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WO2020037905A1 - Gasification system and process for efficient heat energy recovery - Google Patents

Gasification system and process for efficient heat energy recovery Download PDF

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Publication number
WO2020037905A1
WO2020037905A1 PCT/CN2018/122283 CN2018122283W WO2020037905A1 WO 2020037905 A1 WO2020037905 A1 WO 2020037905A1 CN 2018122283 W CN2018122283 W CN 2018122283W WO 2020037905 A1 WO2020037905 A1 WO 2020037905A1
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Prior art keywords
heat exchange
gas
gasification
synthesis gas
water
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PCT/CN2018/122283
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French (fr)
Chinese (zh)
Inventor
赵静一
黄萍
毛炜
张燕
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北京航天迈未科技有限公司
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Publication of WO2020037905A1 publication Critical patent/WO2020037905A1/en

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    • 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
    • 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
    • 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
    • C10J3/72Other features
    • C10J3/86Other features combined with waste-heat boilers
    • 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
    • C10J2300/12Heating the gasifier
    • C10J2300/1269Heating the gasifier by radiating device, e.g. radiant tubes
    • 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
    • C10J2300/1603Integration of gasification processes with another plant or parts within the plant with gas treatment
    • C10J2300/1615Stripping
    • 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
    • C10J2300/1687Integration of gasification processes with another plant or parts within the plant with steam generation
    • 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
    • C10J2300/169Integration of gasification processes with another plant or parts within the plant with water treatments
    • 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
    • C10J2300/18Details of the gasification process, e.g. loops, autothermal operation
    • C10J2300/1807Recycle loops, e.g. gas, solids, heating medium, water
    • 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
    • Y02PCLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P20/00Technologies relating to chemical industry
    • Y02P20/10Process efficiency

Definitions

  • the invention belongs to the technical field of synthesis gas, and particularly relates to a gasification system and a process that can efficiently recover heat energy with chemical products, fuel gas and IGCC as targets.
  • the first process is represented by GE's coal water slurry water gasification-water quenching process.
  • the high-temperature synthesis gas (less than 1400 ° C) produced by the gasifier is cooled by a large amount of water and quickly cooled to 230 ⁇ 250 °C.
  • the cooled syngas is sent out after washing and dust removal (the temperature is further reduced to 210 ⁇ 240 °C).
  • Cooling water and washing dust removal water have a higher solid content and are called black water.
  • Most of the sensible heat of the synthesis gas enters the black water.
  • the black water enters the flash device for multi-stage flash evaporation. Part of the flash steam is used to directly or indirectly heat the black water, and the remaining steam is recovered after cooling by cooling water.
  • This water-chilling process has the advantage of simple operation, but most of the high-temperature heat energy in the process is converted to low-temperature heat energy, the energy utilization efficiency is low, the cooling water consumption is large, and because all ash and slag enter the water, the water system circulation amount Large, high power consumption.
  • the second process is mainly as follows: First, it is represented by Shell gasification technology, which mixes synthesis gas with low-temperature circulating gas on the top of the gasification furnace, and enters the waste pot for heat exchange after the temperature drops below 900 ° C.
  • the heat exchange is mainly convective heat exchange, but due to the high content of particles entrained in the gas, the waste pot is prone to blockage and abrasion.
  • a fly ash filter is used to perform gas-solid separation, and the separated dry ash is separated. High-pressure nitrogen is used for stripping and cooling.
  • This gasification technology has the advantages of simple high-pressure black water treatment and small circulation due to the dry ash removal.
  • the fly ash removal system used for dry ash removal is more complicated and difficult to operate. High, high-pressure nitrogen consumption, and low water-to-gas ratio of synthesis gas, it is difficult to meet the production requirements of chemical products.
  • the existing technology also has the technology represented by the GE waste pot process, which recovers the heat in the synthesis gas by setting up a waste waste pot section and a convection waste pot section, but the convection waste pot is prone to ash accumulation. It is difficult to guarantee long-term stable operation requirements.
  • Chinese patent document CN104017606B proposes a coal water slurry gasification process system based on the idea of cyclic gas quenching, which aims to solve the problem that a large amount of syngas in the coal water slurry gasification process system cannot be recovered.
  • the gasification furnace has an ascending structure. After the high temperature gas at the outlet of the combustion chamber is mixed with the low temperature circulating gas to cool down, it enters a heat exchanger (superheater) to superheat the saturated steam from the steam drum. Syngas then enters the second cyclone dust collector for the first gas-solid separation. Then, the synthesis gas enters the cooling device (including the superheater and two saturated steam generators), and continues to recover the heat in the synthesis gas.
  • a heat exchanger superheater
  • the cooled low-temperature synthesis gas enters the first cyclone dust collector, performs secondary gas-solid separation, and then removes most of the solid particles in the synthesis gas through a ceramic filter.
  • Part of the low-temperature synthesis gas coming out of the ceramic filter is returned to the gasifier as a chilled gas through the compressor, and part is sent out after being washed with water.
  • the dry ash collected by the two-stage cyclone is sent to the ash tank, which is cooled by the ash water and reduced in pressure, and then discharged into the slag-removing machine.
  • a plurality of slag cooling components are arranged inside the aforementioned heat exchanger and cooling device, which can scrape off the ash and slag on the inner surface of the heat exchange cavity to avoid the slag accumulation causing blockage of the heat exchanger.
  • the concentration of particles in the syngas entering the heat exchanger is very high, and there is still the possibility of abrasion and blockage of the heat exchanger.
  • the slag scraping cooling unit is a moving part, the working environment is harsh, and the failure rate is high.
  • the cooling synthesis gas pressurized circulation chilling method is used, because the coal-water slurry gasifies the synthesis gas in a large amount of CO 2 and water vapor, the combustion chamber outlet gas volume is about 1.2 times that of the Shell gasification chamber outlet gas volume.
  • the temperature of the chilled cycle synthesis gas is higher than that of Shell process, which results in the compression of the cycle gas compressor is much larger than that of Shell process, the compressor operating temperature is higher, and the energy consumption is higher.
  • Texaco Development's patent CN1037503C discloses a method for preparing cooling and cleaning synthesis gas to remove entrained particulate matter, which method includes flash evaporation, degassing, gas cooling and energy-saving filtration of wash water.
