WO2007100120A1 - 可燃性ガスが揮発する物質の取扱方法、固体燃料の製造方法、固体燃料の貯留方法、固体燃料の使用方法、および固体燃料の使用装置 - Google Patents
可燃性ガスが揮発する物質の取扱方法、固体燃料の製造方法、固体燃料の貯留方法、固体燃料の使用方法、および固体燃料の使用装置 Download PDFInfo
- Publication number
- WO2007100120A1 WO2007100120A1 PCT/JP2007/054122 JP2007054122W WO2007100120A1 WO 2007100120 A1 WO2007100120 A1 WO 2007100120A1 JP 2007054122 W JP2007054122 W JP 2007054122W WO 2007100120 A1 WO2007100120 A1 WO 2007100120A1
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- WIPO (PCT)
- Prior art keywords
- solid fuel
- combustible gas
- handling
- substance
- air
- Prior art date
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Classifications
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- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23K—FEEDING FUEL TO COMBUSTION APPARATUS
- F23K5/00—Feeding or distributing other fuel to combustion apparatus
- F23K5/02—Liquid fuel
- F23K5/08—Preparation of fuel
- F23K5/10—Mixing with other fluids
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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
- F23G5/02—Incineration of waste; Incinerator constructions; Details, accessories or control therefor with pretreatment
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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
- F23G5/02—Incineration of waste; Incinerator constructions; Details, accessories or control therefor with pretreatment
- F23G5/027—Incineration of waste; Incinerator constructions; Details, accessories or control therefor with pretreatment pyrolising or gasifying stage
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- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23G—CREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
- F23G7/00—Incinerators or other apparatus for consuming industrial waste, e.g. chemicals
- F23G7/04—Incinerators or other apparatus for consuming industrial waste, e.g. chemicals of waste liquors, e.g. sulfite liquors
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- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23G—CREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
- F23G7/00—Incinerators or other apparatus for consuming industrial waste, e.g. chemicals
- F23G7/05—Incinerators or other apparatus for consuming industrial waste, e.g. chemicals of waste oils
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- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23G—CREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
- F23G7/00—Incinerators or other apparatus for consuming industrial waste, e.g. chemicals
- F23G7/10—Incinerators or other apparatus for consuming industrial waste, e.g. chemicals of field or garden waste or biomasses
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- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23C—METHODS OR APPARATUS FOR COMBUSTION USING FLUID FUEL OR SOLID FUEL SUSPENDED IN A CARRIER GAS OR AIR
- F23C2202/00—Fluegas recirculation
- F23C2202/30—Premixing fluegas with combustion air
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- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23G—CREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
- F23G2208/00—Safety aspects
- F23G2208/10—Preventing or abating fire or explosion, e.g. by purging
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- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23G—CREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
- F23G2900/00—Special features of, or arrangements for incinerators
- F23G2900/00001—Exhaust gas recirculation
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- 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
- Y02E50/00—Technologies for the production of fuel of non-fossil origin
- Y02E50/10—Biofuels, e.g. bio-diesel
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- 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
- Y02E50/00—Technologies for the production of fuel of non-fossil origin
- Y02E50/30—Fuel from waste, e.g. synthetic alcohol or diesel
Definitions
- the present invention relates to a method for handling a substance in which a combustible gas volatilizes, and particularly, a handling method for mixing and storing a substance in which a combustible gas volatilizes at low cost and safely, and using the handling method.
- the present invention relates to a method for producing solid fuel, a method for storing solid fuel, a method for using the solid fuel, and a device for using the solid fuel.
- Oil mud such as crude sludge has high energy. Therefore, the oil mud is expected to be effectively used as fuel without being incinerated or landfilled as industrial waste.
- oil mud includes those with high viscosity, those that do not flow at room temperature, and those that solid matter settles and settles. For this reason, the oil mud has poor handling properties during transportation through a pipeline and is difficult to handle as fuel.
