the reactor is fired, it reaches a higher temperature as compared to a reactor with no firing. This heat is needed to burn out the volatiles and to sinter the waste slag, trace and heavy metal species.
- This can be considered as a post-treatment process, i.e. the boiler or waste incinerator is combined with the reactor.
- the final ash and/or slag from the reactor is—due to its low content of leachable trace and heavy metal species, such as one or more of Pb, As, Cd, Cu, Zn, Ni and Zn—well-suited for reuse in road construction, etc and/or for disposal. Accordingly, environmental harm from ash and slag is minimised.
- a separation is provided to maintain separation of the gases, i.e. in order to protect the end superheater ( 8 ) from the corrosive gases ( 7 ), whereby it is mainly subjected to the non-corrosive gases ( 6 ).
- Said separation of the flue gases ( 3 ) is maintained by means of a separator element denoted with reference numeral 4 .
- This element could in an exemplary embodiment be provided as a plate ( 4 a ) or in the form of a wall ( 4 b ).
- the plate ( 4 a ) is typically a water filled boiler tube panel extending from one boiler side wall, typically also a water filled boiler tube panel, to the other boiler side wall, and the plate is suspended on said side walls.
- the plate may be corrosion-protected on the surfaces by e.g. high-alloy Cr—Ni overlay welding or by essentially tight refractory materials.
- the wall ( 4 b ) is typically a reinforced brick or cast refractory wall extending from the one boiler sidewall to the other boiler sidewall.
- the reinforcement may be hollow, allowing for passage of a cooling medium being e.g. a liquid, a vapour, a gas or air.
- the separator element could in another exemplary embodiment be provided as a channel, i.e. said plate ( 4 a ) and wall ( 4 b ) could in various combinations be used to form the channel.
- the channel could also have a tubular shape.
- the separator element secures that the less-corrosive gas flow ( 6 ) and the corrosive gas flow ( 7 ) are kept separated at this point, and that mainly the less-corrosive gas flow ( 6 ) from the reactor ( 16 ) reaches the end superheater ( 8 ).
- the optimal position of the separator element may be reflected in a high efficiency and high electrical power output from a generator driven by a steam turbine supplied with steam from the boiler.
- the separator element is adapted to be suspendable on or from the walls of the boiler.
- the separator element may be a plate, a wall or channel able to pivot at the top in bearings suspended on the opposite boiler side walls and e.g. being able to move and fixate in different positions forwards/backwards at the bottom onto the boiler side walls.
- the steam ( 2 ) at between 300 and 450 degrees Celsius, after leaving said one or more superheaters, is fed, by means of one or more pipes, to an inlet ( 8 a ) of an end superheater ( 8 ), through which this steam ( 2 ) is heated, resulting in a temperature increase of between 25 and 200 degrees Celsius.
- this steam ( 2 a ) can be utilised to produce electricity.
- said steam can be fed by means of piping from said outlet into the steam turbine ( 14 ), which drives a generator ( 15 ), from which generator electrical power then can be generated.
- warmer steam ( 2 a ) is the output from the boiler, i.e. the output from the end superheater, the boiler accordingly also provides high power output efficiency. This is, of course, higher than if steam ( 2 ) at between 300 and 450 Celsius was the output from the boiler.
- the heating of the steam in said end superheater provides the high electrical power and high efficiency output.
- said end superheater ( 8 ) is located in proximity to said separator element ( 4 ), e.g. said plate, wall or into the channel, and in all cases in the flow ( 6 ) of said less-corrosive gas. It is thus an advantage that the end superheater is less subject to corrosion.
- the invention therefore has the advantages that the lifetime of the end superheater is increased and that the boiler provides a high electrical power efficiency.
- the boiler further comprises a blow unit ( 12 ).
- This is adapted to—by blowing secondary air—effectively mix said less-corrosive gas ( 6 ) with said corrosive gas ( 7 ), whereby said mix can be effectively burnt out before it reaches the top zone ( 13 ) of the boiler.
- the boiler is provided with an Industrial Draught fan, which sucks the gases, i.e. flue gases, the less-corrosive and the corrosive gases through the boiler. Additionally, combustion air can be blown in under the grate arrangement ( 21 ).