  • a) water-cooled direct contact cooling and b) indirect heat transfer (radiation and / or convection cooling) are mentioned.
  • a) method is used to cool high-temperature synthesis gas and high-temperature synthesis. Most of the sensible heat of gas enters low-temperature water, and energy waste is serious.
  • the b) method is used to cool the high-temperature synthesis gas.
  • the black water produced by the high-temperature synthesis gas can be degassed by three-stage flash steam. Specifically, the first-stage flash steam heats the grey water indirectly through the grey water heater, and the second-stage flash steam is mixed with the grey water in the deaerator. Direct contact removes dissolved oxygen in grey water, and all three-stage flash steam is cooled with cooling water.
  • the system In industrial applications, due to the large amount of high temperature sensible heat of the synthesis gas entering the black water and the large amount of black water discharge, the system often uses a 3-4 level flash evaporation system to recover the low temperature heat in the black water, and the system configuration is complicated.
  • the first-level flash steam contains a large amount of acidic gas (H 2 S, CO 2 etc.) and the suspended solids concentration, alkalinity and hardness in the gray water are very high, the problem of corrosion and scaling of the gray water heater is prominent, and the cost of equipment and materials It is expensive and difficult to guarantee long-term stable operation, and the running cost is high.
  • the final stage flash steam has a large amount, and all are cooled by cooling water, which consumes a large amount of cooling water.
  • US Patent No. 4,589,213 also discloses a system for preparing and purifying synthesis gas.
  • the high-temperature synthesis gas in the system is first mixed with the low-temperature synthesis gas from the cycle gas compressor.
  • the temperature after mixing should be as low as possible.
  • the molten fly ash particles are solidified.
  • the mixed gas entrained fly ash particles first enter the waste pot for heat recovery, and then enter the dry ash separation equipment (such as a cyclone separator) to separate most of the fine ash particles. Finally, the gas enters the wet washing system to further After washing and cooling, after cooling and heat exchange and acid gas removal, the product gas required by downstream users is obtained.
  • the black water obtained by cooling the slag and wet washing can be recycled after removing the acid gas dissolved therein by a stripping method.
  • This system adopts the method of circulating gas quenching and waste heat recovery, which can convert the high-temperature thermal energy in the synthesis gas into power steam, which has high useful work efficiency, but has the following problems in industrial applications: 1) In order to make high-temperature synthesis gas When the temperature drops to a suitable temperature, a large amount of circulating gas needs to be replenished. The circulating gas compressor has a high failure rate and high power consumption. 2) Syngas needs to be chilled to below 900 ° C and then enters the waste pot. It is mainly convective heat exchange.
  • Ceramic filters are usually used in solid separation in industrial applications, which are easy to damage and costly.
  • the separated fly ash needs a large amount of high-pressure nitrogen for stripping and cooling.
  • the entire fly ash removal system is complicated, the operation is difficult, and the high-pressure nitrogen consumption is large.
  • the invention solves the technical problems of low sensible heat recovery and utilization efficiency of the syngas gasification process and system in the prior art, severe waste pot abrasion, leading to short service life, and complex fly ash removal system.
  • This is a synthesis gasification system and process that can significantly reduce the sensible heat entering the black water, improve the use efficiency of the waste pot, and simplify the fly ash removal system.
  • a gasification system for efficient thermal energy recovery comprising: a gasification furnace for preparing syngas and performing radiation heat exchange, the gasification furnace comprising a gasification chamber and a radiation heat exchange chamber located downstream of the gasification chamber, A spraying device is provided on the heat exchange surface of the radiation heat exchange chamber to form a low temperature region close to the heat exchange surface and a core high temperature region located on the side of the low temperature region away from the heat exchange surface.
  • a chilled slag collecting device is provided downstream of the core high-temperature region, and the chilled slag collecting device contains a chilled liquid, and the chilled slag collecting device is provided with a black water discharge port; a gas-solid separation and cold ash device is connected with all The syngas outlet of the gasification furnace is provided in communication; a convective heat exchange device is in communication with the gas outlet of the gas-solid separation and cooling equipment for recovering the sensible heat of the synthesis gas and generating steam; a gas washing device is connected with the convection The gas outlet of the heat exchange device is connected and includes a Venturi scrubber and a washing tower arranged in series, and the washing tower is provided with a black water discharge port; the black water treatment system includes a first-stage flash evaporation device and a second-stage flash device arranged in series. Steaming device, Said slag quench means and said discharge port black water wash column with a flash device is connected to the set.
  • the gas-solid separation and cooling equipment includes a cyclone separator.
  • the convection heat exchange device includes a superheater, and a water-cooled heat exchange device is provided on the heat exchange surfaces of the gasification chamber and the radiation heat exchange chamber.
  • a steam outlet of the water-cooled heat exchange device is provided in communication with the superheater. The syngas enters the superheater to exchange heat with the steam, and heats the steam from the water-cooled heat exchange device to superheated steam.
  • the convective heat exchange device includes a superheater, a multi-stage saturated steam generator, and a boiler water preheater arranged in series, and the synthesis gas from the superheater enters the multistage saturated steam generator and the boiler water preheating in order. Device.
  • a condensing and separating device is provided in communication with the gas outlets of the first-level flashing device and the second-level flashing device, and the acid gas outlet of the condensing and separating device is connected to the acid gas processing device; it is in communication with the first-level flashing device
  • the liquid outlet of the condensing and separating device provided is in communication with the deaerator; the liquid exit of the secondary flashing device and the liquid and condensing device provided in communication with the secondary flashing device are in communication with the sedimentation tank.
  • a liquid outlet is in communication with the deaerator, and a filtering device is provided in connection with the solid discharge outlet of the sedimentation tank.