- the mixer since the mixer has a high hermeticity, when oil mud and biomass are introduced into the mixer, at least air equivalent to these volumes is exhausted from the mixer. And since this mixer exhaust gas contains a lot of dust, it is sucked with a bag filter etc. so as not to leak out of the device. By this suction, fresh air (containing 21% oxygen) flows into the mixer, and the oxygen concentration is high in the mixer.
- the lower explosive limit oxygen concentration of many flammable gases is around 10%, so if the flammable gas volatilizes in the mixer, there is a risk of explosion or fire because oxygen is sufficient. .
- an inert gas such as nitrogen or carbon dioxide has been blown into the mixer to reduce the oxygen concentration (less than 8%), thereby preventing explosions or fires.
- an inert gas production facility such as nitrogen and carbon dioxide, or these inert gases, and this method was not cheap.
- this method there are 7 problems with post-treatment of exhaust gas containing inert gas and combustible gas.
- the present invention has been made in view of the above-described problems of the background art, and its purpose is to handle a material in which a flammable gas is volatilized at a low cost and in a safe manner, such as mixing and storing, and Production of solid fuel using the handling method It is to propose a manufacturing method, a solid fuel storage method, a method for using the solid fuel, and a device for using the solid fuel. Disclosure of the invention
- the present invention provides a method for handling a substance that emits a combustible gas having the following constitution, a method for producing a solid fuel using the method, a method for storing a solid fuel, The solid fuel usage method and solid fuel usage equipment were used.
- the high-sealing device is a mixing device, and the handling of the substance in which the combustible gas is volatilized is a mixing operation.
- the above-mentioned device having a high degree of sealing is a storage device, and the handling of the substance in which the flammable gas is volatilized is a storage operation, [1]
- a solid fuel characterized by storing solid fuel produced by mixing oil mud and biomass by the handling method described in [4] above. Storage method.
- Mixing device for mixing oil mud and biomass piping for introducing air that dilutes the flammable gas volatilized in the mixing device to a concentration that does not cause an explosion or fire, and mixing by the mixing device
- a method of diluting a combustible gas with air to a concentration that does not cause an explosion or fire is used without using an inert gas such as nitrogen or carbon dioxide that needs to be manufactured or purchased.
- an inert gas such as nitrogen or carbon dioxide that needs to be manufactured or purchased.
- the air used for diluting the combustible gas is used as combustion air
- the exhaust gas from the handling device such as the mixing device or the storage device can be treated safely and effectively.
- the calorific value of the combustible gas can be used effectively.
- FIG. 1 is a diagram conceptually showing a solid fuel production facility for realizing the present invention and a facility for using the solid fuel.
- Oil sludge includes oil sludge (for example, heavy oil sludge, crude oil sludge, etc.), waste oil regeneration residue (residue remaining after waste oil is regenerated using distillation equipment, etc.), waste paint, waste ink, waste solvent, grease, waste Examples include those containing one or more oily substances such as vegetable oil, waste edible oil, and dewatered organic sludge.
- oil sludge and waste oil regeneration residue are preferably used in the present invention.
- these oil muds are mainly composed of hydrocarbons with a high molecular weight, have high viscosity, are easily separated from solids, and are difficult to handle as fuel. Therefore, conventionally, these oil muds have been disposed of by incineration or landfilling, and therefore are preferably used in the present invention from the viewpoint of promoting the use of waste.
- biomass examples include crushed tatami (used waste tatami), wood chips (for example, crushed trash from construction waste), wood flour, and sawdust.
- Biomass is a general term for biologically derived organic resources (excluding fossil fuels) that can be used as fuel.
- the waste tatami used as the material of the crushed tatami mat may be any material that contains at least a part of plant material.
- main tatami mats using rice straw as a material for tatami floors but also polystyrene foam boards (plate-like molded bodies formed by adding a foaming agent to a polystyrene resin composition and expanding them) and Construction material tatami mats that use yo-board (for example, a soft fiberboard formed by crushing wood in water, making paper with adhesive, etc., and then drying it) ⁇ Sand can also be made with polystyrene foam board as a material for tatami flooring.
- the above-mentioned wood chip refers to crushed or crushed wood that has a maximum particle size (mesh size with a sieve residue within 5% by mass) of more than 5 mm and less than 10 mm.
