US20130312328A1 - Method and apparatus for particle recycling in multiphase chemical reactors - Google Patents

Method and apparatus for particle recycling in multiphase chemical reactors Download PDF

Info

Publication number
US20130312328A1
US20130312328A1 US13/990,042 US201113990042A US2013312328A1 US 20130312328 A1 US20130312328 A1 US 20130312328A1 US 201113990042 A US201113990042 A US 201113990042A US 2013312328 A1 US2013312328 A1 US 2013312328A1
Authority
US
United States
Prior art keywords
mcr
fluidized bed
high temperature
ash particles
fly ash
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.)
Abandoned
Application number
US13/990,042
Inventor
Chunfa Xu
Long Wu
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.)
Synthesis Energy Systems Inc
Original Assignee
Synthesis Energy Systems Inc
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
Application filed by Synthesis Energy Systems Inc filed Critical Synthesis Energy Systems Inc
Publication of US20130312328A1 publication Critical patent/US20130312328A1/en
Assigned to SYNTHESIS ENERGY SYSTEMS, INC. reassignment SYNTHESIS ENERGY SYSTEMS, INC. ASSIGNMENT OF ASSIGNORS INTEREST (SEE DOCUMENT FOR DETAILS). Assignors: WU, LONG, XU, CHUNFA
Abandoned legal-status Critical Current

Links

Images

Classifications

    • CCHEMISTRY; METALLURGY
    • C10PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
    • C10JPRODUCTION OF PRODUCER GAS, WATER-GAS, SYNTHESIS GAS FROM SOLID CARBONACEOUS MATERIAL, OR MIXTURES CONTAINING THESE GASES; CARBURETTING AIR OR OTHER GASES
    • C10J3/00Production of combustible gases containing carbon monoxide from solid carbonaceous fuels
    • C10J3/72Other features
    • C10J3/82Gas withdrawal means
    • C10J3/84Gas withdrawal means with means for removing dust or tar from the gas
    • CCHEMISTRY; METALLURGY
    • C10PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
    • C10JPRODUCTION OF PRODUCER GAS, WATER-GAS, SYNTHESIS GAS FROM SOLID CARBONACEOUS MATERIAL, OR MIXTURES CONTAINING THESE GASES; CARBURETTING AIR OR OTHER GASES
    • C10J3/00Production of combustible gases containing carbon monoxide from solid carbonaceous fuels
    • C10J3/46Gasification of granular or pulverulent flues in suspension
    • C10J3/48Apparatus; Plants
    • C10J3/482Gasifiers with stationary fluidised bed
    • CCHEMISTRY; METALLURGY
    • C10PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
    • C10JPRODUCTION OF PRODUCER GAS, WATER-GAS, SYNTHESIS GAS FROM SOLID CARBONACEOUS MATERIAL, OR MIXTURES CONTAINING THESE GASES; CARBURETTING AIR OR OTHER GASES
    • C10J3/00Production of combustible gases containing carbon monoxide from solid carbonaceous fuels
    • C10J3/46Gasification of granular or pulverulent flues in suspension
    • C10J3/48Apparatus; Plants
    • C10J3/52Ash-removing devices
    • C10J3/523Ash-removing devices for gasifiers with stationary fluidised bed
    • CCHEMISTRY; METALLURGY
    • C10PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
    • C10JPRODUCTION OF PRODUCER GAS, WATER-GAS, SYNTHESIS GAS FROM SOLID CARBONACEOUS MATERIAL, OR MIXTURES CONTAINING THESE GASES; CARBURETTING AIR OR OTHER GASES
    • C10J3/00Production of combustible gases containing carbon monoxide from solid carbonaceous fuels
    • C10J3/72Other features
    • C10J3/721Multistage gasification, e.g. plural parallel or serial gasification stages
    • CCHEMISTRY; METALLURGY
    • C10PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
    • C10JPRODUCTION OF PRODUCER GAS, WATER-GAS, SYNTHESIS GAS FROM SOLID CARBONACEOUS MATERIAL, OR MIXTURES CONTAINING THESE GASES; CARBURETTING AIR OR OTHER GASES
    • C10J2300/00Details of gasification processes
    • C10J2300/09Details of the feed, e.g. feeding of spent catalyst, inert gas or halogens
    • C10J2300/0913Carbonaceous raw material
    • C10J2300/0916Biomass
    • CCHEMISTRY; METALLURGY
    • C10PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
    • C10JPRODUCTION OF PRODUCER GAS, WATER-GAS, SYNTHESIS GAS FROM SOLID CARBONACEOUS MATERIAL, OR MIXTURES CONTAINING THESE GASES; CARBURETTING AIR OR OTHER GASES
    • C10J2300/00Details of gasification processes
    • C10J2300/09Details of the feed, e.g. feeding of spent catalyst, inert gas or halogens
    • C10J2300/0913Carbonaceous raw material
    • C10J2300/093Coal
    • CCHEMISTRY; METALLURGY
    • C10PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
    • C10JPRODUCTION OF PRODUCER GAS, WATER-GAS, SYNTHESIS GAS FROM SOLID CARBONACEOUS MATERIAL, OR MIXTURES CONTAINING THESE GASES; CARBURETTING AIR OR OTHER GASES
    • C10J2300/00Details of gasification processes
    • C10J2300/09Details of the feed, e.g. feeding of spent catalyst, inert gas or halogens
    • C10J2300/0953Gasifying agents
    • C10J2300/0959Oxygen
    • CCHEMISTRY; METALLURGY
    • C10PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
    • C10JPRODUCTION OF PRODUCER GAS, WATER-GAS, SYNTHESIS GAS FROM SOLID CARBONACEOUS MATERIAL, OR MIXTURES CONTAINING THESE GASES; CARBURETTING AIR OR OTHER GASES
    • C10J2300/00Details of gasification processes
    • C10J2300/09Details of the feed, e.g. feeding of spent catalyst, inert gas or halogens
    • C10J2300/0953Gasifying agents
    • C10J2300/0973Water
    • C10J2300/0976Water as steam
    • CCHEMISTRY; METALLURGY
    • C10PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
    • C10JPRODUCTION OF PRODUCER GAS, WATER-GAS, SYNTHESIS GAS FROM SOLID CARBONACEOUS MATERIAL, OR MIXTURES CONTAINING THESE GASES; CARBURETTING AIR OR OTHER GASES
    • C10J2300/00Details of gasification processes
    • C10J2300/16Integration of gasification processes with another plant or parts within the plant
    • C10J2300/1625Integration of gasification processes with another plant or parts within the plant with solids treatment
    • C10J2300/1628Ash post-treatment
    • C10J2300/1631Ash recycling
    • CCHEMISTRY; METALLURGY
    • C10PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
    • C10JPRODUCTION OF PRODUCER GAS, WATER-GAS, SYNTHESIS GAS FROM SOLID CARBONACEOUS MATERIAL, OR MIXTURES CONTAINING THESE GASES; CARBURETTING AIR OR OTHER GASES
    • C10J2300/00Details of gasification processes
    • C10J2300/16Integration of gasification processes with another plant or parts within the plant
    • C10J2300/1625Integration of gasification processes with another plant or parts within the plant with solids treatment
    • C10J2300/1628Ash post-treatment
    • C10J2300/1634Ash vitrification