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- Engineering & Computer Science (AREA)
- Mechanical Engineering (AREA)
- General Engineering & Computer Science (AREA)
- Chemical & Material Sciences (AREA)
- Combustion & Propulsion (AREA)
- Physics & Mathematics (AREA)
- Thermal Sciences (AREA)
- Waste-Gas Treatment And Other Accessory Devices For Furnaces (AREA)
- Gasification And Melting Of Waste (AREA)
- Engine Equipment That Uses Special Cycles (AREA)
Abstract
This invention relates to a boiler (1) drying, igniting and combusting refuse and producing steam (2, 2 a) by heat exchange with flue gases (3). Said boiler (1) comprises a reactor (16) with firing a secondary fuel (18) for generating a less-corrosive gas flow (6) and an end superheater (8) located in the flow (6) of said less-corrosive gas. Said reactor (16) could be a sintering reactor, a rotary kiln, a fluidised bed or a spouted bed. This provides for an increased lifetime of the end superheater and makes the boiler provide a high and efficient electrical power output.
Description
- The invention relates to a boiler drying, igniting and combusting refuse and producing steam by heat exchange with flue gases. Subsequently, the steam is utilised to produce electricity.
- The refuse to be burnt can be any mixture of household refuse, bark, industrial waste and hospital refuse and other kinds of waste.
- U.S. Pat. No. 6,269,754 discloses a steam generator for superheated steam for incineration plants with corrosive flue gases. It essentially comprises a radiation section and a convection section, having at least one superheater and having plates arranged on the inside of a wall of the radiation section, a space is being provided between the plates and the wall of the radiation section. At least a part of the superheater is being arranged as a wall superheater in the space in the radiation section. This space contains a less-corrosive gaseous atmosphere, which is at a higher pressure than the pressure of the gases in the combustion chamber. Hereby, it is possible to reach a high superheater temperature without corrosion to the final superheater, so that the superheater can be made from inexpensive material.
- However, U.S. Pat. No. 6,269,754 does not provide direct contact between the flues gases and the mentioned superheaters, and accordingly there is a less efficient transfer of energy from the flue gases to the steam.
- EP 0536268 B1—from the applicant—discloses a method and apparatus for incinerating different kinds of solid and possibly liquid waste material. Solid and possibly liquid waste material is incinerated by a) partial combustion on the stepped grates of the solid waste material, the latter being delivered to a rotary kiln at such a high temperature that a liquid slag is formed at the inlet of the rotary kiln, b) possibly adding liquid waste material to the solid waste material being incinerated on the stepped grates, and c) collecting the ash products from the combustion process, such as grate screenings, boiler ash, fly ash, and residual products from flue-gas cleaning, and returning these products to the input end of the rotary kiln, at which input end these products are introduced into the liquid slag. In this manner, it is achieved that the slag, fly ash and other harmful residual products from the combustion process are fused into a glass-like mass, from which salts and heavy metals cannot be leached out.
- However, EP 0536268 B1 does not provide for an optimised, electrical efficient output from the incineration of the solid and liquid waste material.
- In a world where natural energy resources, e.g. oil, is increasingly scarce, there is an increasing demand for energy supplied from other sources. When refuse is incinerated in a boiler, energy can be extracted from the incineration process. Thus it is important that the incineration process is optimised to provide steam that is not condensed and has a sufficient high temperature to ensure that the steam, when fed in a steam turbine driving a generator, provides a high electrical power output with high efficiency. Such steam can e.g. be superheated steam.
- Thus there is a need for a boiler optimised to provide a high electrical power output from superheated steam and an end superheater with a higher temperature on the wall.
- Typically, superheated steam comes from a so-called end superheater. However, in a boiler some of the gases, e.g. flue gases and the ash particles, are corrosive, which, due to their corrosive nature, will attack said end superheater with the result that the lifetime of the end superheater is shortened.
- Thus, there is also a need for a boiler having an end superheater, where some means are provided to extend the lifetime of the end superheater.
- These needs are fulfilled when the boiler comprises a reactor, positioned downstream of the moving bed furnace and possibly co-fired with firing a secondary fuel, for generating a less-corrosive gas flow and an end superheater located in the flow of said less-corrosive gas. The boiler dries, ignites and combusts refuse and produces steam by heat exchange with flue gases.
- Hereby, the invention has the advantages that the lifetime of the end superheater of the boiler is increased and that the boiler also provides a high and efficient electrical power output due to the increased steam temperature in the end superheater.
- Furthermore the end superheater can be applied at a higher temperature when subjected to cleaner gases, i.e. less-corrosive gas and ash particles.
- The invention will be explained more fully below in connection with preferred embodiments and with reference to the drawings, in which:
-
FIG. 1 shows an embodiment of the boiler using a reactor in combination with a burner applied to generate a non-corrosive gas, and -
FIG. 2 shows an embodiment of the boiler using a reactor in combination with a burner applied to generate a non-corrosive gas with a separator element. - Throughout the drawings, the same reference numerals indicate similar or corresponding features or functions.