- the above-mentioned wood flour refers to a pulverized product of wood having a maximum particle size (mesh size with a sieve residue within 5% by mass) of 5 mm or less.
- the sawdust usually has a particle size distribution of about 0.5 to 5 mm.
- the average particle size of the biomass is 0.5 mm or more. This is because if the average particle size is less than 0.5 mm, the entire particle system is miniaturized, so that fluidity and dispersibility are lowered, and it becomes difficult to obtain effects such as improved handling properties.
- the maximum particle size of the biomass is 10 mm or less, preferably 5 mm or less, more preferably 3 mm or less. This is because when the maximum particle size exceeds 1 O mm, when used with a cement kiln burner, it is difficult to form a flame and the combustion continues even after the fuel has landed. May reduce quality. If the maximum particle size is 5 mm or less, the proportion of particles that land and burn is reduced, and the proportion of solid fuel used can be increased, which is preferable. [Other materials]
- organic powder is used as an oil mud absorber. Can be.
- other materials can be added as long as the quality is not impaired.
- organic powders examples include toner, heavy oil ash, pulverized coal, activated carbon powder, meat and bone powder, waste plastic powder, paper powder, and organic distillation residue powder. These organic powders may be used alone or in combination of two or more.
- the toner is a dry developer used in office machines such as copiers, facsimile machines, and printers, and is a powder having a particle size of about 7 to 11 m.
- waste toner which is waste, is used.
- the toner has a very small particle size and a narrow particle size distribution. Therefore, the toner is preferably used because it can greatly contribute to an increase in the specific gravity of the solid fuel produced and an increase in the usable amount of oil mud.
- the heavy oil ash is a powder having a particle size of about 1 to 30 and a small particle size. Therefore, the heavy oil ash is also preferably used because it can contribute to an increase in the specific gravity of the produced solid fuel and an increase in the usable amount of oil mud.
- the pulverized coal is a powder having a particle size of about 10 to 100 m, and is known as a solid fuel in a firing furnace such as a cement kiln.
- the activated carbon powder and meat-and-bone powder those having an average particle size of 1 mm or less are usually used.
- waste pellets are used as the waste plastic powder.
- the paper dust for example, Thunder dust is used.
- Thunder dust is used as the organic distillation residue powder.
- the average particle size of the organic powder is 1/2 or less, preferably 1/3 or less with respect to the average particle size of the biomass. This is because when the ratio exceeds 1/2, the particle size difference between the biomass and the organic powder becomes small. It is difficult to obtain effects such as improvement of the groutability.
- activated carbon powder composed of fixed carbon, etc. if the average particle size exceeds 300 m, the number of landing and burning particles may increase and the quality of cement clinker may deteriorate. . Therefore, in the case of these organic powders, those having an average particle diameter of 30 Om or less, more preferably 100 wm or less are preferably used.
- the lower limit of the particle size of the organic powder is not particularly limited, but is usually 1 m or more.
- the blending ratio of each of the above materials is as follows. First, for the biomass and the organic powder as the absorbent material, the mass ratio of the biomass and the organic powder is 40/60 to 95/5, preferably 50/500 to 8 0/2 0. This is because if the mass ratio of biomass to organic powder is less than 40/60, the blending amount of biomass is small, so the organic powder fills the gaps between the granules of the biomass, and the fluidity of the fuel is significantly reduced. There are things to do. On the other hand, if the mass ratio of the biomass and the organic powder exceeds 95/5, the blending amount of the organic powder is small, so that it is not possible to sufficiently obtain an effect such as an increase in the specific gravity of the fuel.
- the amount of the oil mud is 30 to 300 parts by weight, preferably 50 to 200 parts by weight, more preferably 80 to 200 parts by weight with respect to 100 parts by weight of the total amount of the biomass and the organic powder. 1500 parts by mass, particularly preferably 100-1400 parts by mass. This means that if the amount of oil mud is less than 30 parts by mass, the purpose of using oil mud as fuel will not be met. On the other hand, if the blended amount of oil mud exceeds 300 parts by mass, oil may remain on the surface of the produced solid fuel particles, resulting in gloss and adhesion on the particle surface, and handling properties may be reduced.