Definitions

  • the present invention relates to a method and apparatus for collecting and recycling fine solids in a multiphase chemical reactor, e.g. a fluidized bed reactor, an entrained-flow bed reactor, and a fixed bed reactor, in particular as it is used in gasification of coal, biomass and municipal solid waste.
  • a multiphase chemical reactor e.g. a fluidized bed reactor, an entrained-flow bed reactor, and a fixed bed reactor, in particular as it is used in gasification of coal, biomass and municipal solid waste.
  • a counter-current fixed bed (“up draft”) gasifier comprises a fixed bed of carbonaceous fuel (e.g. coal, biomass or MSW) through which the gasification agent (steam, carbon dioxide, oxygen and/or air) flows in counter-current configuration.
  • a co-current fixed bed (“down draft”) gasifier is similar to the counter-current type, but the gasification agent gas flows in co-current configuration with the fuel (often downwards, hence the name “down draft gasifier”).
  • the ash is either removed in a dry way or as a slag.
  • Pulverized dry fuel is typically fed into an entrained flow gasifier in the presence of oxidants.
  • the fuel and the oxidant are in co-current flow, forming a dense cloud of very fine particles, wherein gasification reactions take place.
  • the high temperature and pressure usually bring about better process conversion as well as higher throughput of a single gasification reactor.
  • considerable carbon loss can still be found, in the form of ash.
  • a fluid with appropriate high velocities suspends granular solids and causes them to behave as a fluid.
  • This process known as fluidization, possesses many important advantages, which, as a result, is used in many industrial applications, including gasification.
  • feedstock particles react with oxygen and steam to produce “syngas”, which is a mixture of carbon monoxide, hydrogen and carbon dioxide and other minor gas species.
  • the direct product from the fluidized bed region is referred to as the exit gas stream, containing both the product gas mixture and solids comprising carbon and ash.
  • the ash is removed dry (fines, or fly ash) or as heavy agglomerates (bottom ash) that defluidize.
  • fly ash carried over is a typical problem for fluidized bed reactors.
  • a fluidized bed gasifier is typically operated at a temperature between 800-1,100° C., which is lower than the typical ash fusion temperature (softening temperature) of 900-1,300° C. of most coal and biomass materials. Due to this relatively low operation temperature, some fuel particles are not fully reacted and converted to gas before they escape the reaction region. And there are considerable amount of not-fully-reacted fuel particles leaving the top of the reactor with the exit gas stream. It's not unusual that the fly ash contains 10% to 60% of un-reacted carbon.
  • fly ash was routinely returned to the gasifier in an attempt to recycle and reuse the carbon contained therein and reduce ash quantity, but the results have not been satisfactory.
  • the present invention allows the gasification systems to be simplified and capital investment reduced, and the limitation on fines content in feedstock removed or at least relaxed.
  • the present inventors recognized, for the first time, that the failure of the prior attempts was due in part to the failure of returning the ash consistently to a high temperature region of the reactor.
  • no one has attempted to return the fly ash consistently to the high temperature zone of the fluidized bed region.
  • this was in part due to the fact that the fly ash was usually returned to the fluidized bed region using a dipleg connected to the cyclone or baghouse where the fly ash was collected. Due to the high temperature and high particle velocity within the high temperature zone, the dipleg cannot reach the high temperature zone, or it would be quickly and easily eroded.
  • the present invention provides a novel and innovative solution to the above problems, and surprisingly and dramatically increased carbon conversion rate and reduced high fly-ash output in coal gasification.
  • the present invention provides a method for recycling fine ash particles for a multiphase chemical reactor (MCR), wherein coal is partially oxidized in the MCR to produce an exit gas stream in which fine ash particles are entrained, and wherein the MCR comprises a high temperature region with a temperature at or above a fusion temperature of the fine ash particles, the method comprising: a) separating the fine ash particles from the exit gas stream, and b) returning the fine ash particles collected in step a) above to the high temperature region.
  • MCR multiphase chemical reactor
  • the present invention further provides a MCR used in accordance with the method.
  • the MCR of the present invention is a fixed bed reactor, a fluidized bed reactor, or an entrained-flow bed reactor.
  • the MCR of the present invention is used for coal biomass and MSW gasification.
  • the fluidized bed reactor comprises a vertical reaction vessel having a dense phase portion and a dilute phase portion above the dense phase portion, and a distribution grid within the vessel in the dense phase portion defining the bottom of the reaction bed, wherein a high temperature zone is located above the distribution grid, and wherein the fine ash particles are returned to the high temperature zone through the distribution grid.
  • the fine ash particles are returned to the high temperature zone using a pneumatic gas conveyor system.
  • the gas used for the pneumatic conveyor system does not contain oxygen.
  • the gas used for the pneumatic conveyor system comprises carbon dioxide, hydrogen, syngas, steam, nitrogen, or a mixture thereof, in a suitable ratio.
  • one or more cyclones, one or more baghouse filter system, a ceramic filter, or an electric precipitator, or a combination thereof is used to separate or collect the fine ash particles from the exit gas stream.
  • the present invention in one preferred embodiment provides a fluidized bed coal gasification system in which coal-containing fuel particles react with oxygen and steam to produce syngas.
  • the system of the invention comprises 1) a fluidized bed reactor vessel which comprises a) an upper portion, wherein a fluidized bed region is formed during operation, and wherein an exit gas stream is formed with fly ash particles entrained therein; b) a lower portion separated from the upper portion by c) a conically shaped distribution plate with its apex pointing downward, having perforations thereon and a central opening at the apex, wherein bottom ash formed in the fluidized bed region can fall through the perforations and collected in the lower portion of the reactor vessel, d) a gas inlet through the opening, through which inlet a gas stream rich in oxygen can be injected into a region just above the distribution plate, wherein during operation a high temperature region is formed due to enhanced combustion of the carbon material in the region; 2) a fly ash collection subsystem wherein fly ash particles are separated from
  • the fly ash recycle subsystem comprises one or more stages of cyclone; or a bag house, or a ceramic filter; or an electric precipitator or a combination thereof.
  • the fly ash recycle subsystem comprises a pneumatic gas delivery device for delivering the fly ash.
  • the fluidized bed coal gasification system comprises a pneumatic gas delivery system which has a jet stream outlet through the distribution plate, which jet stream outlet has an opening that delivers the fly ash directly into the high temperature region just above the distribution grid.
  • FIG. 1 is a schematic diagram showing a typical fluidized bed reactor system for coal gasification.
  • FIG. 2 shows a specific embodiment of the present invention, wherein the fine particles of the fly ash, collected from the exit gas stream, is delivered though the distribution plate directly into the high temperature region.
  • FIG. 3 illustrates in more detail the construction of a pipe connecting with the distribution plate for delivery of fly ash into the high temperature region, in accordance with an embodiment of the present invention.
  • FIG. 4 are diagrams showing the general location of the high temperature in (a) updraft fixed gasifier; (b) downdraft fixed bed gasifier; (c) top-fired coal-water slurry feed slagging entrained flow gasifier; (d) top-fired dry-coal feed slagging entrained flow gasifier; and (e) side-fired dry-coal feed slagging entrained-flow gasifier.
  • FIG. 5 shows the fly ash size increases when fly ash is returned to the high temperature zone in accordance with a method of the present invention.
  • the present invention provides an apparatus, and a related method, useful in a multiphase reactor, such as a fixed bed reactor, an entrained-flow bed reactor, and a fluidized bed reactor, for recycling fine ash particles collected from the exit gas stream.
  • a multiphase reactor such as a fixed bed reactor, an entrained-flow bed reactor, and a fluidized bed reactor
  • the apparatus and method of the present invention are used in a reactor for coal or biomass gasification.
  • the method and apparatus of the present invention reliably and consistently return the fly ash into a high-temperature reaction region of the reactor, improving coal conversion rate, and reducing fly ash quantity.
  • Test results show that in one embodiment, the method of the present invention can convert almost all of the carbon in the reactant coal to syngas, increasing the carbon conversion rate from less than 90% to more than 99%, and almost all ash are collected as bottom ash from the fluidized bed reactor, while all fly ash was able to be returned to the reaction region and fully re-utilized.