- In general the terms “superheater” or “end superheater” refers to a device that heats the steam generated by the boiler further, thereby increasing the thermal energy in the steam and decreasing the likelihood that said steam condenses. Steam, which has been superheated, is logically known as superheated steam; conversely non-superheated steam is called saturated steam or wet steam. It is important to avoid the latter steam and thus primarily to use the superheated steam. Thus, when this latter steam is fed into a steam turbine driving a generator, it will provide a high and efficient electrical power output, especially if the temperature and the pressure of the steam are sufficiently high.
- In general bottom ash is called slag. Bottom ash or slag is defined as the ash removed from the bottom part of the combustion zone of the boiler. Ashes are defined as the residual products from the combustion process.
-
FIG. 1 shows an embodiment of the boiler using a reactor in combination with a burner applied to generate a less-corrosive gas. In general, the boiler (1) dries, ignites and combusts refuse. When refuse is incinerated, a gaseous atmosphere, i.e. flue gases (3), is in the first place the result of incineration of refuse (9). - The reactor (16) can be a sintering reactor, a rotary kiln, a fluidised bed or a spouted bed. The reactor sinters the bottom ash such that the leaching of heavy metals is reduced and the possibilities of utilising the bottom ash are improved.
- The sintering reactor is a reactor that heats the ash/slag so that leaching properties are improved. This means that the leaching of heavy metals from the ash/slag is reduced.
- In fluid beds and fast fluidised beds, smooth and steady recirculation of solids through a dipleg or other solid trapping device is crucial to good operations. In the spouted bed it represents a somewhat related contacting mode in which comparatively coarse, uniformly sized solids are contacted by gas. In this operation, a high velocity spout of gas punches through the bed of solids, thereby transporting particles to the top of the bed. The rest of the solids move downward slowly around the spout and through gently upward percolating gas. Behaviour somewhere between bubbling and spouting is also seen, and this may be called spouted fluidised bed behaviour.
- Said reactor (16) in general burns the refuse and turns it into slag and/or ash. The refuse to be burnt can be any mixtures of household refuse, bark, industrial waste and hospital refuse and other kinds of waste. Typically the refuse is supplied to the reactor—from the left to the right in the figure—by means of grate blocks, e.g. reciprocable grates (21). In order to convey the refuse, the grates can be combined with one or more conveyors.
- The reactor is located—in the direction of the flow of the refuse—after the grate arrangement (21).
- The process of refuse-incineration is now to be followed—from left to right in the figure—starting at reference numeral 3 with flue gases, proceeding to
reference numeral 7, and ending at reference numeral 6. Atreference numeral 7, a corrosive gas flow is the result in the pre-process, and conversely at reference numeral 6, a less-corrosive gas flow is the result in the post-process. The less-corrosive gas flow is the output from said reactor (16), possibly fired with a fuel (18), typically a secondary fuel (18). The secondary fuel is selected to develop flue gases that are less corrosive than the flue gases from said refuse or waste. - In this embodiment the reactor is fired from the left-hand side with a secondary fuel (18). The firing follows the direction of the transport of refuse in the reactor, and as a result the less-corrosive gas flow as the output from said reactor is co-current, as indicated with the arrow 6.
- Alternatively, or additionally, the firing of the reactor can take place by means of a burner (19), which can be fired with said secondary fuel (18), i.e. the burner can be fired with any combination of oil, gas, coal, biomass, air and a selected waste or refuse fraction. This also applies when said secondary fuel in addition, or as an alternative, is supplied directly to the reactor instead. Said firing may take place by means of a burner (19) and/or take place in the reactor.
- The burner can be a suspension burner, possibly supplied with coal or a gas, or an oil burner, etc.
- The fuel and air injection into the reactor inlet comes via a separate housing/chute, which is separated from the corrosive flue gas (7).
- Since the reactor is fired, it reaches a higher temperature as compared to a reactor with no firing. This heat is needed to burn out the volatiles and to sinter the waste slag, trace and heavy metal species. This can be considered as a post-treatment process, i.e. the boiler or waste incinerator is combined with the reactor. As a result, the final ash and/or slag from the reactor is—due to its low content of leachable trace and heavy metal species, such as one or more of leachable Pb, As, Cd, Cu, Zn, Ni and Zn well-suited for reuse in road construction, etc and/or for disposal. Accordingly, environmental harm from ash and slag are minimised.