- the above materials are introduced into the mixer at the above mixing ratio, and the method for handling substances in which the combustible gas is volatilized according to the present invention, that is, combustible that volatilizes from the mixture by introducing air into the mixer. Dilute the gas to a concentration that will not cause an explosion or fire.
- air is introduced into the mixer, and the concentration of the volatilized combustible gas is diluted to a concentration that does not cause an explosion or fire.
- the amount of specific air introduced into the mixer is appropriately determined depending on the type and amount of the combustible gas that volatilizes from the mixture, the capacity of the mixer, the amount of the mixture, and the like.
- the dilution gas used in the present invention is free air, and as will be described later, in the present invention, the air used for diluting the combustible gas is used in large quantities as combustion air for the firing furnace. Therefore, the necessary and sufficient amount of air should be introduced into the mixer.
- a mixer that is not simply provided with a stirring blade and that also rotates the mixing container itself. This makes it possible to mix well a highly viscous material such as oil mud and a low bulk density material such as biomass.
- the combustible gas volatilized by the rotation of the container flows and does not accumulate in a part of the container. Air can easily and reliably dilute combustible gases.
- An example of such a mixer that also rotates the container itself is an intensive mixer manufactured by Eirich.
- the mixer is preferably provided with a combustible gas detector that constantly detects the concentration of combustible gas. In the unlikely event that this combustible gas detector detects a combustible gas with a concentration above a certain level, the mixing operation is immediately stopped and the amount of air introduced into the mixer is increased, or in some cases. It is preferable to further provide a structure for introducing an inert gas such as carbon dioxide into the mixer in order to reliably prevent an accident such as an explosion or a fire.
- an inert gas such as carbon dioxide
- the oil mud is absorbed by the biomass and the like, and a solid fuel with good handling properties can be produced.
- the above-mentioned solid fuel is a mixture of oil mud and biomass, there is a risk that a flammable gas is generated from the mixture, and a spark is ignited by the flammable gas, causing an explosion or a fire.
- a method for handling a substance in which flammable gas is volatilized according to the present invention that is, introducing air into a storage tank, and setting the concentration of the generated flammable gas to a concentration that does not cause an explosion or fire, that is, a lower explosion limit concentration. Dilute to less than
- the specific amount of air introduced into the storage tank is appropriately determined by the amount of flammable gas, the volume of the storage tank, etc., as in the case of the above mixing.
- the dilution gas used in the present invention is free air. As described later, in the present invention, it is possible to use a large amount of the air used for diluting the combustible gas as the combustion air for the firing furnace. O Should be introduced within
- the storage of the solid fuel includes not only long-term storage but also the case where the manufactured solid fuel is temporarily stored in the tank to be measured because the manufactured solid fuel is used immediately.
- a flammable gas detector in the storage tank that constantly detects the concentration of the flammable gas.
- the combustible gas detector detects a combustible gas with a concentration higher than a predetermined level, the configuration in which the amount of air introduced into the storage tank is increased, or in some cases, the carbon dioxide
- An example of a method of using the solid fuel manufactured and stored in this manner is a method of using the solid fuel that is introduced into a firing furnace via a pipe and burned as fuel.
- the air used for diluting the combustible gas when mixing the oil mud and biomass, or the rare gas of the combustible gas when storing the solid fuel is preferable that the air used for the soot be supplied into the firing furnace as combustion air. This makes it possible to process a large amount of exhaust gas containing combustible gas from a mixer or storage tank safely and effectively, and to effectively use the calorific value of the combustible gas. .
- Fig. 1 is a schematic diagram showing a solid fuel production facility and a facility that uses the solid fuel.
- a batch of waste tatami mat A weighed by a predetermined method is put into the crusher 1 and crushed with a proportion of crushed material having a length of 5 cm or less of 80% by mass or more. It is crushed into objects.
- the resulting debris from waste tatami A is transported by conveyor '2, and organic powder (toner, heavy oil ash) is quantitatively supplied from storage device 3 along the way, and the two are mixed.
