WO2011151537A2 - Dispositif de separation de particules pour une boucle de combustion chimique - Google Patents

Dispositif de separation de particules pour une boucle de combustion chimique Download PDF

Info

Publication number
WO2011151537A2
WO2011151537A2 PCT/FR2011/000317 FR2011000317W WO2011151537A2 WO 2011151537 A2 WO2011151537 A2 WO 2011151537A2 FR 2011000317 W FR2011000317 W FR 2011000317W WO 2011151537 A2 WO2011151537 A2 WO 2011151537A2
Authority
WO
WIPO (PCT)
Prior art keywords
particles
separator
gas
enclosure
combustion zone
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Ceased
Application number
PCT/FR2011/000317
Other languages
English (en)
French (fr)
Other versions
WO2011151537A3 (fr
Inventor
Ali Hoteit
Florent Guillou
Sébastien RIFFLART
Thierry Gauthier
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
IFP Energies Nouvelles IFPEN
TotalEnergies SE
Original Assignee
IFP Energies Nouvelles IFPEN
Total SE
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Priority to RU2012156927/06A priority Critical patent/RU2568017C2/ru
Priority to AU2011260164A priority patent/AU2011260164B2/en
Priority to EP11728314.3A priority patent/EP2577163B1/fr
Priority to US13/701,587 priority patent/US9388979B2/en
Priority to CN201180027105.0A priority patent/CN103080649B/zh
Priority to KR1020127034347A priority patent/KR20130109991A/ko
Priority to PL11728314T priority patent/PL2577163T3/pl
Priority to JP2013512961A priority patent/JP2013532268A/ja
Priority to BR112012030797-5A priority patent/BR112012030797B1/pt
Priority to ES11728314T priority patent/ES2748513T3/es
Application filed by IFP Energies Nouvelles IFPEN, Total SE filed Critical IFP Energies Nouvelles IFPEN
Priority to CA2799139A priority patent/CA2799139C/fr
Publication of WO2011151537A2 publication Critical patent/WO2011151537A2/fr
Publication of WO2011151537A3 publication Critical patent/WO2011151537A3/fr
Priority to ZA2012/08629A priority patent/ZA201208629B/en
Anticipated expiration legal-status Critical
Ceased legal-status Critical Current

Links

Classifications

    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23CMETHODS OR APPARATUS FOR COMBUSTION USING FLUID FUEL OR SOLID FUEL SUSPENDED IN  A CARRIER GAS OR AIR 
    • F23C10/00Fluidised bed combustion apparatus
    • F23C10/02Fluidised bed combustion apparatus with means specially adapted for achieving or promoting a circulating movement of particles within the bed or for a recirculation of particles entrained from the bed
    • F23C10/04Fluidised bed combustion apparatus with means specially adapted for achieving or promoting a circulating movement of particles within the bed or for a recirculation of particles entrained from the bed the particles being circulated to a section, e.g. a heat-exchange section or a return duct, at least partially shielded from the combustion zone, before being reintroduced into the combustion zone
    • F23C10/08Fluidised bed combustion apparatus with means specially adapted for achieving or promoting a circulating movement of particles within the bed or for a recirculation of particles entrained from the bed the particles being circulated to a section, e.g. a heat-exchange section or a return duct, at least partially shielded from the combustion zone, before being reintroduced into the combustion zone characterised by the arrangement of separation apparatus, e.g. cyclones, for separating particles from the flue gases
    • F23C10/10Fluidised bed combustion apparatus with means specially adapted for achieving or promoting a circulating movement of particles within the bed or for a recirculation of particles entrained from the bed the particles being circulated to a section, e.g. a heat-exchange section or a return duct, at least partially shielded from the combustion zone, before being reintroduced into the combustion zone characterised by the arrangement of separation apparatus, e.g. cyclones, for separating particles from the flue gases the separation apparatus being located outside the combustion chamber
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D49/00Separating dispersed particles from gases, air or vapours by other methods
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23CMETHODS OR APPARATUS FOR COMBUSTION USING FLUID FUEL OR SOLID FUEL SUSPENDED IN  A CARRIER GAS OR AIR 
    • F23C10/00Fluidised bed combustion apparatus
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23CMETHODS OR APPARATUS FOR COMBUSTION USING FLUID FUEL OR SOLID FUEL SUSPENDED IN  A CARRIER GAS OR AIR 
    • F23C10/00Fluidised bed combustion apparatus
    • F23C10/005Fluidised bed combustion apparatus comprising two or more beds
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23CMETHODS OR APPARATUS FOR COMBUSTION USING FLUID FUEL OR SOLID FUEL SUSPENDED IN  A CARRIER GAS OR AIR 
    • F23C99/00Subject-matter not provided for in other groups of this subclass
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23CMETHODS OR APPARATUS FOR COMBUSTION USING FLUID FUEL OR SOLID FUEL SUSPENDED IN  A CARRIER GAS OR AIR 
    • F23C2900/00Special features of, or arrangements for combustion apparatus using fluid fuels or solid fuels suspended in air; Combustion processes therefor
    • F23C2900/99008Unmixed combustion, i.e. without direct mixing of oxygen gas and fuel, but using the oxygen from a metal oxide, e.g. FeO
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23JREMOVAL OR TREATMENT OF COMBUSTION PRODUCTS OR COMBUSTION RESIDUES; FLUES 
    • F23J2217/00Intercepting solids
    • F23J2217/60Intercepting solids using settling/precipitation chambers
    • YGENERAL 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
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02EREDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
    • Y02E20/00Combustion technologies with mitigation potential
    • Y02E20/34Indirect CO2mitigation, i.e. by acting on non CO2directly related matters of the process, e.g. pre-heating or heat recovery