  • a gasification process for efficient thermal energy recovery includes: (1) gasification to prepare synthesis gas, and sending the synthesis gas to a radiation heat exchange chamber for heat exchange, and a spray is arranged on a heat exchange surface of the radiation heat exchange chamber;
  • the spraying device sprays fluid to form a low-temperature region close to the heat exchange surface and a core high-temperature region located on the side away from the heat exchange surface of the low-temperature region, and the syngas is heat-exchanged by the radiation heat exchange chamber
  • the temperature is lowered to above 700 ° C and discharged, and the high-temperature ash and slag in the synthesis gas are chilled with a chilled liquid to form black water discharge;
  • gas-solid separation is performed on the synthesis gas after heat exchange by the radiation heat exchange chamber , Cooling the separated fine ash;
  • step (4) the synthesis gas is washed until the particle content is less than or equal to 1 mg / Nm 3 .
  • step (1) the temperature in the low temperature region is less than 900 ° C, and the temperature in the core high temperature region is above 900 ° C.
  • step (2) the synthesis gas is subjected to gas-solid separation, and the particle size of the particles in the synthesis gas is controlled within a range of less than or equal to 5 ⁇ m.
  • step (2) the dry ash is cooled by a dry method.
  • step (3) The heat generated in the synthesis gas produced in step (1) and the heat generated in the radiant heat exchange chamber is heated by the heat exchange to face the water cooling medium to generate steam; in step (3), the synthesis gas and the steam are convected. Heat, the steam is heated into superheated steam with a pressure of 4.0-12 MPa and a temperature of 320-540 ° C.
  • the gas generated during the two-stage flash evaporation process in step (5) is condensed and separated, and the separated acid gas is sent to the downstream acid gas processing device, and the liquid separated and condensed after the first-stage flash evaporation is deoxidized;
  • the liquid separated by condensation after the first-stage flash evaporation and the remaining liquid after the second-stage flash evaporation are subjected to sedimentation treatment, and then subjected to oxygen removal treatment, and the solid produced by the sedimentation treatment is filtered.
  • the gasification furnace in the method of the present application adopts a radiant heat exchange chamber with a side zone temperature control technology, which can ensure the safety of heat exchange tubes, and also ensure higher heat recovery efficiency and high saturated steam output under high radiation intensity.
  • the equipment volume is smaller; compared with the heat recovery device adopting the overall water spray cooling method, the heat recovery rate of the radiant heat exchange chamber using the edge zone temperature control technology in this application can be increased by 10-50%.
  • This application uses a radiation + convection heat exchange device to recover the high-temperature waste heat in the synthesis gas, which further reduces the sensible heat entering the black water system. Compared with the water quenching process, the sensible heat transferred to the black water is reduced by about 49%. The load of the black water flash system is significantly reduced, and only a two-stage flash system needs to be configured. The first stage flash evaporation removes the dissolved acid gas in the black water, and the second stage flash evaporation reduces the temperature of the black water. This application adopts a dry cold ash process.
  • the total amount of ash entering the black water is only 45% of the water quench process, and the black water circulation is only the water quench process. 50%, the sensible heat taken away by black water is about 51% of the water chilling process, and the amount of circulating cooling water is reduced by about 50%.
  • the cyclone separation cooling device can be used to achieve the purpose of controlling the particle size of the fly ash in the synthesis gas and reducing the particle concentration.
  • the whirlwind can be first or second level. If a first-level cyclone configuration is adopted, the particle size of fly ash in the syngas can be controlled ⁇ 5 ⁇ m, which can effectively solve the problems of abrasion and blockage of the convection waste pot in the traditional process, and ensure long-term stable operation of the device. If a second-level cyclone configuration is used, It can control the particle size of fly ash in the synthesis gas ⁇ 1 ⁇ m, further reduce the particle concentration in the synthesis gas, reduce the ash removal load of the washing tower and the concentration of black water, improve water quality, and reduce waste water discharge.
  • the gas-solid separation device may be other separation methods such as a ceramic filter, a sintered metal filter, and an electrostatic precipitator.
  • the inner wall of the cyclone separator is provided with a water cooling coil, which can protect the outer wall of the cyclone from over-temperature, and can also produce saturated steam to recover part of the residual heat in the synthesis gas.
  • the synthesis gas can have a certain water-to-gas ratio, which can meet the downstream requirements for chemical products; the convection heat exchange device is configured to be superheated.
  • the generator + multi-stage saturated steam generator + boiler water heater the waste heat in the high-temperature synthesis gas can be recovered to the maximum, and the produced synthesis gas can meet the downstream requirements for fuel gas or IGCC.
  • FIG. 1 is a schematic flowchart of a gasification system for preparing downstream chemical products according to the present invention
  • FIG. 2 is a schematic structural diagram of a gasification furnace in a gasification system according to the present invention
  • FIG. 3 is a schematic structural diagram of a cross section at an inner cylinder of a radiation heat exchange chamber according to the present invention
  • FIG. 4 is a schematic structural view of a cross section at a throat passage of the heat exchange device according to the present invention.
  • FIG. 5 is a schematic flowchart of a gasification system for preparing a downstream fuel gas or an IGCC product according to the present invention.
  • 2-Gas-solid separation and cold ash equipment 21-Cyclone separator; 3-Convection heat exchange device; 31-Superheater; 32-Multi-stage saturated steam generator; 33-Boiler water preheater; 41- Venturi washing 42-washing tower; 51-first stage flash device; 52-second stage flash device; 61- condensation separation device connected to the first stage flash device; 62- deaerator; 63- connected to the second stage Condensation separation device after flash device; 64-settling tank; 65-ash water tank; 66-filtration device.
  • the gasification system includes a gasification furnace for preparing synthesis gas and performing radiation heat exchange.
  • the gasification furnace 1 includes a gasification chamber 11 and a radiation heat exchange chamber 12.
  • the gasification furnace 1 in this embodiment adopts a structure in which the gasification chamber 11 and the radiation heat exchange chamber 12 are integrated, as shown in FIG. 2 Show.
  • the radiation heat exchange chamber 12 described in this embodiment is disposed below the gasification chamber 11, and a raw material inlet 111 is provided on the top of the gasification chamber 11.
  • the radiation heat exchange chamber 12 includes an inner portion disposed in a casing.
  • the inner and outer side walls of the inner cylinder 126 and the inner side surface of the outer cylinder 124 are heat exchange surfaces.
  • the heat exchange surfaces of the gasification chamber 11 and the radiation heat exchange chamber 12 are provided.