- hopper 4 a batch of waste tatami mat A weighed by a predetermined method is put into the crusher 1 and crushed with a proportion of crushed material having a length of 5 cm or less of 80% by mass or more. It is crushed into objects.
- the resulting debris from waste tatami A is transported by conveyor '2, and organic powder (toner, heavy oil ash) is quantitatively supplied from storage device 3 along the way, and the two are mixed.
- bin 4 Stored in hopper 4.
- One batch of waste tatami A crushed material (approx. 200 kg) stored in hopper 4 is mixed with one batch of oil mud (heavy oil sludge approx. 2). 0 0 kg) is added together with X and stirred and mixed for a predetermined time (about 4 minutes). At this time, a predetermined amount (approximately 20 m 3 / min) of air is introduced into the mixer 5, and the mixing operation is performed while diluting the flammable gas that evaporates from the mixture to a concentration that does not cause an explosion or fire. Done.
- a combustible gas detector 6 is installed in the mixer 5, and in the unlikely event that a combustible gas of a predetermined concentration or more is detected, the mixing operation is immediately stopped and the C 0 2 gas is mixed.
- An operation control panel 7 is provided to perform control such as introduction into 5.
- the oil mud X is mixed with the crushed material of the mixed waste tatami A.
- the solid fuel Y discharged from the mixer 5 is pulverized by a pulverizer 8 installed downstream thereof, conveyed upward by a conveyor 9, foreign matter is removed by a drum magnetic separator 10, and the trommel 1
- the particle size is adjusted with 1 and stored in storage tank 1 2.
- a predetermined amount (up to about 30 mV min) of air is introduced into the storage tank 12 and storage is performed while diluting the combustible gas generated from the solid fuel Y to a concentration that does not cause an explosion or fire. Is called.
- a flammable gas detector 6 is installed, and in the unlikely event that a flammable gas of a predetermined concentration or more is detected, C ⁇ 2 It is connected to the operation control panel 7 that controls the introduction of gas into the storage tank 1 2.
- the solid fuel Y stored in such a state is weighed by the meter 1 3 ′, and instead of the pulverized coal that is the main fuel of the cement kiln 14, or in combination with the pulverized coal, it goes to the burner 15.
- the air is fed into the cement kiln 14 through the fuel injection port of the burner 15.
- Solid fuel Y injected into cement kiln 14 is completely burned in a short time before landing on the bottom of the furnace by the flame from PANA 1 15 and the combustion residue of solid fuel is become part of the ingredients.
- the air used for diluting the combustible gas exhausted from the mixer 5 and the air used for diluting the combustible gas exhausted from the storage tank 12 are combined with the clinker filter through the bag filter 16. And used as cooling air in the cement kiln 14 as well as being used for cooling the clicker.
- foreign matter in the solid fuel removed by the drum magnetic separator 10 and the trommel 11 is introduced from the kiln bottom of the cement kiln 14 and used as fuel, and the residue is one of the components of the clean force. Part.
- the flammable gas is explode or expelled by air without using an inert gas such as nitrogen or carbon dioxide that must be manufactured or purchased. Since the method is used to dilute to a concentration that does not cause a fire, it is possible to handle materials that volatilize flammable gases at low cost and safely in operations such as mixing and storage.
- the air used for diluting the combustible gas is used as combustion air
- the exhaust gas from the handling device such as the mixing device or the storage device can be treated safely and effectively.
- the calorific value of the combustible gas can be used effectively.
