WO2005093014A1 - Method for removing tar in fluidized layer furnace - Google Patents
Method for removing tar in fluidized layer furnace Download PDFInfo
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- WO2005093014A1 WO2005093014A1 PCT/JP2005/005388 JP2005005388W WO2005093014A1 WO 2005093014 A1 WO2005093014 A1 WO 2005093014A1 JP 2005005388 W JP2005005388 W JP 2005005388W WO 2005093014 A1 WO2005093014 A1 WO 2005093014A1
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- alumina
- fluidized bed
- tar
- silica
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J37/00—Processes, in general, for preparing catalysts; Processes, in general, for activation of catalysts
- B01J37/0072—Preparation of particles, e.g. dispersion of droplets in an oil bath
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J21/00—Catalysts comprising the elements, oxides, or hydroxides of magnesium, boron, aluminium, carbon, silicon, titanium, zirconium, or hafnium
- B01J21/12—Silica and alumina
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- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10B—DESTRUCTIVE DISTILLATION OF CARBONACEOUS MATERIALS FOR PRODUCTION OF GAS, COKE, TAR, OR SIMILAR MATERIALS
- C10B47/00—Destructive distillation of solid carbonaceous materials with indirect heating, e.g. by external combustion
- C10B47/18—Destructive distillation of solid carbonaceous materials with indirect heating, e.g. by external combustion with moving charge
- C10B47/22—Destructive distillation of solid carbonaceous materials with indirect heating, e.g. by external combustion with moving charge in dispersed form
- C10B47/24—Destructive distillation of solid carbonaceous materials with indirect heating, e.g. by external combustion with moving charge in dispersed form according to the "fluidised bed" technique
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- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10B—DESTRUCTIVE DISTILLATION OF CARBONACEOUS MATERIALS FOR PRODUCTION OF GAS, COKE, TAR, OR SIMILAR MATERIALS
- C10B53/00—Destructive distillation, specially adapted for particular solid raw materials or solid raw materials in special form
- C10B53/02—Destructive distillation, specially adapted for particular solid raw materials or solid raw materials in special form of cellulose-containing material
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- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10G—CRACKING HYDROCARBON OILS; PRODUCTION OF LIQUID HYDROCARBON MIXTURES, e.g. BY DESTRUCTIVE HYDROGENATION, OLIGOMERISATION, POLYMERISATION; RECOVERY OF HYDROCARBON OILS FROM OIL-SHALE, OIL-SAND, OR GASES; REFINING MIXTURES MAINLY CONSISTING OF HYDROCARBONS; REFORMING OF NAPHTHA; MINERAL WAXES
- C10G11/00—Catalytic cracking, in the absence of hydrogen, of hydrocarbon oils
- C10G11/14—Catalytic cracking, in the absence of hydrogen, of hydrocarbon oils with preheated moving solid catalysts
- C10G11/18—Catalytic cracking, in the absence of hydrogen, of hydrocarbon oils with preheated moving solid catalysts according to the "fluidised-bed" technique
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- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10G—CRACKING HYDROCARBON OILS; PRODUCTION OF LIQUID HYDROCARBON MIXTURES, e.g. BY DESTRUCTIVE HYDROGENATION, OLIGOMERISATION, POLYMERISATION; RECOVERY OF HYDROCARBON OILS FROM OIL-SHALE, OIL-SAND, OR GASES; REFINING MIXTURES MAINLY CONSISTING OF HYDROCARBONS; REFORMING OF NAPHTHA; MINERAL WAXES
- C10G9/00—Thermal non-catalytic cracking, in the absence of hydrogen, of hydrocarbon oils
- C10G9/06—Thermal non-catalytic cracking, in the absence of hydrogen, of hydrocarbon oils by pressure distillation
- C10G9/08—Apparatus therefor
- C10G9/12—Removing incrustation
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- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10J—PRODUCTION OF PRODUCER GAS, WATER-GAS, SYNTHESIS GAS FROM SOLID CARBONACEOUS MATERIAL, OR MIXTURES CONTAINING THESE GASES; CARBURETTING AIR OR OTHER GASES
- C10J3/00—Production of combustible gases containing carbon monoxide from solid carbonaceous fuels
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- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10J—PRODUCTION OF PRODUCER GAS, WATER-GAS, SYNTHESIS GAS FROM SOLID CARBONACEOUS MATERIAL, OR MIXTURES CONTAINING THESE GASES; CARBURETTING AIR OR OTHER GASES
- C10J3/00—Production of combustible gases containing carbon monoxide from solid carbonaceous fuels
- C10J3/72—Other features
- C10J3/82—Gas withdrawal means
- C10J3/84—Gas withdrawal means with means for removing dust or tar from the gas
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- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10K—PURIFYING OR MODIFYING THE CHEMICAL COMPOSITION OF COMBUSTIBLE GASES CONTAINING CARBON MONOXIDE
- C10K3/00—Modifying the chemical composition of combustible gases containing carbon monoxide to produce an improved fuel, e.g. one of different calorific value, which may be free from carbon monoxide
- C10K3/02—Modifying the chemical composition of combustible gases containing carbon monoxide to produce an improved fuel, e.g. one of different calorific value, which may be free from carbon monoxide by catalytic treatment
- C10K3/023—Reducing the tar content
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- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10J—PRODUCTION OF PRODUCER GAS, WATER-GAS, SYNTHESIS GAS FROM SOLID CARBONACEOUS MATERIAL, OR MIXTURES CONTAINING THESE GASES; CARBURETTING AIR OR OTHER GASES
- C10J2300/00—Details of gasification processes
- C10J2300/12—Heating the gasifier
- C10J2300/1246—Heating the gasifier by external or indirect heating
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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
- Y02P—CLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
- Y02P20/00—Technologies relating to chemical industry
- Y02P20/50—Improvements relating to the production of bulk chemicals
- Y02P20/52—Improvements relating to the production of bulk chemicals using catalysts, e.g. selective catalysts
Definitions
- the present invention relates to a method for removing tar in a fluidized bed furnace in a system for gasifying fossil fuels such as coal and heavy oil, biomass, and the like to generate a fuel gas and a chemical raw material gas.
- Gasifiers for coal and the like are roughly classified into three types: a spouted bed gasifier, a fluidized bed gasifier, and a fixed bed gasifier.
- a spouted bed gasifier coarse pulverized coal with an average particle size of 16 mm is used.
- pulverized coal is fluidized by oxygen or air, which is a gasifying agent, and water vapor, and conversion into CO, CO, and H proceeds in the furnace.
- Tar treatment methods in fluidized bed gasification include (1) a method in which the gasification temperature is raised to 900 ° C or more, and (2) a tar decomposition catalyst component such as nickel molybdenum is charged or fluidized into a furnace. (3) A adsorptive substance such as alumina, zeolite, limestone, etc. is placed in the furnace, or is charged as a fluid medium, adsorbs tar, and is decomposed in a regeneration furnace such as a combustion furnace. Methods have been studied.