  • the water-cooled heat exchange device described in this embodiment is a water-cooled pipe.
  • the heat in the gasification chamber 11 and the radiant heat exchange chamber 12 is exchanged with the water cooling medium in the water-cooled pipe through a heat exchange surface.
  • the water cooling medium in the water cooling pipe is evaporated to form steam, and the water cooling medium is boiler water.
  • the inner cylinder 126 and the outer cylinder 124 are both cylindrical cylinders.
  • the inner cylinder 126 and the outer cylinder 124 may also be provided as cylinders having a square cross-section or other arbitrary shapes. body.
  • An inlet of a radiation heat exchange chamber is provided at the top of the inner tube 126, and the inlet of the radiation heat exchange chamber is in communication with the outlet of the gasification chamber 11; a heat exchange surface upstream of the inner tube 126 is provided with a first
  • An injection device 121 forms a low-temperature area close to the heat exchange surface and a core high-temperature area located on a side of the low-temperature area away from the heat exchange surface, that is, inside.
  • the first spraying device 121 is preferably a first nozzle group, and the first nozzle group is arranged around a circle of the heat exchange surface upstream of the inner cylinder 126, and multiple layers or single layers can be provided along the fluid flow direction.
  • the direction of fluid flow in the embodiment is from top to bottom.
  • the first nozzle group is provided with three layers, and the adjacent two layers of nozzles are arranged in a staggered manner. As shown in FIG. 3, multiple nozzles in each layer of nozzles are evenly arranged, and each nozzle in each layer of sprays sprays.
  • the radius d 1 is greater than 0 and smaller than the equivalent radius of the inner cylinder where the nozzle is located.
  • the spray radius d 1 of each nozzle is greater than 0 and less than 60% of the equivalent radius of the inner cylinder 126 where the nozzle is located.
  • the spray radius d 1 of each nozzle is greater than 0 and less than 30% of the equivalent radius of the inner cylinder 126 where the nozzle is located, thereby helping to increase the volume of the core high-temperature region; each nozzle in each layer of the nozzle ejects The fluid flow converges with the fluid flow ejected from an adjacent nozzle located on the same layer at a first vertical distance d 1 from the position of the heat transfer surface, and the first vertical distance d 1 is greater than 0 and smaller than the spraying radius rs of the nozzle. 1 .
  • the nozzles between layers can also be arranged in a non-staggered manner; multiple nozzles in each layer of nozzles can also be arranged non-uniformly, and the nozzles between layers can spray out
  • the fluid streams may or may not converge with each other.
  • the fluid sprayed by the dispersed nozzle forms an effective isolation, thereby forming a low temperature region near the heat exchange surface.
  • the ash and slag particles entering the low temperature area lose their viscosity after cooling, and hard slag that is difficult to be removed will not be formed on the wall surface.
  • the core high temperature area still maintains a high temperature above 900 ° C, thereby maintaining a high radiation heat transfer capacity.
  • the method of cooling the edge region and the core high temperature in the present invention can effectively increase the radiant heat exchange amount.
  • a second injection device 113 is provided at the inlet of the radiation heat exchange chamber 12 or upstream of the inlet, and the second injection device 113 is preferably a second nozzle group.
  • the second nozzle group may be disposed at the entrance of the radiation heat exchange chamber 12 or may be disposed upstream of the entrance, that is, a throat between the gasification chamber 11 and the entrance of the radiation heat exchange chamber 12 Ministry channel 112.
  • the second spraying device 113 is preferably a second nozzle group. As shown in FIG. 4, the spraying radius rs 2 of the nozzles in the second nozzle group is greater than 50% (ie, 50%) of the radius at the throat passage 112.
  • the second nozzle group may be provided with a single layer or multiple layers, and the fluid flow ejected from each nozzle of each layer of nozzles is away from the heat exchange surface where it is located
  • the second vertical distance d 2 converges with the fluid flow ejected from an adjacent nozzle located on the same layer, and the distance d 2 is smaller than the spray radius of the nozzle.
  • a fluid passage is formed between the inner cylinder 126 and the outer cylinder 124, and the fluid enters the fluid passage downstream from the inner cylinder 126, that is, the bottom of the inner cylinder 126.
  • a third spraying device 122 is further provided on an inner wall surface of the inner cylinder 126 downstream of the first spraying device 121.
  • the third spraying device 122 is a third nozzle group.
  • the spray radius of each nozzle is 50% R to 90% R, where R is the equivalent radius of the inner cylinder 126 at the position where the nozzle is located.
  • a fourth spraying device is also provided on the fluid passage.
  • the fourth spraying device is preferably a fourth nozzle group, and the fourth nozzle group is distributed on the outer wall surface of the inner cylinder 126 or the corresponding outer cylinder.
  • the fourth nozzle group is disposed near the bottom ends of the inner tube 126 and the outer tube 124; and the outer tube 124 located downstream of the fourth nozzle group is provided with a radiation heat exchange chamber outlet 125.
  • the fluid sprayed by the first nozzle group, the second nozzle group, the third nozzle group, and the fourth nozzle group is a cooling liquid, specifically, boiler water.
  • the fluid is also It can be any one or more of nitrogen, carbon dioxide, cooled syngas, water vapor, and water.
  • a chilled slag collecting device is provided on the synthesis gas flow path of the radiation heat exchange chamber 12, and the role of the chilled slag collecting device is to water the high temperature ash and slag in the synthesis gas. It is chilled to remove it from the syngas.
  • the chilled slag collecting device is disposed downstream of a low-temperature region and a core high-temperature region formed by the first spraying device 121.
  • the chilled slag collection device uses a slag pool 13, which is disposed at the bottom of the radiation heat exchange chamber 12, and the slag pool 13 contains a chilled liquid.
  • the synthesis gas turns from the inner cylinder 126 to the outer cylinder 124.
  • the high-temperature slag enters the slag pool 13 under the action of gravity and is quickly cooled by the chilled liquid.
  • the slag pool 13 is provided with a black water discharge port.
  • the gas-solid separation and cold ash equipment 2 is provided in communication with the synthesis gas outlet of the gasification furnace 1.