  • fly ash in the exit gas stream is collected, e.g. via a cyclone, or a bag house, or a combination thereof, and sent back to the high-temperature region inside the gasifier.
  • the fine particles of the fly ash can react rapidly with the steam and oxygen. Due to the small size of the ash particles, and the high temperature (at or above the fusion temperature of the ash particles) and the high speed collision that occurs in the reaction region, the ash particles will fuse to form larger particles, and be discharged to the bottom of the gasifier as bottom ash, greatly diminishing their chance of being blown out as fly ash in the exit gas.
  • the high temperature region of a coal gasifier has a temperature not lower than the fusion temperature of the fly ash particles, usually not lower than 1,000° C., preferably not lower than 1,100° C.
  • the high temperature region is a region into which from about 10% to substantially all (100%) of the total oxygen consumed by the gasifier is inputted.
  • the high temperature region is a region into which from about 20%-100%, or from about 30-100%, or from about 40-100%, or from about 50-100%, or from about 60-100% or the total oxygen consumed by the gasifier is inputted.
  • FIG. 1 shows a typical fluidized bed reactor system for coal gasification.
  • the central component is a reaction vessel ( 1 ), frequently cylindrical in shape and made of steel lined in the interior with insulation materials.
  • the lower portion of the reaction vessel is narrower than the top portion.
  • the narrower portion is also referred to as the dense phase portion I of the reaction vessel, and the top portion the dilute phase or expansion phase II.
  • a gas distribution grid ( 2 ) is usually positioned in the vessel in the narrower portion of the vessel, and defines the bottom surface of the fluidized bed.
  • the central portion of the grid may be conical or cylindrical in shape and comprises a passage, usually located in the center of the grid.
  • a constriction having a fixed opening defining a venturi of fixed throat size to provide a uniform upward gas (oxygen/air and steam) velocity into the vessel and thus into the fluidized bed.
  • coal or other carbon-containing materials are introduced via one or more pipes ( 6 ) into the vessel, where they partially combust and react with the steam to form syngas.
  • Directing a stream of high velocity gas through the venturi or passage into the reaction vessel causes ash particles in the vessel to agglomerate and eventually discharge through the passage and venturi throat.
  • Additional gas or oxygenating agent may be provided through another inlet ( 3 ) and is allowed to permeate into the reaction region through the holes in the distribution grid.
  • fly ash is formed and exits with the product gas from the top of the vessel.
  • the reaction vessel is linked at the top to a first stage cyclone ( 11 ), which may in turn be linked to an optional second stage cyclone ( 14 ).
  • a first stage cyclone 11
  • an optional second stage cyclone 14
  • optional components such as a heat recovering tower ( 17 ) and a fly ash collector ( 19 ), which may be a baghouse or other filtering devices, the exit gas stream is separated into clean syngas and fly ash.
  • the fly ash is returned to the reactor region through the distribution grid.
  • a cyclone is a device that utilizes the centrifugal force to separate a fluid from particles entrained therein.
  • a conventional cyclone in a fluidized bed reactor is used to separate the gas and solids.
  • a cyclone has at least one tangential inlet for the solids laden gas stream, an outlet for the gas with reduced solids loading and another outlet for the solids collected.
  • the gas-solids inlet is typically located on the side wall and the gas outlet in the top and the solids outlet at the bottom.
  • a high temperature region ( 25 ) is formed just above the distribution plate, and near the exit of the venturi pipe where the oxygenating agent enters the fluidized bed region. As indicated above, this region is relative rich in oxygen, and relatively more combustion reaction of the coal material maintains the temperature of the entire reaction vessel, and the temperature in this region is higher than the rest of the reaction vessel and above that of the fusion temperature of the fly ash. In prior art devices, much of the fly ash would be blown up, leave this high temperature region, and exit with the syngas before it has had a chance to agglomerate or completely react with the oxygen.
  • FIG. 2 shows a specific embodiment of the present invention, wherein the fine particles of the fly ash, collected from the exit gas stream, is delivered though the distribution plate directly into the high temperature region.
  • the delivery is via a jet stream of carrier gas, e.g. a pneumatic conveyor system, carried in a pipe ( 24 ), whose exit may protrude above the plate by about 0 to about 1,000 mm.
  • carrier gas e.g. a pneumatic conveyor system
  • the carrier gas may be nitrogen, carbon dioxide, syngas, steam, or a mixture of two or more of the above in any suitable ratio. It is desired that the carrier gas should not contain oxygen to minimize the risk that oxygen will react with the carbon contained in the fly ash which is often at a high temperature. A skilled artisan will recognize that the amount, pressure and speed of the carrier gas for delivering the fly ash to the high temperature region can and should adjusted to ensure that all or substantially all of the fly ash will enter and remain into the high temperature region, so that the remaining carbon is converted into syngas product and the ash particles agglomerate to form large particles and exit the reaction vessel as bottom ash.
  • FIG. 3 illustrates in more detail the construction of a connection of a pipe ( 24 ) connecting with the distribution plate for delivery of fly ash into the high temperature region, in accordance with an embodiment of the present invention.
  • the pipe comprises a head 26 which further includes a ribbed plate ( 261 ) and a wear resistant lining ( 262 ).
  • FIG. 4 illustrates the high temperature region in fixed-bed as well as in entrained flow gasifiers.
  • the high temperature region may be defined as the region inside the reactor where the local temperature is higher than those of other regions, and is generally around the oxygen inject nozzle or grate.
  • the temperature of this region is well above ash fusion temperature
  • the invention achieves a high carbon conversion rate and reduces the amount of the fly ash from the gasifier.
  • the invention can be more readily understood by reference to the following examples, which are included merely for purposes of illustration of certain aspects and embodiments of the present invention and are not intended to limit the invention. It will be recognized by one of the skill in the art that many other permutations will accomplish the same objectives of delivering the carbon-containing fly ash directly to the high temperature region of the fluidized bed reactor.
  • the system further comprises and a heat recovering tower ( 17 ), a fly ash collector ( 19 ), a fly ash lock hopper ( 21 ) and a fly ash transfer hopper ( 23 ).
  • a pneumatic gas conveying system was used to delivery the fine fly ash, collected from a baghouse with or without an operational second-stage cyclone, into a high temperature (higher than the hemisphere temperature, or T3, for the fly ash) zone, which is also O 2 -rich (>10%), of the gasifier.
  • Pneumatic Convey System Design A fully automatic programmable logic control (PLC) system was used, and interlock protections were designed.
  • the connection to gasifier was through a D80 pipe installed with an angle of approximately 45° to the vertical center pipe ( 5 ) and enters through the distribution plate or grid board.
  • Control experiments were performed wherein the fly ash was not returned to the high-temperature zone. Specifically, a coal gasification system, as described in FIG. 1 , was operated for 48 hours, wherein the fly ash were not returned to the gasifier.
  • the system was then operated for 72 hours, wherein the fly ash was returned to the high-temperature region via the distribution plate. Other conditions for the operation was kept constant during these two stages. Particularized coal and pure oxygen (99.6%) and steam were used.
  • the pressure inside the reaction vessel was at 321 kPa, with a temperature of about 1020-1024° C.
  • the gas used to deliver the fly ash to the gasifier contains 70% CO 2 , with the remainder being H 2 and CO.
  • the coal used has the following characteristics:
  • the fine carbon-containing ash articles were nearly completely burned just within about 0.2 seconds, and the ash particles melted or softened, and its density increased. As shown in Table 2 below and in FIG. 5 , the molten or softened ash particles were glutinous and grew in size, most likely after repeated collisions. In contrast, fine coal particles, prior to burning, have a higher fusion temperature and as such were not able to melt or soften or fuse with other coal particles.
  • the above test showed that the actual carbon conversion rate reached 99.2%, compared to just a bit above 85% in the control. Almost all ash was discharged as bottom ash with zero fly ash discharge.
  • the test achieved a coal to syngas rate of 1.32 NM 3 /kg with a coal LHV 4550 kcal/kg. The represented a 15% reduction of coal consumption or around 20 ton coal savings per day based on a gasifier output of 7500 NM 3 /h;
  • coal gasification systems can be simplified and capital investment reduced, because at least a second-stage cyclone, and perhaps other fly ash capturing components can be omitted (at least the total bag houses or filters can be reduced) while coal consumption reduced and gas output increased. Furthermore, the limit of coal fine size of 0.15 mm to ⁇ 15% can also be ignored.