- the method (1) reduces the cold gas efficiency and increases energy loss
- the method (2) requires a price of nickel molybdenum used as a decomposition catalyst component impregnated into particles such as alumina. Is expensive, and the particles are easily crushed due to wear due to fluidization of the particles, and the gasification furnace power is also scattered outside the system, or the decomposition effect is reduced due to the carbon content precipitated on the particle surface. Therefore, the method (3), which requires the replenishment of particles and is less economical, regenerates particles by decomposition and combustion of carbon and other substances by using adsorbent particles such as alumina and zeolite without using expensive decomposition catalysts. To some extent, but adsorbable particles • The carbon content resolution is low, and the fine particles are granulated.
- the present invention has been made in view of the above circumstances, and has as its object to provide an excellent method for removing tar in a fluidized bed furnace. Another object of the present invention is to provide a method for removing tar in a fluidized bed furnace having high cold gas efficiency.
- the present inventors have conducted intensive studies to achieve the above object, and as a result, in order to improve cold gas efficiency, set the gasification temperature to a low temperature (for example, 600 ° C or more and less than 900 ° C).
- a low temperature for example, 600 ° C or more and less than 900 ° C.
- a regeneration furnace such as a combustion furnace.
- specific adsorbent particles for example,
- tar generated from the raw material is subjected to fluid catalytic cracking.
- Catalyst, fluid catalytic cracking equilibrium catalyst adsorbs and decomposes using silica-alumina-based particles or alumina-based particles produced by oil immersion granulation, and z or fluid catalytic cracking catalyst, fluid catalytic cracking equilibrium catalyst,
- a method for removing tar in a fluidized bed furnace which comprises attaching and burning silica-alumina-based particles or alumina-based particles produced by an oil immersion granulation method.
- the raw material power is also generated.
- Adsorbed particles to adsorb and decompose the tar, and adhere to Z or adsorbent particles for combustion A method for removing tar in a fluidized bed furnace is provided.
- an excellent method for removing tar in a fluidized bed furnace can be provided. Further, it is possible to provide a method for removing tar in a fluidized-bed furnace having high cold gas efficiency.
- FIG. 1 is a schematic diagram of a publishing type fluidized bed gasification furnace.
- fluidized bed is synonymous with “fluidized bed”.
- the raw material used in the method of the present invention is not particularly limited, and for example, fossil raw materials such as petroleum, coal, and coats, waste, biomass, and the like can be used.
- biomass particularly woody biomass, is preferred.
- the fluidized bed furnace is not particularly limited.
- a fluidized bed furnace that processes a publishing type fluidized bed, an external / internal circulation type fluidized bed, a pressurized type / normal pressure type fluidized bed, or the like is used.
- it is a fluidized bed furnace using a publishing type fluidized bed as a process.
- conditions for gasifying, thermally decomposing, or partially oxidizing the raw material can be appropriately adjusted according to the type of the raw material and the like.
- the raw material is gasified at a low temperature.
- it is gasified at a low temperature of less than 900 ° C, more preferably 850 ° C or less. Further, it is usually gasified at a temperature of 500 ° C or higher, preferably 550 ° C or higher.
- tar produced by the above-mentioned raw material power is adsorbed and decomposed using adsorptive particles to remove tar.
- examples of the adsorptive particles include fluid catalytic cracking catalyst (FCC catalyst) particles, fluid catalytic cracking equilibrium catalyst (FCC equilibrium catalyst) particles, silica-alumina particles, and alumina produced by an oil immersion granulation method.
- Based particles porous alumina, activated alumina, ⁇ -alumina, activated bokeh Site
- silica-based particles such as silica gel, raw concrete sludge and its sludge cake, particles of lime cake, concrete, concrete structures and waste of concrete structures, and clay mineral particles such as activated clay, zeolite, and sepiolite.
- the adsorptive particles include used adsorptive particles or a catalyst containing the adsorptive particles.
- the used catalyst means a catalyst used in a process that is the original purpose of the catalyst such as a desulfurization reaction of petroleum fraction and discarded due to a decrease in desulfurization reaction activity and the like.
- These used catalysts can be used as they are, or they can be used by burning and regenerating adhering carbonaceous materials, and by washing and removing precipitated metal components with an acid or the like.
- adsorptive particles FCC catalyst particles, FCC equilibrium catalyst particles, silica-alumina-based particles, and alumina-based particles produced by an oil immersion granulation method are preferable.
- porous alumina or activated alumina produced by an oil immersion granulation method is preferable.
- the oil immersion granulation method is a method of immersing mainly hydroxylated aluminum converted into a hydrogel in a heated roll bath and granulating into spherical particles by surface tension.
- the fluid catalytic cracking catalyst is a catalyst for catalytically cracking heavy oil (such as vacuum gas oil or atmospheric residual oil) to produce gasoline with a high octane number.
- Metal oxides such as silica 'alumina, titanium, and alumina' titanium; clay minerals such as kaolin and bentonite; various zeolites; 'Examples include porous particle FCC catalysts prepared by a method such as spray drying using alumina, rare earth-substituted Y zeolite, kaolin, or the like.
- Fluid catalytic cracking equilibrium catalyst is a catalyst that is periodically withdrawn when the catalytic activity of the FCC unit becomes constant. Etc.), the metals such as iron, vanadium and nickel accumulated on the above FCC catalyst.
- vanadium and Z or nickel on the particle surface are 500-15000 mass ppm
- FCC equilibrium catalysts that have accumulated FCC and have a vanadium and / or Z or nickel accumulation of 800-5000 ppm by mass!
- a new catalyst is added at appropriate times in order to keep the activity of the FCC catalyst constant. It is completely mixed with a certain catalyst, and the activity of the catalyst will be averaged. However, since the amount of catalyst in the equipment would be excessive if it was not used, a certain amount was always extracted.
- tar can be adsorbed and decomposed by pre-filling these adsorbed particles in a fluidized-bed furnace or charging them into a fluidized-bed furnace.
- tar can also be adsorbed and decomposed by using these adsorbed particles as a fluid medium and a circulating medium (circulating solid) of a fluidized bed furnace.
- these adsorptive particles when using a fluidized bed furnace that processes a publishing type fluidized bed and an internal circulation type fluidized bed, these adsorptive particles can be used as a fluidized medium.
- these adsorptive particles can be used as a circulating medium.
- tar can be adsorbed and decomposed in a fluidized bed furnace (for example, a freeboard portion or the like).
- the conditions for scattering the adsorptive particles can be appropriately adjusted according to the type of the fluidized bed and the adsorptive particles.
- tar produced by the above-mentioned raw material force is attached to the above-mentioned adsorptive particles and burned, whereby tar can be removed.
- the combustion of the attached tar can be performed in the combustion zone in the fluidized bed furnace.
- the tar can be continuously removed by adsorbing and decomposing the tar using the adsorptive particles and further burning the adhered tar remaining without being decomposed by the adsorptive particles. it can.
- the adsorbable particles since the adsorbable particles are regenerated in the combustion region by the combustion of the attached tar, the adsorbable particles can be used continuously.