Definitions

  • the field of the invention is that of the separation of particles, and more specifically metal oxide particles, on the one hand, and unburnt particles possibly associated with fly ash, on the other hand, in the context chemical loop combustion to produce energy, synthesis gas and / or hydrogen.
  • the chemical looping combustion (abbreviation CLC for Chemical Looping Combustion) consists of bringing into contact, in a high-temperature chamber, a gaseous, liquid and / or solid hydrocarbon feedstock with a solid of the metal oxide and oxygen-carrying type.
  • the metal oxide gives up some of the oxygen it contains, the latter participating in the combustion of hydrocarbons.
  • the fumes mainly contain carbon oxides, water and possibly hydrogen. Indeed, it is not necessary to put the hydrocarbon feedstock in contact with air and the fumes are therefore mainly composed of combustion gases and possibly a dilution gas used for transporting and fluidizing the particles or a gas (for example water vapor) promoting the gasification of solid fuel.
  • the patent application FR 2,850,156 describes a chemical loop combustion process for which the fuel is ground before entering the reduction reactor operating in a circulating fluidized bed.
  • the small size of the solid fuel particles allows a more complete and faster combustion.
  • the downstream separation of the circulating bed is first provided by a cyclone and then by a device for separating the unburnt particles from the metal oxide particles. Thus, it avoids the entrainment of unburnt in the oxidation zone and thus the CO 2 emissions in the effluents of the oxidation reactor.
  • the separation device is fluidized by water vapor, which separates the fine and light particles, such as the carbonaceous residue, and reintroduces the latter into the reactor, while the denser and larger particles of oxides are transferred to the oxidation reactor.
  • the patent application FR 2 896 709 relates to a particle separator operating in a chemical loop process.
  • This separator is fed by the flow of particles carrying the oxygen and mixed with the solid fuel.
  • the particles flow in a dense phase following a tortuous path and passing through baffles, which makes it possible to control the residence time and to promote the separation of the light particles (unburnt particles) from the particles. heavy (metal oxides).
  • the particles are then introduced into a fluidization zone, said fluidization being controlled by means located at the base of the separator but also at the wall of the baffles, which makes it possible to entrain the lighter particles which are then recycled to the reactor. fluidization.
  • the separation efficiency is reduced in view of a limitation in the driving capacity of the particles in the gas phase. Indeed, to drive large quantities of particles, it is necessary to implement large amounts of gas and free sections.
  • the geometry of the FR 2 896 709 separator is very complicated by the presence of internals, in particular asymmetrical internals. This geometry is problematic given the mechanical stresses experienced by the materials constituting the separator under the temperature conditions of the CLC process, generally above 800 ° C. Indeed, if the outer walls are often protected by a refractory cement and remain at low temperature, this is not the case of internal walls that are brought to the conditions of the process.
  • Applicants have developed a novel separator wherein the mixture of particles from the combustion zone is contacted with a gas stream from the combustion zone and / or an external gas source. This mixture then enters the dilute phase of the separator. In the separator, the velocity of the gas flow is controlled so as to allow sedimentation of the heavier particles (essentially metal oxide particles), the lighter particles (essentially unburnt particles) being drawn towards the top of the separator to be recycled to the combustion zone.
  • the separator according to the invention has an improved efficiency of separation of unburnt particles and particles of metal oxides.
  • the present invention relates to a chemical loop combustion device using a solid fuel generating unburnt particles and implementing oxygen carrier particles, such as metal oxides, and comprising at least one zone of combustion and separator of particles contained in a gas mixture from said combustion zone, wherein the separator comprises an enclosure with at least one intake pipe of said mixture, an exhaust pipe located in the lower part of the enclosure and a pipe outlet located in the upper part of the device, the inlet and outlet / outlet parameters being chosen to create in the enclosure a dense phase in the lower part and a diluted phase in the upper part, and wherein said intake pipe opens in the diluted phase.
  • the separator enclosure may further include a supply line for a gas from an external source.
  • the outlet pipe may be connected to a gas-solid separator for evacuating a gas depleted of unburnt particles by a pipe, and recycling the unburnt particles via a communication pipe with the combustion zone.
  • the intake pipe can enter the chamber substantially axially and with a length of between 1 and 5 times the diameter of the chamber.
  • the intake pipe can penetrate through the lower part of the enclosure.
  • the lower part of the enclosure may comprise an annular space between the outer wall of the intake pipe and the wall of the separator.
  • the combustion zone may comprise at least one solid feed line, an oxygen carrier particle feed line, a fluidization gas feed line, to form said gas mixture.
  • the invention also relates to a chemical loop combustion method using a solid fuel generating unburnt particles and implementing oxygen carrier particles, such as metal oxides, and comprising at least one combustion zone and one combustion zone.
  • particle separator contained in a gas mixture from the combustion zone, a method according to which a mixture of particles and gas is admitted into the separator enclosure, the particles are extracted by an outlet at the top of the enclosure and a evacuation in the lower part of this chamber, the intake and extraction parameters being chosen to create in the chamber a lower dense phase and an upper dilute phase, dilute phase in which said mixture is admitted.
  • the separator enclosure may be powered by a gas from an external source.
  • the superficial velocity of the gas in the dilute phase of the chamber of the device can be set at a value between 30 and 300% of the average terminal rate of drop of the oxygen carrier particles.
  • the superficial velocity of the gas in the dilute phase of the chamber of the device can be set at a value between 75 and 125% of the average terminal rate of drop of the oxygen carrier particles.
  • the gas velocity in the upper part of the combustion zone can be between 3 and 10 m / s.
  • the separator can be placed above the combustion zone.