- The ash and/or slag is provided from the reactor by means of a bottom ash or slag removal device, which e.g. is a water filled through a piston pusher or belt conveyor.
- Thus an integrated bottom ash treatment and improved electrical plant efficiency may be obtained by the concepts shown in the figure. It is thus advantageous to combine the high-efficient grate firing of e.g. refuse, such as municipal solid waste, with a post-treatment of the bottom ash (by means of the reactor) in a single plant, so that the final bottom-ash and/or slag produced will fulfil the current environmental and technical restrictions necessary for reuse, and at the same time this integrated post-treatment provides a less-corrosive flue gas (6), which can be applied to increase the end superheater (8) steam temperature and thereby the electrical efficiency of the waste-fired boiler of the plant. The total process is integrated, energy-efficient and contained within a single plant without the need for transporting, storing, and subsequent handling/treatment of the bottom ash and/or slag from the grate in another plant.
- The electrical efficiency of the waste incineration plant is improved significantly due to the generation of the less-corrosive flue gas (6), which will allow higher steam temperatures (around 500 degrees Celsius) at the
outlet 8 b of the end superheater (8). Furthermore, it makes it possible to dispose of massive amounts of bottom ash and slag from waste incineration due to fixation of otherwise leachable trace and heavy metal fractions. - Said less-corrosive gas is essentially free from corrosive components, such as Cl, K, Na, Zn, Pb, whereas the corrosive gas comprises corrosive components, e.g. comprises one or more of Cl, K, Na, Zn and Pb. In essence, less-corrosive gas can be understood as gases that provide less corrosion on the end superheater.
-
FIG. 2 shows an embodiment of the boiler using a reactor in combination with a burner (19) applied to generate a less-corrosive gas with a separator element. - In this embodiment the reactor is fired from the right-hand side with a secondary fuel (18). The firing does not follow the direction of the transport of refuse in the reactor, and as a result the less-corrosive gas flow as the output from said reactor is counter current, as indicated with the arrow 6. Note that the reactor is located at the end of the transportation direction of the refuse, which is discharged directly from the grate into the reactor.
- Alternatively, or additionally, the firing of the reactor can take place by means of a burner (19), which can be fired with said secondary fuel (18), i.e. the burner can be fired with any combination of oil, gas, coal, biomass, air and a selected waste or refuse fraction. This also applies when said secondary fuel in addition, or as an alternative, is supplied directly to the reactor instead.
- Since the reactor is fired, it reaches a higher temperature as compared to a reactor with no firing. This heat is needed to burn out the volatiles and to sinter the waste slag, trace and heavy metal species. This can be considered as a post-treatment process, i.e. the boiler or waste incinerator is combined with the reactor. As a result, the final ash and/or slag from the reactor is—due to its low content of leachable trace and heavy metal species, such as one or more of Pb, As, Cd, Cu, Zn, Ni and Zn—well-suited for reuse in road construction, etc and/or for disposal. Accordingly, environmental harm from ash and slag is minimised.
- At this point of the process, it is important that corrosive and less-corrosive gases are not mixed, since these, i.e.
reference numerals 6 and 7, are to be treated differently. - This is because the less-corrosive gas (6) shall be kept separated from the corrosive gas (7) rising from the grate combustion.
- Consequently, according to the invention, a separation is provided to maintain separation of the gases, i.e. in order to protect the end superheater (8) from the corrosive gases (7), whereby it is mainly subjected to the non-corrosive gases (6). Said separation of the flue gases (3) is maintained by means of a separator element denoted with reference numeral 4. This element could in an exemplary embodiment be provided as a plate (4 a) or in the form of a wall (4 b).
- The plate (4 a) is typically a water filled boiler tube panel extending from one boiler side wall, typically also a water filled boiler tube panel, to the other boiler side wall, and the plate is suspended on said side walls. The plate may be corrosion-protected on the surfaces by e.g. high-alloy Cr—Ni overlay welding or by essentially tight refractory materials.
- The wall (4 b) is typically a reinforced brick or cast refractory wall extending from the one boiler sidewall to the other boiler sidewall. The reinforcement may be hollow, allowing for passage of a cooling medium being e.g. a liquid, a vapour, a gas or air.
- Moreover, the separator element could in another exemplary embodiment be provided as a channel, i.e. said plate (4 a) and wall (4 b) could in various combinations be used to form the channel. The channel could also have a tubular shape.
- Thus the separator element secures that the less-corrosive gas flow (6) and the corrosive gas flow (7) are kept separated at this point, and that mainly the less-corrosive gas flow (6) from the reactor (16) reaches the end superheater (8). In the long run, the optimal position of the separator element may be reflected in a high efficiency and high electrical power output from a generator driven by a steam turbine supplied with steam from the boiler.