- the method of the present invention is efficient because the heat of combustion can be used as a gasification heat source.
- gasified gas generated by the combustion of raw materials and fuel generated by the combustion of tar Since the combustion gas is separated, the gasification gas becomes a high-calorie gas.
- a lab-type publishing type fluidized-bed gasification furnace 1 shown in FIG. 1 was used.
- This apparatus 1 is composed of a gasifier 2, a dispersion plate 4, and a wind box 6.
- This apparatus 1 is cylindrical and made of stainless steel with an inner diameter of 100 mm and a height of 1.5 m (the disperser 4 is also up to the furnace outlet 8).
- an electric furnace 10 for controlling the gasification temperature is installed outside the device 1. Nitrogen gas is used as the gasification gas at a flow rate of 6 liters Z, from the gas inlet 12 through the gas preheater 14 equipped with a gas preheating function, the wind box 6, and the disperser 4, Feeded to 2.
- the apparatus 1 was previously filled with particles (particles A to E) having a height of 150 mm as a fluid medium 16 on a dispersion plate 4.
- the fluid medium 16 flows and scatters inside the gasification furnace 2 by the gas gas supplied through the dispersion plate 4.
- a raw material feeder 18 provided outside the apparatus 1 is heated.
- the raw material and the particles were supplied quantitatively from the feeder and the particle feeder 20, respectively.
- the gasified product gas and tar are discharged to the outside through the furnace outlet 8 at the upper part of the gasification furnace, and a part of the gas and tar is introduced into the organic solvent (ethanol) for tar recovery in the tar recovery unit 22. , Completely recovered.
- the amount of the collected tar sample was measured by a combination of GC-FID and desolvation residue method.
- the raw material is wood biomass (cedar: carbon content 48.7%, hydrogen content 5.8%, oxygen content 40.2%, ash content 0.4%, moisture 4.9%), particle size 200—300 / zm And supplied at a flow rate of 5 gZ.
- the total amount of the fluid medium particles was adjusted to a particle size of lmm or less and supplied at a flow rate of 60 gZ.
- Particle A Alumina particles produced by the oil immersion granulation method
- the injection rate of the aqueous solution of aluminum sulfate was set to about 102 mlZmin, and the injection rate of the aqueous solution of sodium aluminate was set to 23.3 mlZmin.
- the mixture was simultaneously mixed with a metering pump under high shear.
- the target basic aluminum sulfate hydrosol molar ratio (SO ZA1 O) is 0.9
- a circulating system of the mixture was formed under high shear so as to obtain 2, and 546 g of an aqueous solution of sodium aluminate was added thereto and mixed at an injection rate of 2. OmlZmin.
- the prepared basic aluminum sulfate hydrosol is further aged for 20 days at room temperature with stirring and aging to promote polymerization and increase the viscosity of the basic aluminum sulfate hydrosol to prepare a concentrated ammonia monosalt in advance.
- PH buffer solution of ammonium chloride (NH Cl: 70g and concentrated
- aqueous ammonia Approximately 500 ml of aqueous ammonia was ion-exchanged and hydrogenated, and the basic aluminum hydrosol was extruded with a syringe into a buffer solution (pH 9.84), adjusted to a total volume of 1 liter, and hydrogelated at room temperature.
- a columnar transparent alumina hydrogel was prepared. After washing with water and drying, it was calcined at 600 ° C. for 3 hours to obtain transparent activated alumina particles.
- the crystalline state of the particle A (600 ° C. for 3 hours) is amorphous, the BET specific surface area is 274 m 2 Zg, and the pore area is 0.37 ml / g.
- Particle B silica 'alumina particles (Neobead SA manufactured by Mizusawa I-Dagaku Kogyo Co., Ltd.)
- Particle C FCC equilibrium catalyst
- Particle D Limestone (made by Taiheiyo Cement, crushed product of 1 mm or less)
- Particle E Alumina particles manufactured by powder granulation method (GB, manufactured by Mizusawa Chemical Industry Co., Ltd.)
- the powder granulation method involves drying and pulverizing a hydrogel, followed by extrusion or fluidization. It refers to a method of molding and flowing.
- Example 1-9 Comparative Example 1-6
- the particle ratio was determined when the particles A, B, D and E were used. Table 2 shows the results.
- the powdering rate was as follows. The force of the following formula was also calculated, where d is the weight and e is the weight of the particles initially charged.
- the method of the present invention is suitable for use in a field of energy and a field of research using a system for producing gas for fuel and gas for chemical raw materials.
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Abstract
Description
流動層炉におけるタールの除去方法 Method of removing tar in fluidized bed furnace
技術分野 Technical field
[0001] 本発明は、石炭、重質油等の化石燃料、バイオマス等をガス化し、燃料用ガス、化 学原料用ガスを生成するシステムにおいて流動層炉における好適なタールの除去方 法に関する。 The present invention relates to a method for removing tar in a fluidized bed furnace in a system for gasifying fossil fuels such as coal and heavy oil, biomass, and the like to generate a fuel gas and a chemical raw material gas.
背景技術 Background art
[0002] 石炭等のガス化炉には、大別して、噴流床ガス化炉、流動床ガス化炉、固定床ガス 化炉の 3方式がある。このうち流動床方式石炭ガス化炉では、平均粒径が 1一 6mm の粗粉砕炭が使用される。この方式では、ガス化剤である酸素ないし空気、それに水 蒸気により粉炭を流動化させ、その炉内で CO、 CO、 Hへの変換が進行する。流動 [0002] Gasifiers for coal and the like are roughly classified into three types: a spouted bed gasifier, a fluidized bed gasifier, and a fixed bed gasifier. In the fluidized bed coal gasifier, coarse pulverized coal with an average particle size of 16 mm is used. In this method, pulverized coal is fluidized by oxygen or air, which is a gasifying agent, and water vapor, and conversion into CO, CO, and H proceeds in the furnace. Flow
2 2 twenty two
床による石炭ガス化は、反応温度が低くなるとタールが生成し、プロセス内において ハンドリングトラブルを発生する。従って、従来の技術では、ガス化温度 900°C以上 の条件下で行われてきた。また、タールの分解触媒として、石灰石、アルミナの使用 が検討されてきた。 Coal gasification using a bed generates tar when the reaction temperature decreases, causing handling trouble in the process. Therefore, in the prior art, the gasification temperature has been higher than 900 ° C. In addition, the use of limestone and alumina as catalysts for decomposing tar has been studied.
[0003] 流動床ガス化におけるタールの処理方法としては、(1)ガス化温度を 900°C以上に 高温化する方法、 (2)ニッケル モリブデン等のタール分解触媒成分を炉内へ投入 あるいは流動媒体に含有させて投入する方法、(3)アルミナ、ゼォライト、石灰石等 の吸着性物質を炉内に投入ある 、は流動媒体として投入し、タールを吸着して燃焼 炉等の再生炉で分解する方法等が検討されてきた。 [0003] Tar treatment methods in fluidized bed gasification include (1) a method in which the gasification temperature is raised to 900 ° C or more, and (2) a tar decomposition catalyst component such as nickel molybdenum is charged or fluidized into a furnace. (3) A adsorptive substance such as alumina, zeolite, limestone, etc. is placed in the furnace, or is charged as a fluid medium, adsorbs tar, and is decomposed in a regeneration furnace such as a combustion furnace. Methods have been studied.