  • the gas-solid separation and cooling equipment in this embodiment includes a cyclone separator 21 as an alternative embodiment, except for a cyclone
  • the separator 21 and the gas-solid separation device may be other separation devices such as a ceramic filter, a sintered metal filter, and an electrostatic precipitator.
  • the convective heat exchange device 3 is in communication with the gas outlet of the cyclone separator 21, and is used to recover the sensible heat of the syngas and generate power steam; the convective heat exchange device 3 in this embodiment is a superheater 31, and the gas
  • the steam outlet of the water-cooled heat exchange device of the chemical furnace 1 is arranged in communication with the superheater 31, and the synthesis gas enters the superheater 31 to exchange heat with the steam, and heats the steam from the water-cooled heat exchange device. For superheated steam.
  • a gas washing device which is arranged in communication with the gas outlet of the convection heat exchange device 3 and includes a Venturi scrubber 41 and a washing tower 42 arranged in series;
  • the black water treatment system includes a first-stage flash steaming device 51 and a second-stage flash steaming device 52 arranged in series.
  • the black water discharge ports of the gasification furnace 1 and the washing tower 42 are connected to the first-stage flash steaming device 51.
  • Condensation and separation devices 61 and 63 are respectively provided in communication with the gas outlets of the first-stage flash evaporation device 51 and the second-stage flash evaporation device 52.
  • the acid gas outlet of the condensation separation device is connected to the acid gas processing device, and the acid gas The processing device processes the acid gas discharged from the acid gas outlet.
  • a combustion treatment may be adopted; the liquid outlet and the deaerator 62 of the condensation separation device provided in communication with the first-stage flash evaporation device 51 Communication; the liquid outlet of the secondary flash device 52 and the condensation separation device provided in communication with the secondary flash device 52 are in communication with the sedimentation tank 64, and the liquid outlet of the sedimentation tank 64 and the deaerator 62 is provided in communication.
  • a gray water tank 65 for buffering is provided between the sedimentation tank 64 and the deaerator 62, and a filter is connected to the solid discharge port of the sedimentation tank 64.
  • Device 66, the liquid outlet of the filtering device 66 is provided in communication with the sedimentation tank 64, and is used for the backflow of part of the liquid.
  • the liquid outlet of the deaerator 62 in this embodiment is provided with two pipelines, one of which is in communication with the washing tower 42 for returning the liquid to the washing tower 42 as the washing liquid; the other is
  • the slag pool 13 is communicated, and after being boosted by a pump, it is sent into the chilled slag collection device for replenishing the chilled liquid in the slag pool 13 and maintaining the chilled liquid in the slag pool 13 to a certain amount.
  • the gasification agent and oxidant are sent to the gasification chamber 11 for gasification reaction to generate synthesis gas, wherein the gasification agent is a carbon-containing fuel, and the oxidant is an oxygen-containing gas and steam; the synthesis gas enters through the throat passage 112
  • the inner cylinder 126 of the radiation heat exchange chamber 12 is pre-cooled by using the second nozzle group spray fluid during the entry process, and the temperature of the fluid entering the inner cylinder 126 of the radiation heat exchange chamber 12 is controlled to be not higher than 1500 ° C.
  • Synthetic gas enters the inner cylinder 126, and the first spraying device 121 is used to spray fluid to keep the temperature in the low-temperature region of the radiation heat exchange chamber 12 lower than 900 ° C and the temperature in the core high-temperature region above 900 ° C. Ensure efficient heat exchange efficiency.
  • the equivalent radius of the core high-temperature region occupies 30% to 95% of the equivalent radius of the radiation heat exchange chamber 12 at the position where it is, and more preferably 30 to 60%.
  • the fluid that continues to descend from the low-temperature region and the core high-temperature region is cooled by the further injection of the third injection device 122, so that the overall cross-sectional temperature of the fluid is lowered, thereby reducing the viscosity, and preventing particles from turning into the outer cylinder from the inner cylinder 126.
  • the fourth nozzle group was further sprayed to reduce the temperature, so that the slag particles that were not sufficiently cooled were further cooled before they hit the wall surface. Reduce or prevent adhesion.
  • the liquid slag in the synthesis gas rapidly solidifies, and large ash and slag particles fall into the bottom slag pool 13, and pass through the slag breaker 14, the slag lock bucket 15 3.
  • the slag-fishing machine discharges, and the remaining part forms black water discharge.
  • the cyclone separator 21 is used to perform gas-solid separation on the synthesis gas that has been heat exchanged by the radiation heat exchange chamber 12, and the particle size of the synthesis gas is controlled within a range of less than or equal to 5 ⁇ m;
  • the cooling method is to cool the high-temperature dry ash separated by the cyclone separator 21.
  • the dry cooling refers to the convective heat exchange of high-temperature dry ash by using gas, circulating water, desalinated water, etc. as a cooling medium.
  • the ash separated by the cyclone which accounts for 90% of the total ash, can be recovered as dry ash.
  • the energy in the high-temperature dry ash can be further recovered, and the recovered energy can be further comprehensively used.
  • hot demineralized water can be used as steam Including make-up water, thermal circulating water can be used as hot water in the factory, and hot gas can be used to heat or dry the powder.
  • the superheater 31 is used to perform convective heat exchange treatment on the synthesis gas separated in step (2).
  • the synthesis gas is used as the heating medium in the superheater 31, and the steam generated by the gasification furnace 1 is subjected to superheat treatment.
  • the steam is heated into high-quality superheated steam with a pressure of 4.0-12MPa and a temperature of 320-540 ° C, so as to recover the sensible heat of the synthesis gas and generate high-quality power steam.
  • a superheater 31 is provided for heat exchange treatment.
  • the synthesis gas from 31 can be used for downstream preparation of chemical products.
  • venturi scrubber 41 and the washing tower 42 are used to sequentially wash the syngas after the convective heat exchange treatment in step (4), and the syngas is washed until the particle content is less than or equal to 1 mg / Nm 3 , and the washing water is formed.
  • step (1) and step (4) The black water generated in step (1) and step (4) is subjected to two-stage flash evaporation, and a condensation separation device is used to condense and separate the gas generated during the two-stage flash evaporation process, and the separated acid gas Combustion treatment is performed, and the liquid separated and condensed after the first stage flash evaporation is sent to the deaerator 62 for deaeration treatment; the liquid separated and condensed after the second stage flash evaporation and the remaining liquid after the second stage flashed enter the sedimentation tank first. 64.