- The separator element is adapted to be suspendable on or from the walls of the boiler. In an exemplary embodiment, the separator element may be a plate, a wall or channel able to pivot at the top in bearings suspended on the opposite boiler side walls and e.g. being able to move and fixate in different positions forwards/backwards at the bottom onto the boiler side walls.
- In general for any embodiment, i.e. it applies both when the firing takes place from the left-hand side (
FIG. 1 ) and from the right hand side (FIG. 2 ), said less-corrosive gas (6) and the corrosive gas (7) continue in the boiler to the mixing zone (10) of the boiler (1). - Also being general for any embodiment is that the steam (2) at between 300 and 450 degrees Celsius, after leaving said one or more superheaters, is fed, by means of one or more pipes, to an inlet (8 a) of an end superheater (8), through which this steam (2) is heated, resulting in a temperature increase of between 25 and 200 degrees Celsius.
- This warmer steam (2 a), i.e. the steam with the increased temperature, is e.g. supplied from an outlet (8 b) of the end superheater (8) to a steam turbine (14). Thus this steam (2 a) can be utilised to produce electricity. For example said steam can be fed by means of piping from said outlet into the steam turbine (14), which drives a generator (15), from which generator electrical power then can be generated. Since warmer steam (2 a) is the output from the boiler, i.e. the output from the end superheater, the boiler accordingly also provides high power output efficiency. This is, of course, higher than if steam (2) at between 300 and 450 Celsius was the output from the boiler. Thus the heating of the steam in said end superheater provides the high electrical power and high efficiency output.
- Typically said end superheater (8) is located in proximity to said separator element (4), e.g. said plate, wall or into the channel, and in all cases in the flow (6) of said less-corrosive gas. It is thus an advantage that the end superheater is less subject to corrosion.
- It is therefore an advantage—which applies to both figures—that the end superheater is located in the flow of said less-corrosive gas (6) as compared to the flow (7) of said corrosive gas. If the end superheater was located in the flow (7) of said corrosive gas—which is not the case according to the invention—such location of the end superheater would result in a short life time of the end superheater, and this location in the aggressive environment would require excessive and frequent repair work due to being subjected to corrosive gases during its working life time.
- The invention therefore has the advantages that the lifetime of the end superheater is increased and that the boiler provides a high electrical power efficiency.
- As discussed above, said less-corrosive gas (6) and the corrosive gas (7) are mixed together in the mixing zone (10) of the boiler (1). The boiler further comprises a blow unit (12). This is adapted to—by blowing secondary air—effectively mix said less-corrosive gas (6) with said corrosive gas (7), whereby said mix can be effectively burnt out before it reaches the top zone (13) of the boiler. Moreover—this applying to both figures—the boiler is provided with an Industrial Draught fan, which sucks the gases, i.e. flue gases, the less-corrosive and the corrosive gases through the boiler. Additionally, combustion air can be blown in under the grate arrangement (21).
- When said less-corrosive gas (6) and the corrosive gas (7) together reach the mixing zone (10) of the boiler, these gases are mixed by injection of secondary combustion air for outburning, and the now mixed gases are cooled by means of the evaporation wall in the radiation zone and one or more superheaters (11), which produce(s) steam (2) at between 300 and 450 Celsius. This (i.e. cooling by means of said one or more superheaters) takes place regardless of whether the less-corrosive gas (6) has been in contact with the plate, the wall or the channel when it moved in the direction (6) and/or whether it was the result of the firing with the burner to the reactor from the left-hand side or from the right-hand side.
Claims (17)
1. A boiler drying, igniting and combusting refuse and producing steam by heat exchange with flue gases, said boiler comprising a reactor with firing a secondary fuel for generating a less-corrosive gas flow and an end superheater located in the flow of said less-corrosive gas, the reactor is a sintering reactor, a rotary kiln, a fluidized bed or a spouted bed.
2. The boiler according to claim 1 , wherein said firing with the secondary fuel takes place by means of a burner and/or in the reactor itself.
3. The boiler according to claim 1 further comprising a separator element for maintaining separation of said flue gases into streams of said less-corrosive gas flow and a corrosive gas flow, respectively.
4. The boiler according to claim 3 , wherein said separator element comprises a plate or a wall.
5. The boiler according to claim 1 , wherein a number of said separator elements forms a channel.
6. The boiler according to claim 1 , wherein said separator element or channel is adapted to be suspendable on or from the walls of the boiler.