[0004] しかしながら、(1)の方法は、冷ガス効率が低下し、エネルギーロスが大きくなり、 (2 )の方法は、分解触媒成分として用いるニッケル モリブデンをアルミナ等の粒子に含 浸したものの価格が高価であり、かつ、粒子の流動化による磨滅により容易に粉ィ匕し てガス化炉カも系外へ飛散してしまったり、あるいは粒子表面に析出する炭素分等 により分解効果が減少するため、粒子の補充が必要となり経済性に乏しぐ(3)の方 法は、高価な分解触媒を用いず、アルミナゃゼオライト等の吸着性粒子の利用により 炭素分等の分解燃焼による粒子の再生をある程度可能としたが、吸着性粒子の吸着 •炭素分分解能が低ぐまた、微細粒子を造粒した粒子のため粉ィ匕性が高ぐ炉内へ の補充が必要となる。 [0004] However, the method (1) reduces the cold gas efficiency and increases energy loss, and the method (2) requires a price of nickel molybdenum used as a decomposition catalyst component impregnated into particles such as alumina. Is expensive, and the particles are easily crushed due to wear due to fluidization of the particles, and the gasification furnace power is also scattered outside the system, or the decomposition effect is reduced due to the carbon content precipitated on the particle surface. Therefore, the method (3), which requires the replenishment of particles and is less economical, regenerates particles by decomposition and combustion of carbon and other substances by using adsorbent particles such as alumina and zeolite without using expensive decomposition catalysts. To some extent, but adsorbable particles • The carbon content resolution is low, and the fine particles are granulated.
このように、現在のタールの処理方法では、低コストでエネルギーを生成する要求 に応えられて 、な 、と 、うのが実情である。 As described above, in the current method of treating tar, it is the reality that the demand for producing energy at low cost is met.
[0005] 本発明は、上記事情に鑑みなされたものであり、流動層炉における優れたタールの 除去方法を提供することを目的とする。また、冷ガス効率が高い流動層炉におけるタ ールの除去方法を提供することを目的とする。 [0005] The present invention has been made in view of the above circumstances, and has as its object to provide an excellent method for removing tar in a fluidized bed furnace. Another object of the present invention is to provide a method for removing tar in a fluidized bed furnace having high cold gas efficiency.
発明の開示 Disclosure of the invention
[0006] 本発明者らは、上記目的を達成するため、鋭意検討を重ねた結果、冷ガス効率の 向上を図るために、ガス化温度を低温 (例えば 600°C以上 900°C未満)に低下させ、 低温ガス化時に生成するタールを、炉内で吸着性粒子を用いて吸着 ·分解し、及び Z又は、粒子表面に付着した炭素質等を燃焼炉等の再生炉で再生するシステムに おいて、特定の吸着性粒子、例えば、 [0006] The present inventors have conducted intensive studies to achieve the above object, and as a result, in order to improve cold gas efficiency, set the gasification temperature to a low temperature (for example, 600 ° C or more and less than 900 ° C). A system that adsorbs and decomposes tar generated during low-temperature gasification using adsorbent particles in the furnace, and regenerates Z or carbonaceous materials attached to the particle surface in a regeneration furnace such as a combustion furnace. In, specific adsorbent particles, for example,
(i)タールの高!、吸着 ·分解能と、流動化による炉内での耐粉ィ匕 (粉化率が少な 、)を 併せ持つ特定のアルミナ系粒子、シリカ'アルミナ系粒子又はシリカ系粒子 (i) Specific alumina-based particles, silica'alumina-based particles or silica-based particles that combine high tar, adsorption and resolution, and powder resistance in the furnace due to fluidization (poor powdering rate)
(ii)タールの吸着能と極めて高 、分解能を併せ持つ特定の粘土系鉱物系粒子 を用いることにより、吸着 ·分解能及び経済性が両立できることを見出し、本発明を 完成させた。 (ii) The present inventors have found that the use of specific clay-based mineral-based particles having both a tar adsorption ability and an extremely high and high resolution can achieve both adsorption, resolution and economy, and completed the present invention.
[0007] 本発明の第一の態様によれば、原料を、流動層炉でガス化、熱分解又は部分酸化 して、生成ガスを得るシステムにおいて、前記原料から生成するタールを、流動接触 分解触媒、流動接触分解平衡触媒、シリカ'アルミナ系粒子又は油浸造粒法で製造 されたアルミナ系粒子を用いて吸着,分解し、及び z又は、流動接触分解触媒、流 動接触分解平衡触媒、シリカ ·アルミナ系粒子又は油浸造粒法で製造されたアルミ ナ系粒子に付着させて燃焼することを含む流動層炉におけるタールの除去方法が 提供される。 [0007] According to a first aspect of the present invention, in a system in which a raw material is gasified, thermally decomposed, or partially oxidized in a fluidized bed furnace to obtain a product gas, tar generated from the raw material is subjected to fluid catalytic cracking. Catalyst, fluid catalytic cracking equilibrium catalyst, adsorbs and decomposes using silica-alumina-based particles or alumina-based particles produced by oil immersion granulation, and z or fluid catalytic cracking catalyst, fluid catalytic cracking equilibrium catalyst, Provided is a method for removing tar in a fluidized bed furnace, which comprises attaching and burning silica-alumina-based particles or alumina-based particles produced by an oil immersion granulation method.
[0008] 本発明の第二の態様によれば、原料を、流動層炉で 900°C未満でガス化、熱分解 又は部分酸ィ匕して、生成ガスを得るシステムにおいて、前記原料力も生成するタール を、吸着性粒子を用いて吸着,分解し、及び Z又は、吸着性粒子に付着させて燃焼 することを含む流動層炉におけるタールの除去方法が提供される。 [0008] According to a second aspect of the present invention, in a system in which a raw material is gasified, thermally decomposed, or partially oxidized in a fluidized bed furnace at less than 900 ° C to obtain a product gas, the raw material power is also generated. Adsorbed particles to adsorb and decompose the tar, and adhere to Z or adsorbent particles for combustion A method for removing tar in a fluidized bed furnace is provided.
本発明によれば、流動層炉における優れたタールの除去方法を提供することがで きる。また、冷ガス効率が高い流動層炉におけるタールの除去方法を提供することが できる。 According to the present invention, an excellent method for removing tar in a fluidized bed furnace can be provided. Further, it is possible to provide a method for removing tar in a fluidized-bed furnace having high cold gas efficiency.
図面の簡単な説明 Brief Description of Drawings
[0009] [図 1]パブリング型流動層ガス化炉の模式図である。 FIG. 1 is a schematic diagram of a publishing type fluidized bed gasification furnace.