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- Engineering & Computer Science (AREA)
- Mechanical Engineering (AREA)
- General Engineering & Computer Science (AREA)
- Environmental & Geological Engineering (AREA)
- Chemical & Material Sciences (AREA)
- Combustion & Propulsion (AREA)
- Oil, Petroleum & Natural Gas (AREA)
- Life Sciences & Earth Sciences (AREA)
- Sustainable Development (AREA)
- Sustainable Energy (AREA)
- Solid Fuels And Fuel-Associated Substances (AREA)
- Treatment Of Sludge (AREA)
Abstract
Description
Claims
Priority Applications (5)
Application Number | Priority Date | Filing Date | Title |
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US12/224,494 US8453584B2 (en) | 2006-03-02 | 2007-02-26 | Method for handling substance from which combustible gas volatilizes, method for producing solid fuel, method for storing solid fuel, method for using solid fuel, and apparatus for using solid fuel |
CN200780007511.4A CN101395427B (zh) | 2006-03-02 | 2007-02-26 | 可燃性气体挥发的物质的处理方法、固体燃料的制造方法、固体燃料的贮存方法、固体燃料的使用方法、以及固体燃料的使用装置 |
EP07737733A EP1990577A1 (en) | 2006-03-02 | 2007-02-26 | Method of handling substance from which combustible gas volatilizes, process for producing solid fuel, method of storing solid fuel, method of using solid fuel, and apparatus using solid fuel |
KR1020087021378A KR101386731B1 (ko) | 2006-03-02 | 2007-02-26 | 가연성 가스가 휘발하는 물질의 취급 방법 |
JP2008502879A JP4913125B2 (ja) | 2006-03-02 | 2007-02-26 | 可燃性ガスが揮発する物質の取扱方法 |
Applications Claiming Priority (2)
Application Number | Priority Date | Filing Date | Title |
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JP2006-055783 | 2006-03-02 | ||
JP2006055783 | 2006-03-02 |
Publications (1)
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WO2007100120A1 true WO2007100120A1 (ja) | 2007-09-07 |
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PCT/JP2007/054122 WO2007100120A1 (ja) | 2006-03-02 | 2007-02-26 | 可燃性ガスが揮発する物質の取扱方法、固体燃料の製造方法、固体燃料の貯留方法、固体燃料の使用方法、および固体燃料の使用装置 |
Country Status (6)
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US (1) | US8453584B2 (ja) |
EP (1) | EP1990577A1 (ja) |
JP (1) | JP4913125B2 (ja) |
KR (1) | KR101386731B1 (ja) |
CN (1) | CN101395427B (ja) |
WO (1) | WO2007100120A1 (ja) |
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JP2016190761A (ja) * | 2015-03-31 | 2016-11-10 | 住友大阪セメント株式会社 | セメント焼成用固体燃料の製造方法及び製造装置 |
JP2018168045A (ja) * | 2017-03-30 | 2018-11-01 | 宇部興産株式会社 | セメントクリンカの製造方法及びセメントの製造方法 |
JP2022150887A (ja) * | 2021-03-26 | 2022-10-07 | 株式会社御池鐵工所 | バイオマス燃料用燃焼炉及びボイラシステム並びにバイオマス燃料の燃焼方法 |
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EP1990577A1 (en) * | 2006-03-02 | 2008-11-12 | Taiheiyo Cement Corporation | Method of handling substance from which combustible gas volatilizes, process for producing solid fuel, method of storing solid fuel, method of using solid fuel, and apparatus using solid fuel |
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Citations (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPH02160988A (ja) * | 1988-12-08 | 1990-06-20 | Oji Paper Co Ltd | クラフトパルプ工場の臭気性ガス処理方法 |
JP2002323213A (ja) * | 2001-04-26 | 2002-11-08 | Nippon Steel Corp | 含油スラッジの焼却方法 |
JP2004002155A (ja) * | 2002-03-22 | 2004-01-08 | Taiheiyo Cement Corp | セメント混和材 |