7. The boiler according to claim 1 , wherein said less-corrosive gas and corrosive gas are cooled by means of an evaporation wall in the radiation zone and one or more superheaters, which produce steam at between 300 and 450 Celsius.
8. The boiler according to claim 1 , wherein said steam is heated in the end superheater.
9. The boiler according to claim 1 , wherein said end superheater heats said steam to become steam of an increased temperature, resulting in a temperature increase of between 25 and 200 degrees Celsius as compared to the temperature of said steam.
10. The boiler according to claim 1 , wherein the less-corrosive gas is essentially free from Cl, K, Na, Zn, Pb.
11. The boiler according to claim 1 , wherein the corrosive gas comprises one or more of Cl, K, Na, Zn and Pb.
12. The boiler according to claim 1 , wherein said flue gases are the results of incineration of refuse.
13. The boiler according to claim 1 further comprising a blow unit adapted to, by blowing secondary air, effectively mix said less-corrosive gas with said corrosive gas, whereby said mix can be effectively burnt out before it reaches the top zone of the boiler.
14. The boiler according to claim 1 , wherein the steam is utilized to produce electricity when said steam is fed into a steam turbine driving a generator.
15. The boiler according to claim 1 , wherein the reactor produces final ash and/or slag with low content of leachable trace and heavy metal species, such as a low content of leachable Pb, As, Cd, Cu, Zn, Ni and Zn.
16. The boiler according to claim 1 , wherein the secondary fuel is any combination of oil, gas, coal, biomass, air and a selected waste or refuse fraction.
17. The boiler according to claim 1 , wherein the secondary fuel is selected to develop flue gases, which are less corrosive than the flue gases from said refuse or waste.
Applications Claiming Priority (3)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| DKPA200501373 | 2005-09-30 | ||
| DKPA200501373 | 2005-09-30 | ||
| PCT/IB2006/053563 WO2007036914A1 (en) | 2005-09-30 | 2006-09-29 | A boiler producing steam from flue gases with high electrical efficiency and improved slag quality |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| US20090050076A1 true US20090050076A1 (en) | 2009-02-26 |
Family
ID=37745895
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| US12/067,968 Abandoned US20090050076A1 (en) | 2005-09-30 | 2006-09-29 | Boiler producing steam from flue gases with high electrical efficiency and improved slag quality |
Country Status (8)
| Country | Link |
|---|---|
| US (1) | US20090050076A1 (en) |
| EP (1) | EP1934526A1 (en) |
| JP (1) | JP5053279B2 (en) |
| KR (1) | KR101029906B1 (en) |
| CN (1) | CN101287950B (en) |
| CA (1) | CA2624054C (en) |
| NO (1) | NO20081542L (en) |
| WO (1) | WO2007036914A1 (en) |
Cited By (5)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| US20080134540A1 (en) * | 2004-04-02 | 2008-06-12 | Skill Associates, Inc. | Biomass converters and processes |
| FR3012578A1 (en) * | 2013-10-24 | 2015-05-01 | Suez Environnement | METHOD AND INSTALLATION FOR ENERGY ENHANCING WASTE |
| WO2016147023A1 (en) * | 2015-03-13 | 2016-09-22 | Babcock & Wilcox Vølund A/S | Incineration plant with superheater |
| US20170198901A1 (en) * | 2016-01-12 | 2017-07-13 | Hitachi Zosen Inova Ag | Method and device for producing superheated steam by means of the heat produced in the boiler of an incineration plant |
| WO2020140337A1 (en) * | 2018-12-30 | 2020-07-09 | 上海康恒环境股份有限公司 | High-temperature high-pressure waste incinerator |
Families Citing this family (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| NL2007384C2 (en) | 2011-09-09 | 2013-03-12 | Ppm Engineering B V | SYSTEM AND METHOD FOR PACKING DOSED QUANTITIES OF SOLID MEDICINES |
| CN111534654A (en) * | 2020-05-26 | 2020-08-14 | 澄江磷化工金龙有限责任公司 | Steam recycling comprehensive utilization system of slag collecting tank |