  • the enclosure may be powered by a gas from an external source representing less than 20% of the total gas flow in the separator.
  • the combustion zone can operate in a dense phase fluidized bed, the particles of which are transported to the separator, the transport being controlled by an L-shaped valve.
  • the combustion zone can operate in a dense phase fluidized bed, the particles of which are transported to the separator through a gas / solid separator at the exit of which the particles flow inside the separator.
  • FIGS. 1 to 5 represent, solely by way of example and in a nonlimiting manner, various implementations and integration of the device according to the invention at the exit of a combustion zone. a CLC unit.
  • FIG. 5 illustrates a particular geometry of the device according to the invention.
  • Figure 1 describes the invention integrated in a global scheme.
  • Zone (2) represents the combustion zone of a chemical looping combustion process (CLC) in which a solid charge is introduced via a pipe (7), particles of oxygen carrier via a pipe (8) from the oxidation zone (not shown) of the CLC process and a fluidization gas supplied by a pipe (17) such as, for example, steam or water.
  • CLC chemical looping combustion process
  • the solid charge (or fuel) treated in the combustion zone is generally composed of a hydrocarbon solid source containing predominantly carbon and hydrogen.
  • the filler is advantageously selected from coal, coke, petcoke, biomass, oil sands and household waste.
  • This combustion zone (2) can operate in a fluidized bed in dense phase or circulating fluidized bed or in a bed arrangement consisting of a dense phase and a transport phase.
  • the gas velocity in the upper part of the combustion zone is between 3 and 10 m / s.
  • a flow of particles containing particles of metal oxides, called heavy particles, and light particles comprising unburnt particles and possibly fly ash, all in a gas stream is extracted from the zone (2) to be is then introduced into a separator (1) by an intake pipe (4).
  • the gaseous flow comes wholly or partly from the combustion zone (2) and consists mainly of CO, CO 2 , H 2 and H 2 O, the complement may come from an external source containing, for example, recycled CO 2 and / or water vapor, introduced through the conduit (11) in the lower part of the separator (1).
  • all the off-gases used for combustion are used for the separation and, very preferably, it consists of at least 80% of the effluents from the combustion zone.
  • this cyclone is to separate the unburned gas into unburnt particles which is then extracted via a pipe (10) and the unburnt particles entrained with the metal oxide particles extracted by a pipe (9) and recycled to the combustion zone (2).
  • the heavy particles extracted in the lower part of the separator consist mainly of metal oxides and can be sent to a second combustion zone in which the oxygen carrier will be reduced, or to an oxidation zone allowing the oxygen carrier recovering at least a part of the oxidation state that it had at the entrance to the combustion zone (2) and the lighter unburned particles are recycled to the combustion zone, after separation of the gaseous effluent .
  • the inlet and outlet / outlet parameters are chosen so as to create a dense phase in the enclosure in the lower part and a diluted phase in the upper part, and the intake pipe (4) opens into the dilute phase.
  • the particles that sediment in the lower part form a dense phase consisting of the heavier particles, of greater or lesser height in the separator, depending, among other things, on the density of the particles, the feed and extraction rates, but the level of said dense phase, forming the interface with the dilute phase, is in all cases located below the inlet (4) opening into the separator for the introduction of the mixture of particles extracted from the combustion zone.
  • rapid separation is meant a separation taking place in less than 1 minute and preferably in less than 20 seconds, this time corresponding to the residence time of the light particles in the dilute phase of the separator.
  • the dilute phase generally has a solids content of less than 5%, or even less than 1% vol.
  • X amount of unburnt particles entrained with the gas / total amount of unburnt particles in the mixture of particles entering the separator
  • the superficial velocity of the flow in the separation zone must be greater than the final rate of fall of the unburnt fuel particles to allow their entrainment with the gas.
  • the superficial gas velocity in the dilute phase of the separation zone is set at a value generally comprised between 30 and 300% of the average terminal rate of drop of the oxygen carrier particles, preferably between 75 and 125%.
  • the particle flow entrained in the dilute phase of the separator remains less than 5 kg / s / m2, preferably less than 1 kg / s / m2.
  • Vt ( 4d p ⁇ p - P g ) g ) 1/2 where: dp is the average particle diameter
  • p s is the density of the particles (kg / m 3 )
  • p g is the density of the gas (kg / m 3 )
  • the geometry of the separator may be parallelepipedal, cylindrical or any other three-dimensional geometry and preferably it has a symmetry of revolution.
  • the material used to make the enclosure of the separator may be selected from special steels such as Phastelloy or even ceramics.
  • the outlet of the pipe (4) enters the enclosure on an axial depth preferably between 1 to 5 times the diameter of the enclosure, preferably from 1 to 2 times the diameter of the enclosure.
  • the height of the enclosure available above the outlet of the intake pipe (4) in the enclosure is generally between 1, 5 to 10 times the diameter of the enclosure.
  • the metal oxide particles such as, for example, oxides of Fe, Ti, Ni, Cu, Mn, Co, V, are used alone or as a mixture, and have an average size generally greater than 50 microns, preferably between 100 and 500 microns.
  • the metal oxides, synthetic or mineral, supported or not, generally have a density greater than 1500 kg / m 3 .
  • the nickel oxide particles supported on alumina generally have a grain density of between 2500 and 3500 kg / m 3 depending on the porosity of the support and the oxide content.
  • nickel typically about 3200 kg / m 3 .
  • Ilmenite a combination of titanium and iron, has a density of 4700 kg / m 3 .
  • the separation device according to the present invention is advantageously used for separating unburnt particles from metal oxide particles having a density greater than 2500 kg / m 3 , preferably greater than 4000 kg / m 3.
  • Oxygen carrier particles are generally much larger in size and density than fly ash and unburnt particles that have previously been in contact with the oxygen carrying particles in the high temperature combustion zone. At the outlet of the combustion zone, it is estimated that the size of the unburned coal particles is less than 100 microns and that the majority of the particles are less than 50 microns in size. The density of these particles is generally between 1000 and 1500 kg / m 3 .