発明を実施するための最良の形態 BEST MODE FOR CARRYING OUT THE INVENTION
[0010] 以下、本発明について説明する。尚、本発明では、「流動層」は「流動床」と同義で ある。 Hereinafter, the present invention will be described. In the present invention, “fluidized bed” is synonymous with “fluidized bed”.
本発明の方法で用いる原料は特に制限されず、例えば、石油、石炭、コータス等の 化石原料、廃棄物、バイオマス等を用いることができる。これらの原料のうち、バイオ マス、特に木質系ノ ィォマスが好適である。 The raw material used in the method of the present invention is not particularly limited, and for example, fossil raw materials such as petroleum, coal, and coats, waste, biomass, and the like can be used. Among these raw materials, biomass, particularly woody biomass, is preferred.
[0011] 本発明の方法では、流動層炉は特に制限されず、例えば、パブリング型流動層、 外部 ·内部循環型流動層、加圧型 ·常圧型流動層をプロセスとする流動層炉等を用 いることができる。好ましくは、パブリング型流動層をプロセスとする流動層炉である。 これらの流動層炉において、上記原料をガス化、熱分解又は部分酸化する際の条 件は、原料の種類等に応じて適宜調節することができる。 [0011] In the method of the present invention, the fluidized bed furnace is not particularly limited. For example, a fluidized bed furnace that processes a publishing type fluidized bed, an external / internal circulation type fluidized bed, a pressurized type / normal pressure type fluidized bed, or the like is used. Can be. Preferably, it is a fluidized bed furnace using a publishing type fluidized bed as a process. In these fluidized bed furnaces, conditions for gasifying, thermally decomposing, or partially oxidizing the raw material can be appropriately adjusted according to the type of the raw material and the like.
[0012] 尚、本発明では、上記原料を、低温でガス化することが好ましい。好ましくは、 900 °C未満、より好ましくは 850°C以下の低温でガス化する。また、通常は 500°C以上、 好ましくは 550°C以上の温度でガス化する。原料をこのような低温で処理することによ り、冷ガス効率を高めることができる。 [0012] In the present invention, it is preferable that the raw material is gasified at a low temperature. Preferably, it is gasified at a low temperature of less than 900 ° C, more preferably 850 ° C or less. Further, it is usually gasified at a temperature of 500 ° C or higher, preferably 550 ° C or higher. By treating the raw material at such a low temperature, the cold gas efficiency can be increased.
低温でガス化するとタールのトラブルが生じるが、本発明では、吸着性粒子を用い ることによりこの問題に対処できる。 Gasification at low temperatures causes tar problems, but the present invention can address this problem by using adsorbent particles.
[0013] 本発明の方法では、上記原料力 生成するタールを、吸着性粒子を用いて吸着- 分解することにより、タールを除去する。 [0013] In the method of the present invention, tar produced by the above-mentioned raw material power is adsorbed and decomposed using adsorptive particles to remove tar.
ここで、吸着性粒子としては、例えば、流動接触分解触媒 (FCC触媒)粒子、流動 接触分解平衡触媒 (FCC平衡触媒)粒子、シリカ'アルミナ系粒子、油浸造粒法で製 造されたアルミナ系粒子(多孔質アルミナ、活性アルミナ、 γ—アルミナ、活性ボーキ サイト等)、シリカゲル等のシリカ系粒子、生コンクリートスラッジ及びそのスラッジケー キ、ライムケーキ、コンクリート、コンクリート構造物及びコンクリート構造物の廃棄物等 の粒子、活性白土、ゼォライト、セピオライト等の粘土鉱物系粒子等が挙げられる。 本発明において、吸着性粒子には、使用済みの吸着性粒子も含まれ、又は吸着性 粒子を含む触媒も含まれる。 Here, examples of the adsorptive particles include fluid catalytic cracking catalyst (FCC catalyst) particles, fluid catalytic cracking equilibrium catalyst (FCC equilibrium catalyst) particles, silica-alumina particles, and alumina produced by an oil immersion granulation method. Based particles (porous alumina, activated alumina, γ-alumina, activated bokeh Site), silica-based particles such as silica gel, raw concrete sludge and its sludge cake, particles of lime cake, concrete, concrete structures and waste of concrete structures, and clay mineral particles such as activated clay, zeolite, and sepiolite. And the like. In the present invention, the adsorptive particles include used adsorptive particles or a catalyst containing the adsorptive particles.
[0014] 尚、前記使用済み触媒とは、石油留分の脱硫反応等触媒本来の使用目的である プロセスで使用され、脱硫反応活性等の低下により廃棄された触媒の意味である。 また、それらの使用済み触媒は、そのまま用いることもできるし、付着している炭素 質を燃焼して再生することにより、また、析出した金属分を酸等で洗浄 '除去して用い ることがでさる。 [0014] The used catalyst means a catalyst used in a process that is the original purpose of the catalyst such as a desulfurization reaction of petroleum fraction and discarded due to a decrease in desulfurization reaction activity and the like. These used catalysts can be used as they are, or they can be used by burning and regenerating adhering carbonaceous materials, and by washing and removing precipitated metal components with an acid or the like. Monkey
[0015] これらの吸着性粒子の中でも、 FCC触媒粒子、 FCC平衡触媒粒子、シリカ'アルミ ナ系粒子、油浸造粒法で製造されたアルミナ系粒子が好ましい。特に、油浸造粒法 で製造された多孔質アルミナ又は活性アルミナが好適である。これらを吸着性粒子と して用いることで、従来技術に対し、流動化時の粉化率を低下させ、かつ、タールの 吸着'分解能を高めることができる。 [0015] Among these adsorptive particles, FCC catalyst particles, FCC equilibrium catalyst particles, silica-alumina-based particles, and alumina-based particles produced by an oil immersion granulation method are preferable. In particular, porous alumina or activated alumina produced by an oil immersion granulation method is preferable. By using these as the adsorptive particles, the powdering rate at the time of fluidization can be reduced and the adsorbing / resolving power of tar can be increased as compared with the prior art.
尚、油浸造粒法とは、ヒドロゲルに転ィ匕した主に水酸ィ匕アルミニウムを、加熱したォ ィルバスに浸して、表面張力により球状粒子に造粒する方法である。 The oil immersion granulation method is a method of immersing mainly hydroxylated aluminum converted into a hydrogel in a heated roll bath and granulating into spherical particles by surface tension.
[0016] 流動接触分解触媒 (FCC触媒)は、重質油 (減圧軽油や常圧残油等)を接触分解 して、オクタン価の高いガソリンを製造するための触媒であり、例えば、アルミナ、シリ 力、シリカ'アルミナ、チタ-ァ、アルミナ 'チタ-ァ等の金属酸化物、カオリン、ベント ナイト等の粘土鉱物、各種ゼォライト、さら〖こはこれら力ゝら常法、例えば、アルミナ、シ リカ'アルミナ、希土類置換 Y型ゼオライト、カオリン等を用いてスプレードライ等の方 法により調製された多孔質粒子の FCC触媒等が挙げられる。 [0016] The fluid catalytic cracking catalyst (FCC catalyst) is a catalyst for catalytically cracking heavy oil (such as vacuum gas oil or atmospheric residual oil) to produce gasoline with a high octane number. Metal oxides such as silica 'alumina, titanium, and alumina' titanium; clay minerals such as kaolin and bentonite; various zeolites; 'Examples include porous particle FCC catalysts prepared by a method such as spray drying using alumina, rare earth-substituted Y zeolite, kaolin, or the like.