  • the supernatant liquid after the sedimentation treatment is sent to the deaerator 62 for deoxygenation treatment, and the sedimented solid part generated by the sedimentation treatment is sent to the filtering device 66 for filtration, and the filtrate generated by the filtration is returned to the sedimentation tank 64;
  • the liquid from the deaerator 62 is returned to the washing tower 42 and the slag tank 13 to realize water recycling; part of the liquid discharged from the sedimentation tank is sent to the deaerator and part of it is returned to the slag lock hopper for promoting Slag discharge, part of the wastewater is formed to balance the dissolved salt in the grey water system.
  • This embodiment provides a high-efficiency thermal energy recovery gasification system that can be used to prepare downstream fuel gas or IGCC products.
  • the gasification system includes:
  • the gasification furnace 1 used for preparing syngas and performing radiative heat exchange the gasification furnace 1 described in this embodiment is the same as the embodiment 1.
  • the gas-solid separation and cold ash equipment 2 is provided in communication with the synthesis gas outlet of the gasification furnace 1.
  • the gas-solid separation and cooling equipment in this embodiment includes a cyclone separator 21.
  • This embodiment adopts a two-stage cyclone configuration. Can control fly ash particle size ⁇ 1 ⁇ m in syngas.
  • the convective heat exchange device 3 is in communication with the gas outlet of the cyclone separator 21 and is used to recover the sensible heat of the synthesis gas and generate power steam.
  • the convective heat exchange device 3 in this embodiment is a superheater 31, Multi-stage saturated steam generator 32 and boiler water preheater 33.
  • the steam outlet of the water-cooled heat exchange device of the gasification furnace 1 is provided in communication with the superheater 31, and the synthesis gas enters the superheater 31 to exchange heat with the steam to cool the water.
  • the steam from the heat exchange device is heated to superheated steam.
  • the synthesis gas After the synthesis gas comes out of the superheater 31, it enters the multi-stage saturated steam generator 32 and the boiler water preheater 33 in order to generate saturated steam and the boiler water. Preheating to further recover the heat in the synthesis gas, wherein the preheated boiler water is used as the water cooling medium in the gasifier 1 and the cooling liquid sprayed from the injection device; the multi-stage saturated steam generator 32 is suitable Any of two to four-stage saturated steam generators is used.
  • the gas washing device is arranged in communication with the gas outlet of the convective heat exchange device 3 and includes a Venturi scrubber 41 and a washing tower 42 arranged in series to wash the syngas that has completed convective heat exchange.
  • the black water treatment system includes a first-stage flash steaming device 51 and a second-stage flash steaming device 52 arranged in series.
  • the black water discharge ports of the gasification furnace 1 and the washing tower 42 are connected to the first-stage flash steaming device 51.
  • Settings A condensation separation device is provided in communication with the gas outlets of the first-stage flash evaporation device 51 and the second-stage flash evaporation device 52, and the acid gas outlet of the condensation separation device is connected to the acid gas processing device;
  • the liquid outlet of the condensation separation device provided in communication with the device 51 is in communication with the deaerator 62;
  • the liquid outlet of the secondary flash device 52 and the liquid separation in the condensation separation device provided in communication with the secondary flash device 52 are connected to the sedimentation tank 64
  • the liquid outlet of the sedimentation tank 64 is in communication with the deaerator 62.
  • a gray water tank for buffering is provided between the sedimentation tank 64 and the deaerator 62. 65.
  • a filtering device 66 is provided in connection with the solid discharge port of the sedimentation tank 64, and a liquid outlet of the filtering device 66 is provided in communication with the sedimentation tank 64 for returning part of the liquid.
  • the gasification agent and oxidant are sent to the gasification chamber 11 for gasification reaction to generate synthesis gas, wherein the gasification agent is a carbon-containing fuel, and the oxidant is an oxygen-containing gas and steam; the synthesis gas enters through the throat passage 112
  • the inner cylinder of the radiation heat exchange chamber 12 is pre-cooled by using the second nozzle group spray fluid during the entry process, and the temperature of the fluid entering the inner cylinder of the radiation heat exchange chamber 12 is controlled to be not higher than 1500 ° C;
  • the gas enters the inner cylinder, and the first spraying device 121 is used to spray the fluid to keep the temperature in the low temperature region of the radiation heat exchange chamber 123 lower than 900 ° C and the temperature in the core high temperature region above 900 ° C, thereby ensuring efficient Heat transfer efficiency.
  • the equivalent radius of the core high-temperature region occupies 30% to 95% of the equivalent radius of the radiation heat exchange chamber 12 at the position where it is, and more preferably 30 to 60%.
  • the fluid that continues to descend from the low-temperature region and the core high-temperature region is cooled by the further spraying effect of the third spraying device 122, so that the overall cross-sectional temperature of the fluid is lowered, thereby reducing the viscosity, and preventing particles from turning from the inner cylinder into the outer cylinder 124 When it collides with the wall surface, it enters between the inner cylinder and the outer cylinder 124, and then the fourth nozzle group is further sprayed to cool down, so that the slag particles that are not sufficiently cooled are further cooled before hitting the wall surface to reduce Or prevent adhesion.
  • the liquid slag in the synthesis gas rapidly solidifies, and large ash and slag particles fall into the bottom slag pool 13, and pass through the slag breaker 14, the slag lock bucket 15
  • the slag-fishing machine discharges, and the remaining part forms black water.
  • the cyclone separator 21 is used to perform gas-solid separation on the syngas that has been heat-exchanged by the radiation heat exchange chamber 12, and the particle size of the syngas is controlled to be less than or equal to 1 ⁇ m;
  • the separated fine ash is subjected to cooling treatment in a method, and the fine ash, which accounts for 90% of the total fine ash, is recovered in the form of dry ash.
  • step (3) Use the superheater 31 to perform convective heat exchange treatment on the synthesis gas separated in step (2), and send the synthesis gas to the superheater 31, the multi-stage saturated steam generator 32, and the boiler water preheater 33 in this order.