  • Figure 2 differs from Figure 1 in that the intake duct (4) opens axially directly into the separator (1) which is placed above the combustion zone (2).
  • the upper part of the combustion zone is narrowed, which makes it possible to accelerate and transport the gas-particle mixture leaving the combustion zone, and comprising combustion fumes, unburnt particles and possibly fly ash.
  • the gas velocity in the upper part of the combustion zone is preferably between 3 and 10 m / s and the flow of particles transported in this part is between 25 and 500 kg / s / m 2 , preferably between 60 and 300 kg / s / m 2 .
  • the conduit (4) opens into the separator in a dilute phase consisting essentially of gas (at least 95% by volume). Due to the imposed velocity of the gas in the separator (1), the heavy particles sediment in the lower part of the separator and are extracted by the pipe (5), while the light particles are entrained in the upper part of the separator (1). and are evacuated by the pipe (6).
  • the flow of light particles entrained relative to the section of the separator (1) is less than 5 kg / s / m 2 , is generally between 0.02 and 1.0 kg / s / m 2 and contains at least 50% of the unburnt particles from the combustion zone (2).
  • the fluidization of the dense phase is performed by adding a gas external to the combustion zone by a conduit (11).
  • This gas passes through the separation zone (1) and advantageously participates in the physical separation process of the particles before leaving the separator via the pipe (6).
  • FIG. 3 differs from FIG. 2 in that the combustion zone (2) in which the solid charge introduced by the pipe (7) is burned in contact with the oxygen carrier particles brought by a pipe (8) in a fluidized bed in dense phase, the fluidization being operated through the introduction of a gas supplied by a pipe (17) and containing for example water vapor and / or carbon dioxide.
  • the combustion fumes are discharged from the combustion zone (2) through a conduit (15) located in the upper portion of the fluidized bed of this zone.
  • the particles are withdrawn into the dense phase of the fluidized bed and transported independently of the combustion fumes in lines (4) and (4 ') to the separation zone (1).
  • the transport means represented by the pipes (4) and (4 ') include, for example, a device for drawing off in a dense phase, a vertical tube in which the particles flow downwards, a non-mechanical valve, such as a valve in L, for controlling the flow rate of particles by controlled injection of an insufflation gas upstream of a bend in a transport lift in which a gas external to the combustion zone (2) is injected to transport the particles.
  • the particles therefore arrive in the separator (1) in the presence of a gas allowing their upward transport.
  • the gas-particle mixture originating from the combustion zone (2) opens into the separator (1) through the end of the pipe (4 ') in a dilute phase consisting essentially of gases (at least 95% by volume) in which the superficial velocity is controlled by adding gas through the pipe (11).
  • the adjustment of the superficial velocity in the separator (1) makes it possible to control the quantity of particles entrained towards the outlet (6). Particles not entrained towards this outlet (6) sediment in the dense phase of the separator (1) and are collected in the lower part of the separator (1) and discharged via a pipe (5) to another reaction zone.
  • FIG. 4 describes another embodiment of the invention, which differs from that of FIG. 3 in that the particles entering the separator (1) are introduced from a downcomer (4 ") in which the particles arrive in a descending transport mode in dense phase, the movement of the particles depending on the gravity and not on the speed of the surrounding gas.
  • a prior separation of the mixture transported in the intake duct (4) is carried out, for example in a gas-solid separator (12).
  • the solid particles then flow through the pipe (4 ") inside the separator (1) and are distributed over the entire section of the separator (1) through a deflector (14), such as for example a" hat “ Chinese “, with a hollow cone of larger section than the duct (4").
  • a deflector such as for example a" hat “ Chinese ", with a hollow cone of larger section than the duct (4"). Due to this new mode of introduction, the gas involved in the separation of the particles in the separator (1) is introduced substantially at the base of the chamber by a conduit (11), the interstitial gas introduced through the conduit.
  • FIG. 5 describes a particular geometry of the device according to the invention, which comprises in its lower part a circular recess or annular space (200) between the wall of the pipe (4) opening into the dilute phase and the outer wall (300) of the smaller diameter separator, whereby all the surfaces of the device have an outer face, which can be easily cooled, and it is possible to coat all internal surfaces with a refractory cement (100). Under these conditions, the outer walls are no longer exposed to high temperature levels and are protected from contact with gas and particle currents.
  • the tests to quantify the performance of the device according to the invention were conducted on a cold model simulating the flows.
  • the model includes a transport tube with an internal diameter of 2 cm, in which the particles are transported by air under ambient conditions, the air simulating the combustion fumes.
  • the transport tube opens into the dilute phase of a cylindrical separation chamber of constant section (internal diameter of 12.5 cm).
  • the tube enters the chamber to a depth of 20 cm, which leaves a height of 80 cm above the outlet of the conduit in the diluted phase to effect the separation.
  • the separation chamber is equipped at its base with a gas distribution box for fluidizing the particles around the transport conduit. The level of the fluidized dense phase is maintained under the outlet of the transport conduit opening into the separation chamber.
  • Vsg The superficial velocity of the gas in the dilute phase above the outlet of the transport tube.
  • the gas velocity in the transport tube is equal to 3m s.
  • the flow of solids circulating in the transport tube, feeding the separation zone is equal to 140 kg / h, which corresponds to a flow of 123 kg / s / m 2 .
  • the mass concentration of light particles in all the particles entering the separator is called Cl.
  • Oxygen carrier particles consisting of a heavy ore of iron and titanium (ilmenite), whose properties are as follows:
  • FCC catalyst particles smaller and less dense, simulating coke particles or unburned carbon at process conditions, the properties of which are as follows:
  • the separation efficiency is important.
  • the gas velocity in the dilute phase is 1, 0 or 1, 1 m / s, the recovery efficiency of the light particles can be greater than 70%.