[0017] 流動接触分解平衡触媒 (FCC平衡触媒)は、この FCC装置の触媒活性が一定に なった際に定期的に抜き出される触媒のことで、重質油 (減圧軽油や常圧残油等)の 接触分解反応により上記 FCC触媒上に鉄、バナジウム、ニッケル等の金属が蓄積し たものである。 [0017] Fluid catalytic cracking equilibrium catalyst (FCC equilibrium catalyst) is a catalyst that is periodically withdrawn when the catalytic activity of the FCC unit becomes constant. Etc.), the metals such as iron, vanadium and nickel accumulated on the above FCC catalyst.
好ましくは、粒子表面にバナジウム及び Z又はニッケルが 500— 15000質量 ppm 蓄積した FCC平衡触媒であり、バナジウム及び Z又はニッケル蓄積量が 800— 500 0質量 ppmの FCC平衡触媒が特に好まし!/、。 Preferably, vanadium and Z or nickel on the particle surface are 500-15000 mass ppm Particularly preferred are FCC equilibrium catalysts that have accumulated FCC and have a vanadium and / or Z or nickel accumulation of 800-5000 ppm by mass!
また、一般に前記オクタン価の高いガソリンを製造するための流動接触分解装置( FCC装置)においては、 FCC触媒の活性を一定に保っために適時新触媒を添加し ており、この新触媒は装置内にある触媒と完全混合され、触媒の活性は平均化され ることになる。しかしながら、そのままでは装置内の触媒量が過剰になるので、一定量 を常に抜き出している。 Generally, in a fluid catalytic cracking unit (FCC unit) for producing gasoline having a high octane number, a new catalyst is added at appropriate times in order to keep the activity of the FCC catalyst constant. It is completely mixed with a certain catalyst, and the activity of the catalyst will be averaged. However, since the amount of catalyst in the equipment would be excessive if it was not used, a certain amount was always extracted.
[0018] 本発明では、これら吸着粒子を、流動層炉内に予め充填したり、また、流動層炉内 に投入することにより、タールを吸着'分解することができる。 In the present invention, tar can be adsorbed and decomposed by pre-filling these adsorbed particles in a fluidized-bed furnace or charging them into a fluidized-bed furnace.
[0019] また、本発明では、これら吸着粒子を、流動層炉の流動媒体、循環媒体 (循環ソリツ ド)として用いることによつても、タールを吸着'分解することができる。 In the present invention, tar can also be adsorbed and decomposed by using these adsorbed particles as a fluid medium and a circulating medium (circulating solid) of a fluidized bed furnace.
[0020] 本発明では、パブリング型流動層、内部循環型流動層をプロセスとする流動層炉を 用いるときは、これら吸着性粒子を流動媒体として用いることができる。 [0020] In the present invention, when using a fluidized bed furnace that processes a publishing type fluidized bed and an internal circulation type fluidized bed, these adsorptive particles can be used as a fluidized medium.
一方、外部循環型流動層をプロセスとする流動層炉を用いるときは、これら吸着性 粒子を循環媒体として用いることができる。 On the other hand, when a fluidized bed furnace using an external circulation type fluidized bed as a process is used, these adsorptive particles can be used as a circulating medium.
[0021] さらに、本発明では、これら吸着性粒子を、流動層から飛散させることにより、流動 層炉内(例えば、フリーボード部等)でタールを吸着 ·分解することができる。尚、吸着 性粒子を飛散させる際の条件は、流動層や吸着性粒子の種類等に応じて、適宜調 節することができる。 Further, in the present invention, by scattering these adsorptive particles from the fluidized bed, tar can be adsorbed and decomposed in a fluidized bed furnace (for example, a freeboard portion or the like). The conditions for scattering the adsorptive particles can be appropriately adjusted according to the type of the fluidized bed and the adsorptive particles.
[0022] 本発明の方法では、上記原料力 生成するタールを、上記の吸着性粒子に付着さ せて燃焼することにより、タールを除去することができる。付着タールの燃焼は、流動 層炉内の燃焼領域内で行うことができる。 [0022] In the method of the present invention, tar produced by the above-mentioned raw material force is attached to the above-mentioned adsorptive particles and burned, whereby tar can be removed. The combustion of the attached tar can be performed in the combustion zone in the fluidized bed furnace.
[0023] 本発明では、タールを、吸着性粒子を用いて吸着 '分解し、吸着性粒子により分解 されずに残つた付着タールをさらに燃焼することにより、タールの除去を連続的に行う ことができる。本発明では、燃焼領域において、付着タールの燃焼により、吸着性粒 子が再生されるので、これを連続的に使用することができる。 In the present invention, the tar can be continuously removed by adsorbing and decomposing the tar using the adsorptive particles and further burning the adhered tar remaining without being decomposed by the adsorptive particles. it can. In the present invention, since the adsorbable particles are regenerated in the combustion region by the combustion of the attached tar, the adsorbable particles can be used continuously.
本発明の方法は、燃焼熱をガス化熱源として利用することができるので、効率的で ある。また、原料の燃焼により生成するガス化ガスと、タールの燃焼により生成する燃 焼ガスとが分離されて ヽるので、ガス化ガスは高カロリーガスとなる。 The method of the present invention is efficient because the heat of combustion can be used as a gasification heat source. In addition, gasified gas generated by the combustion of raw materials and fuel generated by the combustion of tar Since the combustion gas is separated, the gasification gas becomes a high-calorie gas.
[実施例] [Example]
[0024] 次に、実施例及び比較例により本発明を具体的に示すが、本発明は下記実施例 に限定されるものではない。 Next, the present invention will be specifically described with reference to Examples and Comparative Examples, but the present invention is not limited to the following Examples.
[0025] [実験装置及び方法] [Experimental Apparatus and Method]
図 1に示す実験室規模のパブリング型流動層ガス化炉装置 1を用いた。この装置 1 は、ガス化炉 2、分散盤 4、風箱 6から構成される。この装置 1は、内径 100mm、高さ 1. 5m (分散盤 4上カも炉出口 8まで)の円筒形でステンレス製である。装置 1の外部 には、ガス化温度を制御するための電気炉 10が設置されている。ガス化用ガスとして は、窒素ガスを使用し、 6リットル Z分の流量で、ガス導入部 12から、ガス予熱機能を 持たせたガス予熱機 14、風箱 6、分散盤 4を通してガス化炉 2に供給した。 A lab-type publishing type fluidized-bed gasification furnace 1 shown in FIG. 1 was used. This apparatus 1 is composed of a gasifier 2, a dispersion plate 4, and a wind box 6. This apparatus 1 is cylindrical and made of stainless steel with an inner diameter of 100 mm and a height of 1.5 m (the disperser 4 is also up to the furnace outlet 8). Outside the device 1, an electric furnace 10 for controlling the gasification temperature is installed. Nitrogen gas is used as the gasification gas at a flow rate of 6 liters Z, from the gas inlet 12 through the gas preheater 14 equipped with a gas preheating function, the wind box 6, and the disperser 4, Feeded to 2.