JP2005207684A (ja) * | 2004-01-23 | 2005-08-04 | Ishikawajima Harima Heavy Ind Co Ltd | 密閉式廃棄物焼却処理設備の不活性ガス封入方法及び装置 |
Family Cites Families (29)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US1781934A (en) * | 1925-06-08 | 1930-11-18 | Frederick T Snyder | Process of distilling material and cracking oil |
US1861452A (en) * | 1927-12-05 | 1932-06-07 | U G L Contracting Company | Process of producing coal gas |
US1954352A (en) * | 1932-03-14 | 1934-04-10 | Milwaukee Electric Railway And | Apparatus for treating pulverized fuel such as coal and the like |
US2412879A (en) * | 1941-05-31 | 1946-12-17 | Standard Oil Dev Co | Chemical process |
US3984217A (en) * | 1975-02-14 | 1976-10-05 | American Air Filter Company, Inc. | Wet gas cleaning system |
JPS5439401A (en) | 1977-09-05 | 1979-03-26 | Masao Kobayashi | Production of solid fuels |
DE2913666C2 (de) * | 1979-04-05 | 1986-01-02 | Carl Still Gmbh & Co Kg, 4350 Recklinghausen | Verfahren zur Herstellung von Hüttenformkoks |
US4528917A (en) * | 1983-07-05 | 1985-07-16 | Northwest Iron Fireman, Inc. | Solid fuel burner |
US4715810A (en) * | 1985-06-28 | 1987-12-29 | Aluminum Company Of America | Process and apparatus for removing volatiles from metal |
US5174067A (en) * | 1990-10-19 | 1992-12-29 | Shin-Etsu Handotai Co., Ltd. | Automatic wafer lapping apparatus |
US5117771A (en) * | 1991-08-23 | 1992-06-02 | Vanguard Environmental, Inc. | Method and apparatus to decontaminate soil |
US5259358A (en) * | 1992-07-14 | 1993-11-09 | Gas Research Institute | Air-fuel ratio control system for catalytic engine exhaust emission control |
US5250080A (en) * | 1992-10-13 | 1993-10-05 | Corpoven, S.A. | Process for manufacturing a solid fuel |
US5937652A (en) * | 1992-11-16 | 1999-08-17 | Abdelmalek; Fawzy T. | Process for coal or biomass fuel gasification by carbon dioxide extracted from a boiler flue gas stream |
US6752581B1 (en) * | 1994-06-10 | 2004-06-22 | Johnson & Johnson Vision Care, Inc. | Apparatus for removing and transporting articles from molds |
US5720165A (en) * | 1995-09-21 | 1998-02-24 | Bioten Gp | System for burning biomass to produce hot gas |
US5728271A (en) * | 1996-05-20 | 1998-03-17 | Rti Resource Transforms International Ltd. | Energy efficient liquefaction of biomaterials by thermolysis |
DE19722408C1 (de) * | 1997-05-28 | 1999-03-25 | Singulus Technologies Ag | Vorrichtung und Verfahren zum getrennten Transportieren von Substraten |
US5910454A (en) * | 1998-05-29 | 1999-06-08 | Sprules; Rodney K. | Coffee-based solid fuel composition |
US6553924B2 (en) * | 1998-10-19 | 2003-04-29 | Eco/Technologies, Llc | Co-combustion of waste sludge in municipal waste combustors and other furnaces |
US6145599A (en) * | 1999-05-22 | 2000-11-14 | Mumme; Christian F. | Anti-combustion safeguard for confined combustibles |
US6245390B1 (en) * | 1999-09-10 | 2001-06-12 | Viatcheslav Baranovski | High-velocity thermal spray apparatus and method of forming materials |
US6973883B1 (en) * | 2001-03-22 | 2005-12-13 | The Texas A&M University System | Reburn system with feedlot biomass |
US6832485B2 (en) * | 2001-11-26 | 2004-12-21 | Ormat Industries Ltd. | Method of and apparatus for producing power using a reformer and gas turbine unit |