Landscapes

  • Engineering & Computer Science (AREA)
  • Chemical & Material Sciences (AREA)
  • Combustion & Propulsion (AREA)
  • Mechanical Engineering (AREA)
  • General Engineering & Computer Science (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Fluidized-Bed Combustion And Resonant Combustion (AREA)
  • Solid-Fuel Combustion (AREA)
  • Combined Means For Separation Of Solids (AREA)
  • Filtering Of Dispersed Particles In Gases (AREA)
PCT/FR2011/000317 2010-06-02 2011-05-27 Dispositif de separation de particules pour une boucle de combustion chimique Ceased WO2011151537A2 (fr)

Priority Applications (12)

Application Number Priority Date Filing Date Title
BR112012030797-5A BR112012030797B1 (pt) 2010-06-02 2011-05-27 Dispositivo de separaqao de particulas para um circuito de combustao quimica
EP11728314.3A EP2577163B1 (fr) 2010-06-02 2011-05-27 Dispositif de séparation de particules pour une boucle de combustion chimique
US13/701,587 US9388979B2 (en) 2010-06-02 2011-05-27 Particle separation device for a chemical-looping combustion loop
CN201180027105.0A CN103080649B (zh) 2010-06-02 2011-05-27 用于化学回路燃烧回路的颗粒分离装置
KR1020127034347A KR20130109991A (ko) 2010-06-02 2011-05-27 화학적 순환식 연소 루프용 입자 분리 장치
PL11728314T PL2577163T3 (pl) 2010-06-02 2011-05-27 Urządzenie do oddzielania cząstek do spalania w pętli chemicznej
JP2013512961A JP2013532268A (ja) 2010-06-02 2011-05-27 ケミカルルーピング燃焼のループのための粒子分離装置
RU2012156927/06A RU2568017C2 (ru) 2010-06-02 2011-05-27 Устройство разделения частич для химического контура сжигания
AU2011260164A AU2011260164B2 (en) 2010-06-02 2011-05-27 Particle separation device for chemical looping combustion loop
ES11728314T ES2748513T3 (es) 2010-06-02 2011-05-27 Dispositivo de separación de partículas para una combustión en bucle químico
CA2799139A CA2799139C (fr) 2010-06-02 2011-05-27 Dispositif de separation de particules pour une boucle de combustion chimique
ZA2012/08629A ZA201208629B (en) 2010-06-02 2012-11-15 Particle seaparation device for chemical looping combustion loop