装置 1には予め、分散盤 4上に高さ 150mmの粒子 (粒子 A— E)を流動媒体 16とし て充填した。流動媒体 16は、ガス化炉 2の内部において、分散盤 4を通して供給され たガス用ガスによって流動 ·飛散する。 The apparatus 1 was previously filled with particles (particles A to E) having a height of 150 mm as a fluid medium 16 on a dispersion plate 4. The fluid medium 16 flows and scatters inside the gasification furnace 2 by the gas gas supplied through the dispersion plate 4.
[0026] 外部に設けた電気炉 10で、ガス化炉 2内を所定の温度(600°C、 700°C、 800°C) に加熱した後、装置 1の外部に設けた原料フィーダ一 18と粒子フィーダ一 20からそ れぞれ原料と粒子を定量供給した。ガス化した生成ガスとタールは、ガス化炉上部の 炉出口 8を通って外部へ排出し、その一部を、タール回収装置 22内のタール回収用 の有機溶媒 (ァ-ノール)に導入し、完全に回収した。回収したタールサンプル量を、 GC— FID及び脱溶媒残さ法の組み合わせにより測定した。 After the inside of the gasification furnace 2 is heated to a predetermined temperature (600 ° C., 700 ° C., 800 ° C.) by an electric furnace 10 provided outside, a raw material feeder 18 provided outside the apparatus 1 is heated. The raw material and the particles were supplied quantitatively from the feeder and the particle feeder 20, respectively. The gasified product gas and tar are discharged to the outside through the furnace outlet 8 at the upper part of the gasification furnace, and a part of the gas and tar is introduced into the organic solvent (ethanol) for tar recovery in the tar recovery unit 22. , Completely recovered. The amount of the collected tar sample was measured by a combination of GC-FID and desolvation residue method.
原料としては、木質バイオマス (杉:炭素分 48. 7%、水素分 5. 8%、酸素分 40. 2 %、灰分 0. 4%、水分 4. 9%)を粒径 200— 300 /z mに調整して、流量 5gZ分で供 給した。流動媒体粒子は、全量を粒径 lmm以下に調整し、流量 60gZ分で供給し た。 The raw material is wood biomass (cedar: carbon content 48.7%, hydrogen content 5.8%, oxygen content 40.2%, ash content 0.4%, moisture 4.9%), particle size 200—300 / zm And supplied at a flow rate of 5 gZ. The total amount of the fluid medium particles was adjusted to a particle size of lmm or less and supplied at a flow rate of 60 gZ.
[0027] 流動媒体粒子として、以下の粒子 A— Eを使用した。 [0027] The following particles A to E were used as the fluid medium particles.
粒子 A :油浸造粒法によって製造されたアルミナ粒子 Particle A: Alumina particles produced by the oil immersion granulation method
製造方法: 20Lのステンレス製容器に硫酸アルミニウム水溶液 (AI O : 7. 72% Production method: Aluminum sulfate aqueous solution (AI O: 7.72%) in a 20L stainless steel container
2 3 、 S 2 3, S
O : 18. 20%)を 16kg計りとり、アルミン酸ナトリウム水溶液 (AI O : 23. 80%、 Na 0 : 19. 10%) 4. 28kgを 5Lのステンレス製容器に計量した。 O: 18.20%), weigh 16 kg of sodium aluminate aqueous solution (AI O: 23.80%, Na (0: 19.10%) 4. 28 kg was weighed into a 5 L stainless steel container.
次に、硫酸アルミニウム水溶液の注加速度を約 102mlZmin、アルミン酸ナトリウム 水溶液の注加速度を 23. 3mlZmin、に設定し、高剪断下、定量ポンプで同時混合 した。 Next, the injection rate of the aqueous solution of aluminum sulfate was set to about 102 mlZmin, and the injection rate of the aqueous solution of sodium aluminate was set to 23.3 mlZmin. The mixture was simultaneously mixed with a metering pump under high shear.
さらに、 目標の塩基性硫酸アルミニウムのヒドロゾルのモル比(SO ZA1 O )が 0. 9 Furthermore, the target basic aluminum sulfate hydrosol molar ratio (SO ZA1 O) is 0.9
3 2 3 3 2 3
2となるように高剪断下のもとで混合液の循環系を形成し、そこに、 546gのアルミン 酸ナトリウム水溶液を 2. OmlZminの注加速度で添加混合した。 A circulating system of the mixture was formed under high shear so as to obtain 2, and 546 g of an aqueous solution of sodium aluminate was added thereto and mixed at an injection rate of 2. OmlZmin.
[0028] 尚、循環速度は 800mlZminとし、 7日間室温で攪拌熟成した。最終的に Al O濃 [0028] The circulation speed was 800 ml Zmin, and the mixture was aged at room temperature for 7 days with stirring. Finally Al O concentration
2 3 度 11. 44%, pH3. 97、粘度 180m. pa. s、 70。Cにおけるゲノレイ匕時間力 5分 40禾少 の塩基性硫酸アルミニウムのヒドロゾルを得た。また、塩基性硫酸アルミニウムのヒドロ ゾルのモル比(SO /Al O )は 0. 922であった。 23 degrees 11.44%, pH 3.97, viscosity 180m.pa.s, 70. A Genolei dangling time in C was 5 minutes, and a hydrosol of basic aluminum sulfate of 40 min was obtained. The molar ratio of the basic aluminum sulfate hydrosol (SO 2 / Al 2 O 3) was 0.922.
3 2 3 3 2 3
[0029] 調製された塩基性硫酸アルミニウムのヒドロゾルをさらに室温下で 20日間攪拌熟成 して重合を促進せしめ粘度を上昇させた塩基性硫酸アルミニウムのヒドロゾルを予め 、調製しておいた濃アンモニア一塩ィ匕アンモ-ゥムの pH緩衡溶液 (NH Cl: 70gと濃 [0029] The prepared basic aluminum sulfate hydrosol is further aged for 20 days at room temperature with stirring and aging to promote polymerization and increase the viscosity of the basic aluminum sulfate hydrosol to prepare a concentrated ammonia monosalt in advance. PH buffer solution of ammonium chloride (NH Cl: 70g and concentrated
4 Four
アンモニア水、約 500mlをイオン交換水添カ卩し、全量を 1リットルに調製した緩衡溶 液: pH9. 84)に塩基性アルミニウムのヒドロゾルを注射器で押出し、室温下でヒドロ ゲル化せしめ、円柱状の透明なアルミナヒドロゲルを調製した。水洗、乾燥した後、 6 00°Cで 3時間焼成して透明性を有する活性アルミナ粒子を得た。粒子 Aの結晶状態 (600°C ' 3hr)は非晶質であり、 BET比表面積は 274m2Zg、細孔面積は 0. 37ml / gであつ 7こ。 Approximately 500 ml of aqueous ammonia was ion-exchanged and hydrogenated, and the basic aluminum hydrosol was extruded with a syringe into a buffer solution (pH 9.84), adjusted to a total volume of 1 liter, and hydrogelated at room temperature. A columnar transparent alumina hydrogel was prepared. After washing with water and drying, it was calcined at 600 ° C. for 3 hours to obtain transparent activated alumina particles. The crystalline state of the particle A (600 ° C. for 3 hours) is amorphous, the BET specific surface area is 274 m 2 Zg, and the pore area is 0.37 ml / g.