  • the steam generator and the boiler water preheater 33 the synthesis gas is used to generate power steam and saturated steam, and further preheat the boiler water, thereby fully recovering the sensible heat of the synthesis gas.
  • the superheater 31 in this embodiment performs a heat treatment on the steam generated by the gasification furnace 1 and the multi-stage saturated steam generator 32, and can heat the steam to a pressure of 4.0-12MPa and a temperature of 320-540 ° C. Superheated steam quality.
  • the Venturi scrubber 41 and the washing tower 42 are used to sequentially wash the syngas after the convective heat exchange treatment in step (4), and the syngas is washed to a particle content of 1 mg / Nm 3 or less, and the washing water is formed Black water.
  • the black water generated in steps (1) and (4) is subjected to a two-stage flash evaporation process, and a condensation separation device is used to condense and separate the gas generated during the two-stage flash evaporation process, and the separated acid gas Combustion treatment is performed, and the liquid separated and condensed after the first stage flash evaporation is sent to the deaerator 62 for deaeration treatment; the liquid separated and condensed after the second stage flash evaporation and the remaining liquid after the second stage flashed enter the sedimentation tank 64.
  • the supernatant liquid after the sedimentation treatment is sent to the deaerator 62 for deoxygenation treatment, and the sedimented solid part generated by the sedimentation treatment is sent to the filtering device 66 for filtration, and the filtrate generated by the filtration is returned to the sedimentation tank 64;
  • the liquid from the deaerator 62 is returned to the washing tower 42 and the slag tank 13 to realize water recycling.
  • the process system in the present application can effectively recover the high-temperature heat energy in the synthesis gas, with an output of (CO + H 2 ) of 100,000 Nm 3 / h, an average reaction temperature in the gasification chamber 11 of 1400 ° C., and an annual operating time.
  • the output values in Example 1 and Example 2 were estimated based on 8000 hours. The results are shown in the following table:
  • the price of 10MPag power steam is calculated at 120 yuan / ton, and the price of circulating cooling water is calculated at 0.1 yuan / ton.

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Abstract

A gasification system for efficient heat energy recovery, comprising a gasification furnace (1), a spray apparatus being disposed on a heat exchange surface within a radiation heat exchange chamber (12) of the gasification furnace (1) so as to form a low temperature area close to the heat exchange surface and a core high temperature area located on a side of the low temperature area that is far from the heat exchange surface; a gas-solid separation and ash cooling device (2) that is provided in communication with a syngas outlet of the gasification furnace (1); a convection heat exchange device (3) that is used for recovering sensible heat from a syngas and generating power steam; a gas washing device that comprises a venturi scrubber (41) and a washing tower (42) which are arranged in series; a black water treatment system that comprises a first-stage flash evaporation apparatus (51) and a second-stage flash evaporation apparatus (52) which are arranged in series. Further provided is a gasification process for efficient heat energy recovery, wherein the radiation heat exchange chamber (12) employing side zone temperature-control technology may ensure the safety of heat exchange tubes, and may also ensure that heat energy recovery efficiency is high under high radiation intensity; the present invention has high saturated steam yield and smaller equipment volume.

Description

一种高效热能回收的气化系统及工艺Gasification system and process for efficient thermal energy recovery 技术领域Technical field
本发明属于合成气技术领域,具体涉及以化工产品、燃料气和IGCC为目标的,可高效回收热能的气化系统及工艺。The invention belongs to the technical field of synthesis gas, and particularly relates to a gasification system and a process that can efficiently recover heat energy with chemical products, fuel gas and IGCC as targets.
背景技术Background technique
以煤、石油、煤焦等含碳物质为原料生产合成气(主要成分为CO和H 2)的气化技术,作为化石原料洁净利用的重要手段,已广泛应用于燃气、合成气、IGCC等领域。在气化反应过程中,含碳原料的化学能大部分转化为合成气的化学能,但仍有约20%的化学能转化为合成气和灰渣的显热,从而导致热量损失。如何提高这部分显热的回收和利用效率,对化工装置生产和节能降耗意义重大。 Gasification technology that uses coal, petroleum, coal coke and other carbonaceous materials as raw materials to produce syngas (mainly composed of CO and H 2 ), as an important means for the clean utilization of fossil raw materials, has been widely used in gas, syngas, IGCC, etc. field. During the gasification reaction, most of the chemical energy of the carbon-containing raw material is converted into the chemical energy of the synthesis gas, but about 20% of the chemical energy is still converted into the sensible heat of the synthesis gas and ash, resulting in heat loss. How to improve the recovery and utilization efficiency of this part of the sensible heat is of great significance to the production of chemical equipment and energy saving.
目前,对气化炉产生的高温合成气的热量回收工艺主要有两种,一种是通过快速冷却方法将高温合成气中的显热转移至黑水中,再对较低温的黑水进行热量的回收和综合利用,一种是利用废热锅炉回收合成气中的高温位热能。At present, there are mainly two heat recovery processes for the high-temperature synthesis gas produced by the gasification furnace. One is to transfer the sensible heat in the high-temperature synthesis gas to black water through a rapid cooling method, and then heat the lower temperature black water. Recovery and comprehensive utilization, one is to use waste heat boiler to recover high-temperature heat energy in syngas.
第一种工艺的代表为GE公司的水煤浆水气化-水激冷工艺,在该工艺中,气化炉产生的高温合成气(低于1400℃)经大量水冷却后,迅速降温至230~250℃,降温后的合成气经洗涤除尘(温度进一步降至210~240℃)后送出。冷却水和洗涤除尘水中的固含量较高,被称为黑水,合成气的显热大部分进入黑水中。黑水进入闪蒸装置进行多级闪蒸,闪蒸出的部分蒸汽用于对黑水进行直接或间接加热,剩余蒸汽则经冷却水冷却后回收。这种水激冷工艺具有操作简单的优点,但工艺中的高温位热能大部分转换为低温热能,能量利用效率较低,冷却水消耗量大,且由于灰渣全部进入水中,水系统循环量大,功耗较高。The first process is represented by GE's coal water slurry water gasification-water quenching process. In this process, the high-temperature synthesis gas (less than 1400 ° C) produced by the gasifier is cooled by a large amount of water and quickly cooled to 230 ~ 250 ℃. The cooled syngas is sent out after washing and dust removal (the temperature is further reduced to 210 ~ 240 ℃). Cooling water and washing dust removal water have a higher solid content and are called black water. Most of the sensible heat of the synthesis gas enters the black water. The black water enters the flash device for multi-stage flash evaporation. Part of the flash steam is used to directly or indirectly heat the black water, and the remaining steam is recovered after cooling by cooling water. This water-chilling process has the advantage of simple operation, but most of the high-temperature heat energy in the process is converted to low-temperature heat energy, the energy utilization efficiency is low, the cooling water consumption is large, and because all ash and slag enter the water, the water system circulation amount Large, high power consumption.