Applications Claiming Priority (2)

Application Number Priority Date Filing Date Title
FR1002326A FR2960941B1 (fr) 2010-06-02 2010-06-02 Dispositif de separation de particules pour une boucle de combustion chimique
FR1002326 2010-06-02

Publications (2)

Publication Number Publication Date
WO2011151537A2 true WO2011151537A2 (fr) 2011-12-08
WO2011151537A3 WO2011151537A3 (fr) 2012-01-26

Family

ID=43568210

Family Applications (1)

Application Number Title Priority Date Filing Date
PCT/FR2011/000317 Ceased WO2011151537A2 (fr) 2010-06-02 2011-05-27 Dispositif de separation de particules pour une boucle de combustion chimique

Country Status (14)

Country Link
US (1) US9388979B2 (https=)
EP (1) EP2577163B1 (https=)
JP (1) JP2013532268A (https=)
KR (1) KR20130109991A (https=)
CN (1) CN103080649B (https=)
AU (1) AU2011260164B2 (https=)
BR (1) BR112012030797B1 (https=)
CA (1) CA2799139C (https=)
ES (1) ES2748513T3 (https=)
FR (1) FR2960941B1 (https=)
PL (1) PL2577163T3 (https=)
RU (1) RU2568017C2 (https=)
WO (1) WO2011151537A2 (https=)
ZA (1) ZA201208629B (https=)

Cited By (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN106238443A (zh) * 2016-09-22 2016-12-21 新奥科技发展有限公司 一种二旋飞灰的处理方法
WO2017013038A1 (fr) 2015-07-21 2017-01-26 IFP Energies Nouvelles Procede et installation clc avec production d'azote de haute purete
FR3084138A1 (fr) 2018-07-23 2020-01-24 IFP Energies Nouvelles Installation clc comportant un separateur solide/solide avec des moyens de dispersion d'un melange gaz-solide
WO2020058141A1 (fr) 2018-09-20 2020-03-26 IFP Energies Nouvelles Dispositif et procede de combustion en boucle chimique avec separateur de particules muni d'une conduite d'admission inclinee
FR3089828A1 (fr) 2018-12-17 2020-06-19 IFP Energies Nouvelles Installation clc comportant un separateur solide/solide integrant une enceinte cyclonique
FR3089827A1 (fr) 2018-12-17 2020-06-19 IFP Energies Nouvelles Réacteur de combustion en boucle chimique à toit plat

Families Citing this family (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
FR2936301B1 (fr) * 2008-09-23 2010-09-10 Inst Francais Du Petrole Procede et dispositif optimises de combustion par boucle chimique sur des charges hydrocarbonees liquides
US9740214B2 (en) 2012-07-23 2017-08-22 General Electric Technology Gmbh Nonlinear model predictive control for chemical looping process
FR3007104B1 (fr) 2013-06-13 2019-01-25 IFP Energies Nouvelles Procede et installation de combustion par oxydo-reduction en boucle chimique d'une charge hydrocarbonee solide
US20150343416A1 (en) 2014-06-03 2015-12-03 Saudi Arabian Oil Company Activation of Waste Metal Oxide as an Oxygen Carrier for Chemical Looping Combustion Applications
KR102628156B1 (ko) * 2016-05-02 2024-01-25 엘지전자 주식회사 미세입자 집속장치 및 그의 동작 방법
CN111545042B (zh) * 2020-05-12 2022-07-12 江苏峰峰鸿运环保科技发展有限公司 一种烟气半干法脱硫装置及方法
RU2754712C1 (ru) * 2021-02-03 2021-09-06 Федеральное государственное бюджетное учреждение науки Институт химии твердого тела Уральского отделения Российской акдемии наук Реактор с псевдоожиженным слоем для сжигания топлива в химической петле
FR3166687A1 (fr) * 2024-09-20 2026-03-27 IFP Energies Nouvelles Procede de combustion en boucle chimique d'un combustible comprenant une forte teneur en volatiles

Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
FR2850156A1 (fr) 2003-01-16 2004-07-23 Alstom Switzerland Ltd Installation de combustion avec recuperation de co2
FR2896709A1 (fr) 2006-02-02 2007-08-03 Alstom Technology Ltd Separateur de solides en particulier pour installation de combustion