Landscapes

  • Chemical & Material Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Combustion & Propulsion (AREA)
  • Oil, Petroleum & Natural Gas (AREA)
  • Organic Chemistry (AREA)
  • Devices And Processes Conducted In The Presence Of Fluids And Solid Particles (AREA)
  • Fluidized-Bed Combustion And Resonant Combustion (AREA)
  • Physical Or Chemical Processes And Apparatus (AREA)
  • Processing Of Solid Wastes (AREA)
  • Industrial Gases (AREA)

Abstract

Method and apparatus for recycling fine ash particles for a multiphase chemical reactor (MCR), wherein coal is partially oxidized in the MCR to produce an exit gas stream in which fine ash particles are entrained, and wherein the MCR comprises a high temperature region with a temperature at or above a fusion temperature of the fine ash particles, wherein substantially all of the fine ash particles from the exit gas stream are returned to the high temperature region, to achieve improved carbon conversion and reduction in fly ash quantity.

Description

    FIELD
  • The present invention relates to a method and apparatus for collecting and recycling fine solids in a multiphase chemical reactor, e.g. a fluidized bed reactor, an entrained-flow bed reactor, and a fixed bed reactor, in particular as it is used in gasification of coal, biomass and municipal solid waste.
  • BACKGROUND OF THE INVENTION
  • In industrial chemical engineering, several types of reactors are commonly used to carry out a variety of multiphase chemical reactions. Fixed bed reactors (counter-current or co-current), fluidized bed reactors, and entrained-flow bed reactors are typical multiphase reactors. They are often used in gasification of coal, biomass and municipal solid waste (MSW).
  • Specifically, a counter-current fixed bed (“up draft”) gasifier comprises a fixed bed of carbonaceous fuel (e.g. coal, biomass or MSW) through which the gasification agent (steam, carbon dioxide, oxygen and/or air) flows in counter-current configuration. A co-current fixed bed (“down draft”) gasifier is similar to the counter-current type, but the gasification agent gas flows in co-current configuration with the fuel (often downwards, hence the name “down draft gasifier”). The ash is either removed in a dry way or as a slag.
  • Pulverized dry fuel is typically fed into an entrained flow gasifier in the presence of oxidants. The fuel and the oxidant are in co-current flow, forming a dense cloud of very fine particles, wherein gasification reactions take place. The high temperature and pressure usually bring about better process conversion as well as higher throughput of a single gasification reactor. However, in some cases, considerable carbon loss can still be found, in the form of ash.
  • In a fluidized bed reactor, a fluid with appropriate high velocities suspends granular solids and causes them to behave as a fluid. This process, known as fluidization, possesses many important advantages, which, as a result, is used in many industrial applications, including gasification. In fluidized bed gasification, feedstock particles react with oxygen and steam to produce “syngas”, which is a mixture of carbon monoxide, hydrogen and carbon dioxide and other minor gas species. The direct product from the fluidized bed region is referred to as the exit gas stream, containing both the product gas mixture and solids comprising carbon and ash. Generally, the ash is removed dry (fines, or fly ash) or as heavy agglomerates (bottom ash) that defluidize.
  • Fly ash carried over is a typical problem for fluidized bed reactors. A fluidized bed gasifier is typically operated at a temperature between 800-1,100° C., which is lower than the typical ash fusion temperature (softening temperature) of 900-1,300° C. of most coal and biomass materials. Due to this relatively low operation temperature, some fuel particles are not fully reacted and converted to gas before they escape the reaction region. And there are considerable amount of not-fully-reacted fuel particles leaving the top of the reactor with the exit gas stream. It's not unusual that the fly ash contains 10% to 60% of un-reacted carbon.
  • In order to make the most of the solid phase reactant, and to reduce fines loss at the top, one or more stages of cyclones are often used for such multiphase reactors. These fine particles may be burned in another reactor, but this requires additional equipment and may significantly add operational costs to the process.
  • Another typical way to utilize the collected fly ash which contains high carbon contents is to recycle them to the gasification reactor for further reactions. However, there is a possibility that the recycled fly ash would not be readily reacted, especially when the temperature in the reactor is not high enough. In this case, the fly ash would be just cycling within the loop without bringing any apparent improvement in gasification process efficiency.
  • Therefore, there is a need for a new method and a new apparatus that can solve the above problems of the prior art.
  • SUMMARY OF THE INVENTION
  • As discussed above, fly ash was routinely returned to the gasifier in an attempt to recycle and reuse the carbon contained therein and reduce ash quantity, but the results have not been satisfactory. The present invention allows the gasification systems to be simplified and capital investment reduced, and the limitation on fines content in feedstock removed or at least relaxed.
  • The present inventors recognized, for the first time, that the failure of the prior attempts was due in part to the failure of returning the ash consistently to a high temperature region of the reactor. In fact, prior to the advent of the present invention, no one has attempted to return the fly ash consistently to the high temperature zone of the fluidized bed region. In the case of the fluidized bed reactors, this was in part due to the fact that the fly ash was usually returned to the fluidized bed region using a dipleg connected to the cyclone or baghouse where the fly ash was collected. Due to the high temperature and high particle velocity within the high temperature zone, the dipleg cannot reach the high temperature zone, or it would be quickly and easily eroded.
  • The present invention provides a novel and innovative solution to the above problems, and surprisingly and dramatically increased carbon conversion rate and reduced high fly-ash output in coal gasification.
  • In one embodiment, the present invention provides a method for recycling fine ash particles for a multiphase chemical reactor (MCR), wherein coal is partially oxidized in the MCR to produce an exit gas stream in which fine ash particles are entrained, and wherein the MCR comprises a high temperature region with a temperature at or above a fusion temperature of the fine ash particles, the method comprising: a) separating the fine ash particles from the exit gas stream, and b) returning the fine ash particles collected in step a) above to the high temperature region.
  • The present invention further provides a MCR used in accordance with the method.
  • In one embodiment, the MCR of the present invention is a fixed bed reactor, a fluidized bed reactor, or an entrained-flow bed reactor.
  • In one embodiment, the MCR of the present invention is used for coal biomass and MSW gasification.
  • In one embodiment, the fluidized bed reactor comprises a vertical reaction vessel having a dense phase portion and a dilute phase portion above the dense phase portion, and a distribution grid within the vessel in the dense phase portion defining the bottom of the reaction bed, wherein a high temperature zone is located above the distribution grid, and wherein the fine ash particles are returned to the high temperature zone through the distribution grid.
  • In one embodiment, the fine ash particles are returned to the high temperature zone using a pneumatic gas conveyor system. In one embodiment, the gas used for the pneumatic conveyor system does not contain oxygen. In one embodiment, the gas used for the pneumatic conveyor system comprises carbon dioxide, hydrogen, syngas, steam, nitrogen, or a mixture thereof, in a suitable ratio.