[0030] 粒子 B :シリカ'アルミナ粒子 (水澤ィ匕学工業 (株)製 ネオビード SA) [0030] Particle B: silica 'alumina particles (Neobead SA manufactured by Mizusawa I-Dagaku Kogyo Co., Ltd.)
[0031] 粒子 C : FCC平衡触媒 [0031] Particle C: FCC equilibrium catalyst
製造方法: FCCの実装置力も抜き出したバナジウム 520質量 ppm及びニッケル 28 0質量 ppmが蓄積されたレニウム置換超安定 Y型ゼオライトを 10質量0 /0、アルミナ 40 質量%、シリカ 30質量%及び粘土鉱物カオリン 20質量%からなるものを用いた。 Production Method: real device forces also withdrawn vanadium 520 ppm by weight and nickel 28 0 mass ppm rhenium accumulated substituted ultrastable Y-type zeolite of 10 mass FCC 0/0, alumina 40 wt%, silica 30 wt% and clay minerals Kaolin consisting of 20% by mass was used.
[0032] 粒子 D:石灰石 (太平洋セメント製、 1mm以下粉砕品) [0032] Particle D: Limestone (made by Taiheiyo Cement, crushed product of 1 mm or less)
粒子 E:粉体造粒法によって製造されたアルミナ粒子 (水澤化学工業 (株)製、 GB) ここで、粉体造粒法とは、ヒドロゲルを乾燥、粉末化した後、押出や流動化によって 成形、造流する方法をいう。 Particle E: Alumina particles manufactured by powder granulation method (GB, manufactured by Mizusawa Chemical Industry Co., Ltd.) Here, the powder granulation method involves drying and pulverizing a hydrogel, followed by extrusion or fluidization. It refers to a method of molding and flowing.
[0033] [タール除去率] [0033] [tar removal rate]
実施例 1一 9、比較例 1一 6 Example 1-9, Comparative Example 1-6
上記の粒子 A— Eを用いたときの、ガス化温度毎のタール除去率を求めた。結果を 表 1に示す。 The tar removal rate at each gasification temperature when using the above particles A to E was determined. Table 1 shows the results.
尚、タール除去率は、タール除去効果の無い砂 (JIS7号)を粒子として用いたときに 発生するタール量を a、各粒子を用いたときのタール量を bとして、次式力も算出した タール除去率 = [ 1 (b/a) ] X 100 (%) The tar removal rate was calculated using the following equation, where a is the amount of tar generated when sand (JIS No. 7) having no tar removal effect is used as particles, and b is the amount of tar when each particle is used. Removal rate = [1 (b / a)] X 100 (%)
[0034] [表 1] [0034] [Table 1]
[0035] [粉化率] [Powder rate]
実施例 10, 11、比較例 7, 8 Examples 10 and 11, Comparative Examples 7 and 8
粒子として、上記粒子 A、粒子 B、粒子 D及び粒子 Eを用いたときの粉ィ匕率を求めた 。結果を表 2に示す。 尚、粉化率は、流動層温度を 800°C、初期粒子充填高さを 150mm、原料のみを 投入する条件で試験を行ったときのガス化時間 1時間後の層内に残った粒子の重量 を d、初期に充填した粒子の重量を eとして、次式力も算出した。 As a particle, the particle ratio was determined when the particles A, B, D and E were used. Table 2 shows the results. In addition, the powdering rate was as follows. The force of the following formula was also calculated, where d is the weight and e is the weight of the particles initially charged.
粉化率 = { l-[d/e] } X 100 (%) Powdering rate = {l- [d / e]} X 100 (%)
[表 2][Table 2]
産業上の利用可能性 Industrial applicability
本発明の方法は、燃料用ガス、化学原料用ガスを生成するシステムを利用するェ ネルギー分野及びィ匕学分野において好適である。 The method of the present invention is suitable for use in a field of energy and a field of research using a system for producing gas for fuel and gas for chemical raw materials.
Claims
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| JP2004092275A JP4505247B2 (en) | 2004-03-26 | 2004-03-26 | Method for removing tar in a fluidized bed furnace |
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| JP2005272782A (en) * | 2004-03-26 | 2005-10-06 | Idemitsu Kosan Co Ltd | Method for removing tar in fluidized bed furnace |
| WO2007064014A1 (en) * | 2005-11-30 | 2007-06-07 | Nippon Oil Corporation | Fuel and method for producing same |
| JP2007153924A (en) * | 2005-11-30 | 2007-06-21 | Nippon Oil Corp | Biomass treatment using fluid catalytic cracking |
| JP2007153925A (en) * | 2005-11-30 | 2007-06-21 | Nippon Oil Corp | Biomass treatment using fluid catalytic cracking |
| JP2007153939A (en) * | 2005-11-30 | 2007-06-21 | Nippon Oil Corp | Liquefied fuel gas composition |
| JP2007177193A (en) * | 2005-11-30 | 2007-07-12 | Nippon Oil Corp | Biomass treatment using fluid catalytic cracking |
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| WO2007064014A1 (en) * | 2005-11-30 | 2007-06-07 | Nippon Oil Corporation | Fuel and method for producing same |
| JP2007153924A (en) * | 2005-11-30 | 2007-06-21 | Nippon Oil Corp | Biomass treatment using fluid catalytic cracking |
| JP2007153925A (en) * | 2005-11-30 | 2007-06-21 | Nippon Oil Corp | Biomass treatment using fluid catalytic cracking |
| JP2007153939A (en) * | 2005-11-30 | 2007-06-21 | Nippon Oil Corp | Liquefied fuel gas composition |
| JP2007177193A (en) * | 2005-11-30 | 2007-07-12 | Nippon Oil Corp | Biomass treatment using fluid catalytic cracking |
| JP7017747B1 (en) | 2021-09-08 | 2022-02-09 | シンエネルギー開発株式会社 | Biomass power generation method, information management method for biomass power generation, biomass power generation system, and sales method for external products of biomass power generation |
| JP2023039168A (en) * | 2021-09-08 | 2023-03-20 | シンエネルギー開発株式会社 | Biomass power generation method, biomass power generation information management method, biomass power generation system, and sales method of biomass power generation external sales product |
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| JP4505247B2 (en) | 2010-07-21 |
| CN1934230A (en) | 2007-03-21 |
| JP2005272782A (en) | 2005-10-06 |
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