Family Cites Families (22)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
DE2524540C2 (de) * 1975-06-03 1986-04-24 Metallgesellschaft Ag, 6000 Frankfurt Verfahren zur Durchführung endothermer Prozesse
SU877226A1 (ru) * 1978-08-28 1981-10-30 Ордена Трудового Красного Знамени Институт Тепло-И Массообмена Им. А.В.Лыкова Горелка
JPS56916A (en) * 1979-06-15 1981-01-08 Hokkaido Togyo Kk Method and apparatus for generating hot blast for incineration of chaff
FR2556983B1 (fr) * 1983-12-23 1986-05-16 Creusot Loire Procede et installation de traitement de matieres en lit fluidise, en particulier pour la combustion ou gazeification de matiere combustible
JPH0324971Y2 (https=) * 1985-06-13 1991-05-30
DK158531C (da) * 1985-06-13 1990-10-29 Aalborg Vaerft As Fremgangsmaade til kontinuerlig drift af en cirkulerende fluidiseret bed-reaktor samt reaktor til anvendelse ved udoevelse af fremgangsmaaden
JPH0830566B2 (ja) * 1987-09-22 1996-03-27 三井造船株式会社 循環型流動層ボイラ
US4829912A (en) * 1988-07-14 1989-05-16 Foster Wheeler Energy Corporation Method for controlling the particulate size distributions of the solids inventory in a circulating fluidized bed reactor
SU1751599A1 (ru) * 1989-09-27 1992-07-30 Институт химии и химической технологии СО АН СССР Способ розжига топки с кип щим слоем
DE4007635C1 (https=) * 1990-03-10 1991-09-19 Vereinigte Kesselwerke Ag, 4000 Duesseldorf, De
JP2592176B2 (ja) 1990-08-14 1997-03-19 三菱重工業株式会社 多段圧延機のロール支持構造
US5346631A (en) * 1992-12-07 1994-09-13 Exxon Research & Engineering Co. Phase separator
JPH1079504A (ja) * 1996-09-05 1998-03-24 Sony Corp 量子細線デバイス及びその製造方法
AU2002212765A1 (en) 2000-11-14 2002-05-27 Nippon Soda Co., Ltd. Ion-conductive material containing combined low-molecular compound having hydrogen bond part
US7767191B2 (en) * 2003-12-11 2010-08-03 The Ohio State University Combustion looping using composite oxygen carriers
JP2005299938A (ja) * 2004-04-06 2005-10-27 Mitsubishi Heavy Ind Ltd 循環流動炉
JP2006223961A (ja) * 2005-02-16 2006-08-31 Babcock Hitachi Kk 流動層によるチャー・不燃物分離方法
FR2895413B1 (fr) 2005-12-27 2011-07-29 Alstom Technology Ltd Installation de conversion d'hydrocarbures petroliers a installation de combustion integree comprenant une capture du dioxyde de carbone
DE112007000518A5 (de) 2006-03-16 2009-01-22 Alstom Technology Ltd. Anlage zur Erzeugung von Elektrizität
US8160730B2 (en) * 2008-03-03 2012-04-17 Xinsheng Lou Fuzzy logic control and optimization system
ES2483723T3 (es) * 2008-04-01 2014-08-07 Alstom Technology Ltd Procedimiento para usar una instalación para quemar materiales carbonosos e instalación relacionada
AT509586B8 (de) * 2010-06-11 2011-12-15 Univ Wien Tech Verbessertes wirbelschichtreaktorsystem

Patent Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
FR2850156A1 (fr) 2003-01-16 2004-07-23 Alstom Switzerland Ltd Installation de combustion avec recuperation de co2
FR2896709A1 (fr) 2006-02-02 2007-08-03 Alstom Technology Ltd Separateur de solides en particulier pour installation de combustion

Cited By (11)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2017013038A1 (fr) 2015-07-21 2017-01-26 IFP Energies Nouvelles Procede et installation clc avec production d'azote de haute purete
CN106238443A (zh) * 2016-09-22 2016-12-21 新奥科技发展有限公司 一种二旋飞灰的处理方法
FR3084138A1 (fr) 2018-07-23 2020-01-24 IFP Energies Nouvelles Installation clc comportant un separateur solide/solide avec des moyens de dispersion d'un melange gaz-solide
WO2020020739A1 (fr) 2018-07-23 2020-01-30 IFP Energies Nouvelles Installation clc comportant un separateur solide/solide avec des moyens de repartition d'un melange gaz-solide
US11885488B2 (en) 2018-07-23 2024-01-30 IFP Energies Nouvelles CLC facility comprising a solid/solid separator with means for distributing a gas-solid mixture
WO2020058141A1 (fr) 2018-09-20 2020-03-26 IFP Energies Nouvelles Dispositif et procede de combustion en boucle chimique avec separateur de particules muni d'une conduite d'admission inclinee
FR3086369A1 (fr) 2018-09-20 2020-03-27 IFP Energies Nouvelles Dispositif et procede de combustion en boucle chimique avec separateur de particules muni d'une conduite d'admission inclinee
FR3089828A1 (fr) 2018-12-17 2020-06-19 IFP Energies Nouvelles Installation clc comportant un separateur solide/solide integrant une enceinte cyclonique
FR3089827A1 (fr) 2018-12-17 2020-06-19 IFP Energies Nouvelles Réacteur de combustion en boucle chimique à toit plat
WO2020126703A1 (fr) 2018-12-17 2020-06-25 IFP Energies Nouvelles Installation clc comportant un separateur solide/solide integrant une enceinte cyclonique
WO2020126704A1 (fr) 2018-12-17 2020-06-25 IFP Energies Nouvelles Réacteur de combustion en boucle chimique à toit plat