  • In accordance with another embodiment, one or more cyclones, one or more baghouse filter system, a ceramic filter, or an electric precipitator, or a combination thereof, is used to separate or collect the fine ash particles from the exit gas stream.
  • The present invention in one preferred embodiment provides a fluidized bed coal gasification system in which coal-containing fuel particles react with oxygen and steam to produce syngas. The system of the invention, in one embodiment, comprises 1) a fluidized bed reactor vessel which comprises a) an upper portion, wherein a fluidized bed region is formed during operation, and wherein an exit gas stream is formed with fly ash particles entrained therein; b) a lower portion separated from the upper portion by c) a conically shaped distribution plate with its apex pointing downward, having perforations thereon and a central opening at the apex, wherein bottom ash formed in the fluidized bed region can fall through the perforations and collected in the lower portion of the reactor vessel, d) a gas inlet through the opening, through which inlet a gas stream rich in oxygen can be injected into a region just above the distribution plate, wherein during operation a high temperature region is formed due to enhanced combustion of the carbon material in the region; 2) a fly ash collection subsystem wherein fly ash particles are separated from the exit gas stream and collected, and 3) a fly ash recycle subsystem, wherein the fly ash particles collected in the fly ash collection system are returned directly into the high temperature region.
  • In one embodiment, in the fluidized bed coal gasification system the fly ash recycle subsystem comprises one or more stages of cyclone; or a bag house, or a ceramic filter; or an electric precipitator or a combination thereof. In another embodiment, in the fluidized bed coal gasification system according of the present invention, the fly ash recycle subsystem comprises a pneumatic gas delivery device for delivering the fly ash.
  • In one embodiment, the fluidized bed coal gasification system comprises a pneumatic gas delivery system which has a jet stream outlet through the distribution plate, which jet stream outlet has an opening that delivers the fly ash directly into the high temperature region just above the distribution grid.
  • BRIEF DESCRIPTION OF THE DRAWINGS
  • FIG. 1 is a schematic diagram showing a typical fluidized bed reactor system for coal gasification.
  • FIG. 2 shows a specific embodiment of the present invention, wherein the fine particles of the fly ash, collected from the exit gas stream, is delivered though the distribution plate directly into the high temperature region.
  • FIG. 3 illustrates in more detail the construction of a pipe connecting with the distribution plate for delivery of fly ash into the high temperature region, in accordance with an embodiment of the present invention.
  • FIG. 4 are diagrams showing the general location of the high temperature in (a) updraft fixed gasifier; (b) downdraft fixed bed gasifier; (c) top-fired coal-water slurry feed slagging entrained flow gasifier; (d) top-fired dry-coal feed slagging entrained flow gasifier; and (e) side-fired dry-coal feed slagging entrained-flow gasifier.
  • FIG. 5 shows the fly ash size increases when fly ash is returned to the high temperature zone in accordance with a method of the present invention.
  • DETAILED DESCRIPTION OF THE INVENTION
  • The present invention provides an apparatus, and a related method, useful in a multiphase reactor, such as a fixed bed reactor, an entrained-flow bed reactor, and a fluidized bed reactor, for recycling fine ash particles collected from the exit gas stream. Preferably, the apparatus and method of the present invention are used in a reactor for coal or biomass gasification. When used in coal or biomass gasification, the method and apparatus of the present invention reliably and consistently return the fly ash into a high-temperature reaction region of the reactor, improving coal conversion rate, and reducing fly ash quantity.
  • Test results show that in one embodiment, the method of the present invention can convert almost all of the carbon in the reactant coal to syngas, increasing the carbon conversion rate from less than 90% to more than 99%, and almost all ash are collected as bottom ash from the fluidized bed reactor, while all fly ash was able to be returned to the reaction region and fully re-utilized.
  • In accordance with an aspect of the present invention, fly ash in the exit gas stream is collected, e.g. via a cyclone, or a bag house, or a combination thereof, and sent back to the high-temperature region inside the gasifier. In the high-temperature region, the fine particles of the fly ash can react rapidly with the steam and oxygen. Due to the small size of the ash particles, and the high temperature (at or above the fusion temperature of the ash particles) and the high speed collision that occurs in the reaction region, the ash particles will fuse to form larger particles, and be discharged to the bottom of the gasifier as bottom ash, greatly diminishing their chance of being blown out as fly ash in the exit gas.
  • One of skills in the art will readily recognize that in a multiphase reactors, a region exists where the reaction is most intensive. For example, in the reaction zone of a coal gasifier, wherein oxygen is introduced to coal, the region where oxygen content is higher than other regions would have more rapid or intensive oxidization reaction and as such would have a higher temperature than the rest of the reaction zone. For the purpose of this description, the high temperature region of a coal gasifier has a temperature not lower than the fusion temperature of the fly ash particles, usually not lower than 1,000° C., preferably not lower than 1,100° C. In the case in a fluidized coal gasifier, usually the high temperature region is a region into which from about 10% to substantially all (100%) of the total oxygen consumed by the gasifier is inputted. Preferably the high temperature region is a region into which from about 20%-100%, or from about 30-100%, or from about 40-100%, or from about 50-100%, or from about 60-100% or the total oxygen consumed by the gasifier is inputted.
  • FIG. 1 shows a typical fluidized bed reactor system for coal gasification. The central component is a reaction vessel (1), frequently cylindrical in shape and made of steel lined in the interior with insulation materials. In the illustrated embodiment, the lower portion of the reaction vessel is narrower than the top portion. The narrower portion is also referred to as the dense phase portion I of the reaction vessel, and the top portion the dilute phase or expansion phase II. A gas distribution grid (2) is usually positioned in the vessel in the narrower portion of the vessel, and defines the bottom surface of the fluidized bed. The central portion of the grid may be conical or cylindrical in shape and comprises a passage, usually located in the center of the grid. At the bottom of the passage, a constriction is provided having a fixed opening defining a venturi of fixed throat size to provide a uniform upward gas (oxygen/air and steam) velocity into the vessel and thus into the fluidized bed. In an appropriate position above the distribution plate, coal or other carbon-containing materials are introduced via one or more pipes (6) into the vessel, where they partially combust and react with the steam to form syngas. Directing a stream of high velocity gas through the venturi or passage into the reaction vessel causes ash particles in the vessel to agglomerate and eventually discharge through the passage and venturi throat. Additional gas or oxygenating agent may be provided through another inlet (3) and is allowed to permeate into the reaction region through the holes in the distribution grid. As discussed above, in the prior art devices, fly ash is formed and exits with the product gas from the top of the vessel.