Citations (14)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| US3208411A (en) * | 1961-06-24 | 1965-09-28 | Bernhard Urban | Garbage destruction plant |
| US3769921A (en) * | 1971-12-27 | 1973-11-06 | Mullen F Mc | Waste materials processing system |
| US3808989A (en) * | 1972-01-07 | 1974-05-07 | Koppers Wistra Ofenbau Gmbh | Method and arrangement for jointly combusting household refuse and sewage sludge |
| US4188892A (en) * | 1977-04-06 | 1980-02-19 | Von Roll Ag | Method and apparatus for removal of fly ash from a waste incinerator with liquid slag discharge |
| JPH06147442A (en) * | 1992-11-16 | 1994-05-27 | Chiyoda Corp | Refuse incinerating facility |
| US5385104A (en) * | 1990-07-03 | 1995-01-31 | Volund Ecology Systems A/S | Method and apparatus for incinerating different kinds of solid and possibly liquid waste material |
| US5707490A (en) * | 1991-11-26 | 1998-01-13 | Ahlstrom Machinery Oy | Method of recovering energy from waste liquors from pulp processes |
| US5749307A (en) * | 1995-07-10 | 1998-05-12 | Hitachi Zosen Corporation | Refuse incineration facility including material crusher and melt burner |
| US6036484A (en) * | 1997-10-13 | 2000-03-14 | Asea Brown Boveri Ag | Process for reprocessing slag and/or ash from the thermal treatment of refuse |
| US6269754B1 (en) * | 1998-08-20 | 2001-08-07 | Asea Brown Boveri Ag | Steam generator for superheated steam for incineration plants with corrosive flue gases |
| JP2002228131A (en) * | 2001-02-06 | 2002-08-14 | Nkk Corp | Waste incinerator |
| US20040007546A1 (en) * | 2002-07-09 | 2004-01-15 | Stinnett Harold K. | Article dispensing apparatus |
| US20050252458A1 (en) * | 2002-06-07 | 2005-11-17 | Andritz Oy | System for producing energy at a pulp mill |
| US20090145344A1 (en) * | 2005-09-30 | 2009-06-11 | Kim Dam-Johansen | Boiler producing steam from flue gases under optimized conditions |
Family Cites Families (12)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| DE1175378B (en) * | 1960-08-10 | 1964-08-06 | Licentia Gmbh | Steam boiler firing system with a main combustion chamber and a separately fired secondary combustion chamber |
| CH376604A (en) * | 1961-03-20 | 1964-04-15 | Von Roll Ag | Method for operating a waste incineration plant |
| JPS53118868A (en) * | 1976-02-10 | 1978-10-17 | Takuma Co Ltd | Refuse burning plant combining stoker type incinerator and melting gasification burning furnace |
| DK168245B1 (en) * | 1990-07-03 | 1994-02-28 | Lund Milj Teknik A S V | Process and plant for incineration of solid and possibly liquid waste of various kinds |
| CN1061428C (en) * | 1993-10-23 | 2001-01-31 | 郭聪贤 | Waste incineration and heat recovery equipment |
| AU2976995A (en) * | 1994-07-15 | 1996-02-16 | Aalborg Industries A/S | A fluid-bed heat exchanger, fluid-bed combustion reactor systems and methods for the operation of a fluid-bed heat exchanger and a fluid-bed combustion reactor system |
| JP3654932B2 (en) * | 1994-07-15 | 2005-06-02 | 川崎重工業株式会社 | Fluidized bed waste incineration method and apparatus |
| JPH08159429A (en) * | 1994-12-05 | 1996-06-21 | Chiyoda Corp | Fluidized bed refuse incinerator |
| JP3048968B2 (en) * | 1997-07-09 | 2000-06-05 | 川崎重工業株式会社 | Waste treatment method using waste plastic gasification and ash melting |
| CN1092088C (en) * | 1998-08-26 | 2002-10-09 | 苏进邦 | A waste treatment system |
| JP2002364824A (en) * | 2001-06-08 | 2002-12-18 | Kobe Steel Ltd | Stoker type incinerator and method of treating incinerated ash |
| JP2004163009A (en) * | 2002-11-13 | 2004-06-10 | Jfe Engineering Kk | Operating method of waste incineration system and waste incineration system |
-
2006
- 2006-09-29 US US12/067,968 patent/US20090050076A1/en not_active Abandoned
- 2006-09-29 EP EP06809447A patent/EP1934526A1/en not_active Withdrawn
- 2006-09-29 CA CA2624054A patent/CA2624054C/en not_active Expired - Fee Related
- 2006-09-29 WO PCT/IB2006/053563 patent/WO2007036914A1/en not_active Ceased
- 2006-09-29 KR KR1020087009450A patent/KR101029906B1/en not_active Expired - Fee Related