Also Published As

Publication number Publication date
CN103080649B (zh) 2015-09-30
FR2960941A1 (fr) 2011-12-09
BR112012030797A2 (pt) 2016-11-01
US20130118957A1 (en) 2013-05-16
WO2011151537A3 (fr) 2012-01-26
JP2013532268A (ja) 2013-08-15
RU2012156927A (ru) 2014-07-20
ES2748513T3 (es) 2020-03-17
ZA201208629B (en) 2013-09-25
KR20130109991A (ko) 2013-10-08
BR112012030797A8 (pt) 2019-01-22
US9388979B2 (en) 2016-07-12
CA2799139C (fr) 2019-01-15
BR112012030797B1 (pt) 2020-11-17
PL2577163T3 (pl) 2020-03-31
EP2577163B1 (fr) 2019-07-10
FR2960941B1 (fr) 2014-11-14
RU2568017C2 (ru) 2015-11-10
CA2799139A1 (fr) 2011-12-08
CN103080649A (zh) 2013-05-01
AU2011260164A1 (en) 2013-01-10
AU2011260164B2 (en) 2016-06-09
EP2577163A2 (fr) 2013-04-10

Similar Documents

Publication Publication Date Title
EP2577163B1 (fr) Dispositif de séparation de particules pour une boucle de combustion chimique
CA2799133C (fr) Procede de combustion en boucle chimique avec une zone de reaction integrant une zone de separation gaz-solide et installation utilisant un tel procede
CA2846993C (fr) Procede de combustion en boucle chimique avec elimination des cendres et fines dans la zone de reduction et installation utilisant un tel procede
CA2737105C (fr) Procede et dispositif optimises de combustion par boucle chimique sur des charges hydrocarbonees liquides
CA2850612A1 (fr) Procede de combustion en boucle chimique avec elimination des cendres et fines en sortie de la zone d'oxydation et installation utilisant un tel procede
FR2983489A1 (fr) Procede de combustion en boucle chimique avec elimination en phase diluee des cendres et finess dans la zone d'oxydation et installation utilisant un tel procede
WO2020126704A1 (fr) Réacteur de combustion en boucle chimique à toit plat
EP3827201B1 (fr) Installation clc comportant un separateur solide/solide avec des moyens de repartition d'un melange gaz-solide
EP4449018B1 (fr) Installation et procede de combustion en boucle comportant un reacteur air cyclonique
EP3853525B1 (fr) Dispositif et procede de combustion en boucle chimique avec separateur de particules muni d'une conduite d'admission inclinee
WO2020126703A1 (fr) Installation clc comportant un separateur solide/solide integrant une enceinte cyclonique
CA3238175A1 (fr) Cyclone pour une installation et un procede de combustion en boucle chimique muni d'une conduite d'arrivee a parois inclinees et injection de gaz

Legal Events

Date Code Title Description
WWE Wipo information: entry into national phase

Ref document number: 201180027105.0

Country of ref document: CN

121 Ep: the epo has been informed by wipo that ep was designated in this application

Ref document number: 11728314

Country of ref document: EP

Kind code of ref document: A2

ENP Entry into the national phase

Ref document number: 2799139

Country of ref document: CA

WWE Wipo information: entry into national phase

Ref document number: 2011728314

Country of ref document: EP

ENP Entry into the national phase

Ref document number: 2013512961

Country of ref document: JP

Kind code of ref document: A

NENP Non-entry into the national phase

Ref country code: DE

WWE Wipo information: entry into national phase

Ref document number: 10827/CHENP/2012

Country of ref document: IN

ENP Entry into the national phase

Ref document number: 20127034347

Country of ref document: KR

Kind code of ref document: A

ENP Entry into the national phase

Ref document number: 2012156927

Country of ref document: RU

Kind code of ref document: A

ENP Entry into the national phase

Ref document number: 2011260164

Country of ref document: AU

Date of ref document: 20110527

Kind code of ref document: A

WWE Wipo information: entry into national phase

Ref document number: 13701587

Country of ref document: US

REG Reference to national code

Ref country code: BR

Ref legal event code: B01A

Ref document number: 112012030797

Country of ref document: BR

ENP Entry into the national phase

Ref document number: 112012030797

Country of ref document: BR

Kind code of ref document: A2

Effective date: 20121203