  • The reaction vessel is linked at the top to a first stage cyclone (11), which may in turn be linked to an optional second stage cyclone (14). Through optional components such as a heat recovering tower (17) and a fly ash collector (19), which may be a baghouse or other filtering devices, the exit gas stream is separated into clean syngas and fly ash.
  • According to an embodiment of the present invention, the fly ash is returned to the reactor region through the distribution grid.
  • A cyclone is a device that utilizes the centrifugal force to separate a fluid from particles entrained therein. A conventional cyclone in a fluidized bed reactor is used to separate the gas and solids. A cyclone has at least one tangential inlet for the solids laden gas stream, an outlet for the gas with reduced solids loading and another outlet for the solids collected. For most conventional cyclones, the gas-solids inlet is typically located on the side wall and the gas outlet in the top and the solids outlet at the bottom.
  • A high temperature region (25) is formed just above the distribution plate, and near the exit of the venturi pipe where the oxygenating agent enters the fluidized bed region. As indicated above, this region is relative rich in oxygen, and relatively more combustion reaction of the coal material maintains the temperature of the entire reaction vessel, and the temperature in this region is higher than the rest of the reaction vessel and above that of the fusion temperature of the fly ash. In prior art devices, much of the fly ash would be blown up, leave this high temperature region, and exit with the syngas before it has had a chance to agglomerate or completely react with the oxygen.
  • FIG. 2 shows a specific embodiment of the present invention, wherein the fine particles of the fly ash, collected from the exit gas stream, is delivered though the distribution plate directly into the high temperature region. In one embodiment, the delivery is via a jet stream of carrier gas, e.g. a pneumatic conveyor system, carried in a pipe (24), whose exit may protrude above the plate by about 0 to about 1,000 mm.
  • The carrier gas may be nitrogen, carbon dioxide, syngas, steam, or a mixture of two or more of the above in any suitable ratio. It is desired that the carrier gas should not contain oxygen to minimize the risk that oxygen will react with the carbon contained in the fly ash which is often at a high temperature. A skilled artisan will recognize that the amount, pressure and speed of the carrier gas for delivering the fly ash to the high temperature region can and should adjusted to ensure that all or substantially all of the fly ash will enter and remain into the high temperature region, so that the remaining carbon is converted into syngas product and the ash particles agglomerate to form large particles and exit the reaction vessel as bottom ash.
  • FIG. 3 illustrates in more detail the construction of a connection of a pipe (24) connecting with the distribution plate for delivery of fly ash into the high temperature region, in accordance with an embodiment of the present invention. The pipe comprises a head 26 which further includes a ribbed plate (261) and a wear resistant lining (262).
  • FIG. 4 illustrates the high temperature region in fixed-bed as well as in entrained flow gasifiers. In both cases, the high temperature region may be defined as the region inside the reactor where the local temperature is higher than those of other regions, and is generally around the oxygen inject nozzle or grate. In the entrained flow gasifier, the temperature of this region is well above ash fusion temperature
  • The invention achieves a high carbon conversion rate and reduces the amount of the fly ash from the gasifier. The invention can be more readily understood by reference to the following examples, which are included merely for purposes of illustration of certain aspects and embodiments of the present invention and are not intended to limit the invention. It will be recognized by one of the skill in the art that many other permutations will accomplish the same objectives of delivering the carbon-containing fly ash directly to the high temperature region of the fluidized bed reactor.
  • For example, in one preferred embodiment of the present invention, the system further comprises and a heat recovering tower (17), a fly ash collector (19), a fly ash lock hopper (21) and a fly ash transfer hopper (23).
  • EXAMPLES Example 1
  • A pneumatic gas conveying system was used to delivery the fine fly ash, collected from a baghouse with or without an operational second-stage cyclone, into a high temperature (higher than the hemisphere temperature, or T3, for the fly ash) zone, which is also O2-rich (>10%), of the gasifier.
  • Pneumatic Convey System Design A fully automatic programmable logic control (PLC) system was used, and interlock protections were designed. The connection to gasifier was through a D80 pipe installed with an angle of approximately 45° to the vertical center pipe (5) and enters through the distribution plate or grid board.
  • Control experiments were performed wherein the fly ash was not returned to the high-temperature zone. Specifically, a coal gasification system, as described in FIG. 1, was operated for 48 hours, wherein the fly ash were not returned to the gasifier.
  • The system was then operated for 72 hours, wherein the fly ash was returned to the high-temperature region via the distribution plate. Other conditions for the operation was kept constant during these two stages. Particularized coal and pure oxygen (99.6%) and steam were used. The pressure inside the reaction vessel was at 321 kPa, with a temperature of about 1020-1024° C. The gas used to deliver the fly ash to the gasifier contains 70% CO2, with the remainder being H2 and CO. The coal used has the following characteristics:
  • TABLE 1
    Analysis of Coal Used in the Testing (Wt %)
    C H O N S Ash Water
    Element wt % 55.58 3.62 8.56 0.94 1.10 25.92 4.28
  • Once returned to the high-temperature zone, the fine carbon-containing ash articles were nearly completely burned just within about 0.2 seconds, and the ash particles melted or softened, and its density increased. As shown in Table 2 below and in FIG. 5, the molten or softened ash particles were glutinous and grew in size, most likely after repeated collisions. In contrast, fine coal particles, prior to burning, have a higher fusion temperature and as such were not able to melt or soften or fuse with other coal particles.
  • TABLE 2
    Ash Particle Size Comparison
    Ash Size Range (mm)
    >3.35 2.36-3.35 1.18-2.36 0.83-1.18 0.27-0.83 <0.27
    Control 6.39 5.17 10.64 5.1 25.91 46.79
    (%)
    Test (%) 5.54 2.81 5.96 4.31 67.87 13.51
  • Carbon Conversion Rate; Coal to Net Syngas Rate, and Bottom Ash Analysis
  • Using both the ash balance and carbon balance methods of calculation, we determined that the carbon conversion (CC) rate was 99.2%, with an error rate of less than 0.1%. We also calculated the coal to syngas conversion rate, and carbon content in the bottom ash. These results are summarized in Table 3 below.
  • TABLE 3
    Comparison of Carbon Conversion Rate, Cold Gas
    Efficiency and Bottom Ash Carbon Content
    Coal Conversion Cold Gas Bottom Ash
    Rate % Efficiency % Coal Content wt %
    Control 85.2 70.8 6.6
    Test 99.1 81.1 1.5
  • Conclusion
  • The above test showed that the actual carbon conversion rate reached 99.2%, compared to just a bit above 85% in the control. Almost all ash was discharged as bottom ash with zero fly ash discharge. The test achieved a coal to syngas rate of 1.32 NM3/kg with a coal LHV 4550 kcal/kg. The represented a 15% reduction of coal consumption or around 20 ton coal savings per day based on a gasifier output of 7500 NM3/h;
  • The test results showed that using the method of the present invention, coal gasification systems can be simplified and capital investment reduced, because at least a second-stage cyclone, and perhaps other fly ash capturing components can be omitted (at least the total bag houses or filters can be reduced) while coal consumption reduced and gas output increased. Furthermore, the limit of coal fine size of 0.15 mm to <15% can also be ignored.