US6726888B2 (en) * | 2002-01-25 | 2004-04-27 | General Electric Company | Method to decrease emissions of nitrogen oxide and mercury |
WO2003080532A1 (fr) | 2002-03-22 | 2003-10-02 | Taiheiyo Cement Corporation | Adjuvant de ciment |
US6887389B2 (en) * | 2002-10-23 | 2005-05-03 | Wendell Judd | Method and apparatus for recycling sewage sludge utilizing spent water-softener lime |
EP1990577A1 (en) * | 2006-03-02 | 2008-11-12 | Taiheiyo Cement Corporation | Method of handling substance from which combustible gas volatilizes, process for producing solid fuel, method of storing solid fuel, method of using solid fuel, and apparatus using solid fuel |
US8695514B2 (en) * | 2009-05-14 | 2014-04-15 | Alstom Technology Ltd. | Gas leakage reduction system |
-
2007
- 2007-02-26 EP EP07737733A patent/EP1990577A1/en not_active Withdrawn
- 2007-02-26 KR KR1020087021378A patent/KR101386731B1/ko active IP Right Grant
- 2007-02-26 US US12/224,494 patent/US8453584B2/en not_active Expired - Fee Related
- 2007-02-26 JP JP2008502879A patent/JP4913125B2/ja active Active
- 2007-02-26 WO PCT/JP2007/054122 patent/WO2007100120A1/ja active Application Filing
- 2007-02-26 CN CN200780007511.4A patent/CN101395427B/zh not_active Expired - Fee Related
Patent Citations (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPH02160988A (ja) * | 1988-12-08 | 1990-06-20 | Oji Paper Co Ltd | クラフトパルプ工場の臭気性ガス処理方法 |
JP2002323213A (ja) * | 2001-04-26 | 2002-11-08 | Nippon Steel Corp | 含油スラッジの焼却方法 |
JP2004002155A (ja) * | 2002-03-22 | 2004-01-08 | Taiheiyo Cement Corp | セメント混和材 |
JP2005207684A (ja) * | 2004-01-23 | 2005-08-04 | Ishikawajima Harima Heavy Ind Co Ltd | 密閉式廃棄物焼却処理設備の不活性ガス封入方法及び装置 |
Cited By (11)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP2008086973A (ja) * | 2006-10-05 | 2008-04-17 | Taiheiyo Cement Corp | 水素発生油泥の混合方法、固体燃料の製造方法、および固体燃料の貯留方法 |
JP2010089979A (ja) * | 2008-10-06 | 2010-04-22 | Taiheiyo Cement Corp | フロン或いはフロン類似物質を含有する合成樹脂発泡体の処理方法 |
JP2010089978A (ja) * | 2008-10-06 | 2010-04-22 | Taiheiyo Cement Corp | フロン或いはフロン類似物質を含有する合成樹脂発泡体の処理方法 |
JP2010270244A (ja) * | 2009-05-22 | 2010-12-02 | Toa Oil Kogyosho:Kk | 固形燃料の製造システム |
JP2011093991A (ja) * | 2009-10-28 | 2011-05-12 | Taiheiyo Cement Corp | 低引火点廃油の処理方法および固体燃料 |
JP2011201982A (ja) * | 2010-03-25 | 2011-10-13 | Taiheiyo Cement Corp | 廃油系固体燃料の使用方法 |
JP2012145291A (ja) * | 2011-01-13 | 2012-08-02 | Nippon Steel Engineering Co Ltd | 廃棄物溶融処理方法 |
JP2016190761A (ja) * | 2015-03-31 | 2016-11-10 | 住友大阪セメント株式会社 | セメント焼成用固体燃料の製造方法及び製造装置 |
JP2018168045A (ja) * | 2017-03-30 | 2018-11-01 | 宇部興産株式会社 | セメントクリンカの製造方法及びセメントの製造方法 |
JP2022150887A (ja) * | 2021-03-26 | 2022-10-07 | 株式会社御池鐵工所 | バイオマス燃料用燃焼炉及びボイラシステム並びにバイオマス燃料の燃焼方法 |
JP7467383B2 (ja) | 2021-03-26 | 2024-04-15 | 株式会社御池鐵工所 | バイオマス燃料用燃焼炉及びボイラシステム並びにバイオマス燃料の燃焼方法 |
Also Published As
Publication number | Publication date |
---|---|
US8453584B2 (en) | 2013-06-04 |
KR20080106216A (ko) | 2008-12-04 |
JP4913125B2 (ja) | 2012-04-11 |
US20090031932A1 (en) | 2009-02-05 |
JPWO2007100120A1 (ja) | 2009-07-23 |
CN101395427A (zh) | 2009-03-25 |
CN101395427B (zh) | 2015-06-17 |
EP1990577A1 (en) | 2008-11-12 |
KR101386731B1 (ko) | 2014-04-17 |
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