- 2006-09-29 CN CN2006800359997A patent/CN101287950B/en not_active Expired - Fee Related
- 2006-09-29 JP JP2008532967A patent/JP5053279B2/en not_active Expired - Fee Related
-
2008
- 2008-03-31 NO NO20081542A patent/NO20081542L/en not_active Application Discontinuation
Patent Citations (14)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| US3208411A (en) * | 1961-06-24 | 1965-09-28 | Bernhard Urban | Garbage destruction plant |
| US3769921A (en) * | 1971-12-27 | 1973-11-06 | Mullen F Mc | Waste materials processing system |
| US3808989A (en) * | 1972-01-07 | 1974-05-07 | Koppers Wistra Ofenbau Gmbh | Method and arrangement for jointly combusting household refuse and sewage sludge |
| US4188892A (en) * | 1977-04-06 | 1980-02-19 | Von Roll Ag | Method and apparatus for removal of fly ash from a waste incinerator with liquid slag discharge |
| US5385104A (en) * | 1990-07-03 | 1995-01-31 | Volund Ecology Systems A/S | Method and apparatus for incinerating different kinds of solid and possibly liquid waste material |
| US5707490A (en) * | 1991-11-26 | 1998-01-13 | Ahlstrom Machinery Oy | Method of recovering energy from waste liquors from pulp processes |
| JPH06147442A (en) * | 1992-11-16 | 1994-05-27 | Chiyoda Corp | Refuse incinerating facility |
| US5749307A (en) * | 1995-07-10 | 1998-05-12 | Hitachi Zosen Corporation | Refuse incineration facility including material crusher and melt burner |
| US6036484A (en) * | 1997-10-13 | 2000-03-14 | Asea Brown Boveri Ag | Process for reprocessing slag and/or ash from the thermal treatment of refuse |
| US6269754B1 (en) * | 1998-08-20 | 2001-08-07 | Asea Brown Boveri Ag | Steam generator for superheated steam for incineration plants with corrosive flue gases |
| JP2002228131A (en) * | 2001-02-06 | 2002-08-14 | Nkk Corp | Waste incinerator |
| US20050252458A1 (en) * | 2002-06-07 | 2005-11-17 | Andritz Oy | System for producing energy at a pulp mill |
| US20040007546A1 (en) * | 2002-07-09 | 2004-01-15 | Stinnett Harold K. | Article dispensing apparatus |
| US20090145344A1 (en) * | 2005-09-30 | 2009-06-11 | Kim Dam-Johansen | Boiler producing steam from flue gases under optimized conditions |
Non-Patent Citations (3)
| Title |
|---|
| 2002228131 - machine translation * |
| JP 2002228131 Machine translation * |
| Machine Translation - JP-06147442 * |
Cited By (8)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| US20080134540A1 (en) * | 2004-04-02 | 2008-06-12 | Skill Associates, Inc. | Biomass converters and processes |
| US7891114B2 (en) * | 2004-04-02 | 2011-02-22 | Skill Associates, Inc. | Biomass converters and processes |
| FR3012578A1 (en) * | 2013-10-24 | 2015-05-01 | Suez Environnement | METHOD AND INSTALLATION FOR ENERGY ENHANCING WASTE |
| WO2015059653A3 (en) * | 2013-10-24 | 2015-08-06 | Suez Environnement | Method and facility for recovering energy from waste |
| WO2016147023A1 (en) * | 2015-03-13 | 2016-09-22 | Babcock & Wilcox Vølund A/S | Incineration plant with superheater |
| US20170198901A1 (en) * | 2016-01-12 | 2017-07-13 | Hitachi Zosen Inova Ag | Method and device for producing superheated steam by means of the heat produced in the boiler of an incineration plant |
| US10260740B2 (en) * | 2016-01-12 | 2019-04-16 | Hitachi Zosen Inova Ag | Method and device for producing superheated steam by means of the heat produced in the boiler of an incineration plant |
| WO2020140337A1 (en) * | 2018-12-30 | 2020-07-09 | 上海康恒环境股份有限公司 | High-temperature high-pressure waste incinerator |
Also Published As
| Publication number | Publication date |
|---|---|
| EP1934526A1 (en) | 2008-06-25 |
| JP2009510384A (en) | 2009-03-12 |
| CN101287950A (en) | 2008-10-15 |
| CA2624054A1 (en) | 2007-04-05 |
| CA2624054C (en) | 2012-03-27 |
| NO20081542L (en) | 2008-06-25 |
| KR101029906B1 (en) | 2011-04-18 |
| KR20080094656A (en) | 2008-10-23 |
| CN101287950B (en) | 2012-09-26 |
| JP5053279B2 (en) | 2012-10-17 |
| WO2007036914A1 (en) | 2007-04-05 |
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