Claims (22)

What is claimed is:
1. A method for recycling fine ash particles for a multiphase chemical reactor (MCR), wherein coal is partially combusted in the MCR to produce an exit gas stream in which fine ash particles are entrained, and wherein the MCR comprises a high temperature region with a temperature at or above a fusion temperature of the fine ash particles, the method comprising:
a) separating the fine ash particles from the exit gas stream, and
b) returning the fine ash particles collected in step a) above to the high temperature region.
2. The method according to claim 1, wherein the MCR is selected from the group consisting of a fixed bed reactor, a fluidized bed reactor, and an entrained-flow bed reactor.
3. The method according to claim 2, wherein the MCR is a fluidized bed reactor.
4. The method according to claim 3, wherein the fluidized bed reactor is one used for coal gasification.
5. The method according to claim 4, wherein the fluidized bed reactor comprises a vertical reaction vessel having a dense phase portion and a dilute phase portion above the dense phase portion, and a distribution grid within the vessel in the dense phase portion defining the bottom of the reaction bed, wherein a high temperature zone is located above the distribution grid, and wherein the fine ash particles are returned to the high temperature zone through the distribution grid.
6. The method according to claim 5, wherein the fine ash particles are returned to the high temperature zone using a pneumatic gas conveyor system.
7. The method according to claim 6, where the gas used for the pneumatic conveyor system does not contain oxygen.
8. The method according to claim 6, where the gas used for the pneumatic conveyor system comprises nitrogen, carbon dioxide, hydrogen, syngas, steam, or a mixture thereof.
9. The method according to claim 1, wherein one or more cyclones, one or more baghouse filter systems, one or more ceramic filters, one or more electric precipitators, or a combination thereof, are used to separate or collect the fine ash particles from the exit gas stream.
10. A multiphase chemical reactor (MCR) in which coal is partially combusted in the MCR to produce an exit gas stream in which fine ash particles are entrained, and wherein the MCR comprises a high temperature region with a temperature at or above a fusion temperature of the fine ash particles, comprising: a fine ash particle collection system for separating the fine ash particles from the exit gas stream, and a fine ash particle conveyor system for returning the fine ash particles to the high temperature region.
11. The MCR according to claim 10, selected from the group consisting of a fixed bed reactor, a fluidized bed reactor, and an entrained-flow bed reactor.
12. The MCR according to claim 11, which is a fluidized bed reactor.
13. The MCR according to claim 12, wherein the fluidized bed reactor is used for coal gasification.
14. The MCR according to claim 13, wherein the fluidized bed reactor comprises a vertical reaction vessel having a dense phase portion and a dilute phase portion above the dense phase portion, and a distribution grid within the vessel in the dense phase portion defining the bottom of the reaction bed, wherein a high temperature zone is located above the distribution grid, and wherein the fine ash particles are returned to the high temperature zone through the distribution grid.
15. The MCR according to claim 14, wherein the fine ash particles are returned to the high temperature zone using a pneumatic gas conveyor system.
16. The MCR according to claim 15, where the gas used for the pneumatic conveyor system does not contain oxygen.
17. The MCR according to claim 16, where the gas used for the pneumatic conveyor system comprises nitrogen, carbon dioxide, hydrogen, syngas, steam, or a mixture thereof.
18. The MCR according to claim 10, wherein one or more cyclones or one or more baghouse filter systems, one or more ceramic filters, one or more electric precipitators, or a combination thereof, are used to separate or collect the fine ash particles from the exit gas stream.
19. A fluidized bed coal gasification system in which coal-containing fuel particles react with oxygen and steam to produce syngas, the system comprising
1) a fluidized bed reactor vessel which comprises
a) an upper portion, wherein a fluidized bed region is formed during operation, and wherein an exit gas stream is formed with fly ash particles entrained therein;
b) a lower portion separated from the upper portion by
c) a conically shaped distribution plate with its apex pointing downward, having perforations thereon and a central opening at the apex, wherein bottom ash formed in the fluidized bed region can fall through the central opening and collected in the lower portion of the reactor vessel,
d) a gas inlet through the opening, through which inlet a gas stream rich in oxygen can be injected into a region just above the distribution plate, wherein during operation a high temperature region is formed due to enhanced combustion of the carbon material in the region,
2) a fly ash collection subsystem wherein fly ash particles are separated from the exit gas stream and collected, and
3) a fly ash recycle subsystem, wherein the fly ash particles collected in the fly ash collection system are returned directly into the high temperature region.
20. The fluidized bed coal gasification system according to claim 19, wherein the fly ash recycle subsystem comprises one or more stages of cyclone, one or more baghouse filter systems, one or more ceramic filters, one or more electric precipitators, or a combination thereof.
21. The fluidized bed coal gasification system according to claim 20, wherein the fly ash recycle subsystem comprises a pneumatic gas delivery device for delivering the fly ash.
22. The fluidized bed coal gasification system according to claim 21, wherein the pneumatic gas delivery system has a jet stream outlet through the distribution plate, and the fly ash is delivered directly into the high temperature region just above the distribution grid.
US13/990,042 2010-11-29 2011-11-29 Method and apparatus for particle recycling in multiphase chemical reactors Abandoned US20130312328A1 (en)

Applications Claiming Priority (3)

Application Number Priority Date Filing Date Title
CN201010582393.3 2010-11-29
CN201010582393.3A CN102477314B (en) 2010-11-29 2010-11-29 Method and apparatus used for recovering and utilizing particles in heterogeneous chemical reactor
PCT/US2011/062273 WO2012074942A2 (en) 2010-11-29 2011-11-29 Method and apparatus for particle recycling in multiphase chemical reactors

Publications (1)

Publication Number Publication Date
US20130312328A1 true US20130312328A1 (en) 2013-11-28

Family

ID=46090098

Family Applications (1)

Application Number Title Priority Date Filing Date
US13/990,042 Abandoned US20130312328A1 (en) 2010-11-29 2011-11-29 Method and apparatus for particle recycling in multiphase chemical reactors

Country Status (4)

Country Link
US (1) US20130312328A1 (en)
CN (1) CN102477314B (en)
AU (1) AU2011336788B2 (en)
WO (1) WO2012074942A2 (en)

Cited By (10)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US20140090298A1 (en) * 2011-06-10 2014-04-03 Bharat Petroleum Corporation Limited Process for co-gasification of two or more carbonaceous feedstocks and apparatus thereof
CN104673397A (en) * 2015-01-26 2015-06-03 新奥科技发展有限公司 Fluidized bed gas distributor and gasifier
WO2016158918A1 (en) * 2015-03-30 2016-10-06 株式会社クボタ Gasification furnace, method of operating gasification furnace and biomass gasification treatment method
CN106010666A (en) * 2016-07-25 2016-10-12 上海锅炉厂有限公司 Circulating fluidized bed gasifying system and gasifying method thereof
JP2016190887A (en) * 2015-03-30 2016-11-10 株式会社クボタ Gasification furnace, method for operating the gasification furnace, and biomass gasification treatment method
JP2016190889A (en) * 2015-03-30 2016-11-10 株式会社クボタ Gasification furnace and method for operating the gasification furnace
US9527026B2 (en) 2013-03-14 2016-12-27 Synthesis Energy Systems, Inc. Method and apparatus for recycling ash fines
JP2019094362A (en) * 2017-11-17 2019-06-20 三菱日立パワーシステムズ株式会社 Biomass gasification equipment and operation method thereof
US20220340828A1 (en) * 2020-12-07 2022-10-27 Huaneng Clean Energy Research Institute Fly ash recycling gasification furnace
US20230132767A1 (en) * 2021-10-29 2023-05-04 Simonpietri Enterprises LLC Processing and gasification of construction and demolition materials

Families Citing this family (19)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102827644A (en) * 2012-09-18 2012-12-19 山东天力干燥股份有限公司 Gas distributor for ash agglomerating fluidized-bed gasification furnace
DE102013101368B4 (en) * 2013-02-12 2023-04-27 Gidara Energy B.V. fluidized bed gasifier
CN103184077A (en) * 2013-03-21 2013-07-03 浙江工业大学化工设备有限公司 Fine coal gasification method with fly ash compulsory recycling system
CN103224813B (en) * 2013-04-15 2014-11-05 中国五环工程有限公司 Pressurized fluidized bed technology for coal gasification and pressurized fluidized bed system
US10458329B2 (en) 2014-03-06 2019-10-29 Uop Llc System and process for recovering power and steam from regenerator flue gas
CN104277881B (en) * 2014-09-25 2017-02-15 上海锅炉厂有限公司 Dry-process deslagging fluidized bed gasification reaction device
CN104498103B (en) * 2014-12-30 2017-03-15 上海锅炉厂有限公司 A kind of combined type circulating fluidized gasification reaction unit
CN104531224B (en) * 2015-01-04 2017-02-22 武汉江汉化工设计有限公司 Clean coal pressurized fluidized bed slag gasification process and system
CN104593088B (en) * 2015-01-23 2018-05-25 新奥科技发展有限公司 A kind of coal gasification reaction device and method
CN105602625B (en) * 2016-03-14 2018-09-21 鲁西化工集团股份有限公司煤化工分公司 A kind of flyash recycling new process
CN106520209B (en) * 2016-08-10 2021-12-14 义马煤业综能新能源有限责任公司 Continuous fly ash return control system and method for U-Gas gasifier
CN107057771A (en) * 2017-06-27 2017-08-18 哈尔滨工业大学 A kind of Two-way Cycle Circulating Fluidized Bed Gasifier For Biomass
BR112020007743B1 (en) * 2017-10-19 2023-11-21 Phakorn Kosonsittiwit APPARATUS FOR PRODUCTION AND COMBUSTION OF FUEL GAS
CN108219859B (en) * 2018-03-09 2024-01-23 陕西延长石油(集团)有限责任公司 Dust removal device and method for producing coarse synthetic gas by circulating fluidized bed pulverized coal gasification
CN108753367A (en) * 2018-07-25 2018-11-06 上海正申建设工程有限公司 A kind of the fluid bed powder coal gasification device and technique of flying dust zero-emission
CN109517627A (en) * 2019-01-22 2019-03-26 中聚信海洋工程装备有限公司 A kind of device and method of carbon containing flying dust cycle gasification
CN109628153A (en) * 2019-01-24 2019-04-16 江苏普格机械有限公司 The method and fluidized-bed gasification furnace of coal gasification efficiency can be improved
CN109694752B (en) * 2019-03-01 2024-08-09 中化学装备科技(苏州)有限公司 Powder return method of fluidized bed and fluidized bed gasification furnace based on method
CN110527560A (en) * 2019-10-08 2019-12-03 邰学林 A kind of organic solid waste cleaning disposal of resources method

Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US4177742A (en) * 1978-04-05 1979-12-11 Babcock-Hitachi Kabushiki Kaisha Incinerator for burning waste and a method of utilizing same
US4315758A (en) * 1979-10-15 1982-02-16 Institute Of Gas Technology Process for the production of fuel gas from coal
US4690076A (en) * 1986-04-04 1987-09-01 Combustion Engineering, Inc. Method for drying coal with hot recycle material
US4872423A (en) * 1987-03-25 1989-10-10 Abb Stal Ab Method for improving utilization of sulphur-absorbent when burning fuel in a fluidized bed and a power plant in which fuel is burned in a fluidized bed

Family Cites Families (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US4158552A (en) * 1977-08-29 1979-06-19 Combustion Engineering, Inc. Entrained flow coal gasifier
US4474583A (en) * 1982-06-11 1984-10-02 Foster Wheeler Energy Corporation Process for gasifying solid carbonaceous fuels
US4483692A (en) * 1983-01-27 1984-11-20 Institute Of Gas Technology Process for the recycling of coal fines from a fluidized bed coal gasification reactor
JP3118630B2 (en) * 1995-09-22 2000-12-18 株式会社日立製作所 Coal gasifier
WO2009149311A1 (en) * 2008-06-05 2009-12-10 Synthesis Energy Systems, Inc.Reply To # Fluidized bed gasifier with solids discharge and classification device
CN101372635B (en) * 2008-10-15 2011-07-06 东南大学 High-density pressurized fluidized bed coal gasification apparatus and method

Patent Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US4177742A (en) * 1978-04-05 1979-12-11 Babcock-Hitachi Kabushiki Kaisha Incinerator for burning waste and a method of utilizing same
US4315758A (en) * 1979-10-15 1982-02-16 Institute Of Gas Technology Process for the production of fuel gas from coal
US4690076A (en) * 1986-04-04 1987-09-01 Combustion Engineering, Inc. Method for drying coal with hot recycle material
US4872423A (en) * 1987-03-25 1989-10-10 Abb Stal Ab Method for improving utilization of sulphur-absorbent when burning fuel in a fluidized bed and a power plant in which fuel is burned in a fluidized bed

Cited By (14)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US10174265B2 (en) * 2011-06-10 2019-01-08 Bharat Petroleum Corporation Limited Process for co-gasification of two or more carbonaceous feedstocks and apparatus thereof
US20140090298A1 (en) * 2011-06-10 2014-04-03 Bharat Petroleum Corporation Limited Process for co-gasification of two or more carbonaceous feedstocks and apparatus thereof
US9527026B2 (en) 2013-03-14 2016-12-27 Synthesis Energy Systems, Inc. Method and apparatus for recycling ash fines
CN104673397A (en) * 2015-01-26 2015-06-03 新奥科技发展有限公司 Fluidized bed gas distributor and gasifier
WO2016158918A1 (en) * 2015-03-30 2016-10-06 株式会社クボタ Gasification furnace, method of operating gasification furnace and biomass gasification treatment method
JP2016190887A (en) * 2015-03-30 2016-11-10 株式会社クボタ Gasification furnace, method for operating the gasification furnace, and biomass gasification treatment method
JP2016190889A (en) * 2015-03-30 2016-11-10 株式会社クボタ Gasification furnace and method for operating the gasification furnace
CN106010666A (en) * 2016-07-25 2016-10-12 上海锅炉厂有限公司 Circulating fluidized bed gasifying system and gasifying method thereof
JP2019094362A (en) * 2017-11-17 2019-06-20 三菱日立パワーシステムズ株式会社 Biomass gasification equipment and operation method thereof
JP7051384B2 (en) 2017-11-17 2022-04-11 三菱重工業株式会社 Biomass gasifier and its operation method
US20220340828A1 (en) * 2020-12-07 2022-10-27 Huaneng Clean Energy Research Institute Fly ash recycling gasification furnace
US11834617B2 (en) * 2020-12-07 2023-12-05 Huaneng Clean Energy Research Institute Fly ash recycling gasification furnace
US20230132767A1 (en) * 2021-10-29 2023-05-04 Simonpietri Enterprises LLC Processing and gasification of construction and demolition materials
US20240084207A1 (en) * 2021-10-29 2024-03-14 Simonpietri Enterprises LLC Processing and gasification of construction and demolition materials

Also Published As

Publication number Publication date
AU2011336788B2 (en) 2016-11-03
WO2012074942A3 (en) 2014-04-10
WO2012074942A2 (en) 2012-06-07
CN102477314A (en) 2012-05-30
CN102477314B (en) 2014-09-24
AU2011336788A1 (en) 2013-07-11

Similar Documents

Publication Publication Date Title
AU2011336788B2 (en) Method and apparatus for particle recycling in multiphase chemical reactors
US5154732A (en) Apparatus for gasifying or combusting solid carbonaceous
US4969930A (en) Process for gasifying or combusting solid carbonaceous material
US6283048B1 (en) Swirling-type melting furnace and method for gasifying wastes by the swirling-type melting furnace
EP0676464B1 (en) Method of and apparatus for fluidized-bed gasification and melt combustion
US9726369B2 (en) Chemical-looping combustion method with ashes and fines removal in the reduction zone and plant using same
KR102203125B1 (en) Second stage gasifier in staged gasification
US9181502B2 (en) Gasification of high ash, high ash fusion temperature bituminous coals
WO2007128370A1 (en) Process and plant for producing char and fuel gas
CN107043641B (en) Coal gasification method and device of circulating fluidized bed with fine ash return
US7503945B2 (en) Method and apparatus for gasifying carbonaceous material
US3847566A (en) Fluidized bed gasification process with reduction of fines entrainment by utilizing a separate transfer line burner stage
JP4660874B2 (en) Operation control method for waste two-stage gasification system
JP2573046B2 (en) Fluidized bed gasification method and fluidized bed gasification furnace
JP2004212032A (en) Fluidized bed gasification furnace
JP3938981B2 (en) Gas recycling method for waste gasification
CN112111304B (en) Fly ash circulating gasification system and recovery treatment method of fly ash in coal gas
CN214654699U (en) Gasification system for ultrafine particles of carbon-containing substance
JPH05156265A (en) Pneumatic bed gasifier
JP2008063185A (en) Method for producing synthesis gas
JP3941196B2 (en) Waste gasification method and apparatus
CN115466635B (en) Circulating fluidized bed gasification equipment
CA2151893A1 (en) Apparatus for separating solid particles from a gas and for injecting the so-separated particles into a reaction vessel
JPS58225191A (en) Coal gasification by fluidized bed and its apparatus
CN112442394A (en) Synthetic gas generating device and method for producing synthetic gas by high-temperature gasification of household garbage

Legal Events

Date Code Title Description
AS Assignment

Owner name: SYNTHESIS ENERGY SYSTEMS, INC., TEXAS

Free format text: ASSIGNMENT OF ASSIGNORS INTEREST;ASSIGNORS:XU, CHUNFA;WU, LONG;REEL/FRAME:045282/0283

Effective date: 20130208

STCB Information on status: application discontinuation

Free format text: ABANDONED -- FAILURE TO RESPOND TO AN OFFICE ACTION