第二种工艺主要有以下几种:一是以壳牌气化技术为代表,该技术将合成气在气化炉顶部与低温循环气混合,温度降至900℃以下后进入废锅进行换热,换热以对流换热为主,但因气体中所夹带颗粒含量较高,废锅易出现堵塞和磨蚀现象,合成气出废锅后采用飞灰过滤器进行气固分离,分离出的干灰采用高 压氮气进行气提和冷却,该气化技术因采用干法除灰,具有高压黑水处理简单、循环量小的优点,但干法除灰采用的飞灰脱除系统较为复杂,操作难度高,且高压氮气的消耗量大,同时合成气水气比低,较难达到化工产品的生产要求。除了壳牌气化技术,现有技术还有以GE废锅流程为代表的技术,其通过设置辐射废锅段和对流废锅段回收合成气中的热量,但对流废锅易产生积灰现象,难以保证长周期稳定运行要求。The second process is mainly as follows: First, it is represented by Shell gasification technology, which mixes synthesis gas with low-temperature circulating gas on the top of the gasification furnace, and enters the waste pot for heat exchange after the temperature drops below 900 ° C. The heat exchange is mainly convective heat exchange, but due to the high content of particles entrained in the gas, the waste pot is prone to blockage and abrasion. After the syngas exits the waste pot, a fly ash filter is used to perform gas-solid separation, and the separated dry ash is separated. High-pressure nitrogen is used for stripping and cooling. This gasification technology has the advantages of simple high-pressure black water treatment and small circulation due to the dry ash removal. However, the fly ash removal system used for dry ash removal is more complicated and difficult to operate. High, high-pressure nitrogen consumption, and low water-to-gas ratio of synthesis gas, it is difficult to meet the production requirements of chemical products. In addition to Shell gasification technology, the existing technology also has the technology represented by the GE waste pot process, which recovers the heat in the synthesis gas by setting up a waste waste pot section and a convection waste pot section, but the convection waste pot is prone to ash accumulation. It is difficult to guarantee long-term stable operation requirements.
中国专利文件CN104017606B在循环气激冷思路的基础上,提出了一种水煤浆气化工艺系统,旨在解决水煤浆气化工艺系统中合成气的大量热能无法回收的问题。气化炉为上行结构,燃烧室出口的高温气体在上升管内与低温循环气混合降温后,进入换热器(过热器)将来自汽包的饱和蒸汽进行过热。随后合成气进入第二旋风除尘器,进行初次气固分离。然后,合成气进入冷却装置(含过热器和两个饱和蒸汽发生器),继续回收合成气中的热量。冷却后的低温合成气进入第一旋风除尘器,进行二次气固分离,再经陶瓷过滤器除去合成气中的绝大部分的固体颗粒。从陶瓷过滤器出来的低温合成气,一部分作为激冷气经过压缩机返回气化炉,一部分经水洗后送出。两级旋风收集的干灰送入灰罐经灰水降温并降压后排入捞渣机中。前述换热器和冷却装置内部设置多个挂渣冷却组件,可将换热腔内表面的灰渣刮落,以避免灰渣堆积造成换热器的阻塞。但该工艺中,二级旋风设置于换热器(过热器)之后,进入换热器的合成气中的颗粒浓度很高,仍有可能出现换热器磨蚀堵塞的情况。刮渣冷却组件为动部件,工作环境恶劣,故障率高。此外,采用冷却合成气加压循环激冷的方法,因水煤浆气化合成气中存在大量CO 2和水蒸气,燃烧室出口气量为壳牌气化室出口气量的约1.2倍,同时用于激冷的循环合成气温度较壳牌工艺更高,导致循环气压缩机压缩量远大于壳牌工艺,压缩机工作温度更加高、能耗更高。 Chinese patent document CN104017606B proposes a coal water slurry gasification process system based on the idea of cyclic gas quenching, which aims to solve the problem that a large amount of syngas in the coal water slurry gasification process system cannot be recovered. The gasification furnace has an ascending structure. After the high temperature gas at the outlet of the combustion chamber is mixed with the low temperature circulating gas to cool down, it enters a heat exchanger (superheater) to superheat the saturated steam from the steam drum. Syngas then enters the second cyclone dust collector for the first gas-solid separation. Then, the synthesis gas enters the cooling device (including the superheater and two saturated steam generators), and continues to recover the heat in the synthesis gas. The cooled low-temperature synthesis gas enters the first cyclone dust collector, performs secondary gas-solid separation, and then removes most of the solid particles in the synthesis gas through a ceramic filter. Part of the low-temperature synthesis gas coming out of the ceramic filter is returned to the gasifier as a chilled gas through the compressor, and part is sent out after being washed with water. The dry ash collected by the two-stage cyclone is sent to the ash tank, which is cooled by the ash water and reduced in pressure, and then discharged into the slag-removing machine. A plurality of slag cooling components are arranged inside the aforementioned heat exchanger and cooling device, which can scrape off the ash and slag on the inner surface of the heat exchange cavity to avoid the slag accumulation causing blockage of the heat exchanger. However, in this process, after the secondary cyclone is set in the heat exchanger (superheater), the concentration of particles in the syngas entering the heat exchanger is very high, and there is still the possibility of abrasion and blockage of the heat exchanger. The slag scraping cooling unit is a moving part, the working environment is harsh, and the failure rate is high. In addition, the cooling synthesis gas pressurized circulation chilling method is used, because the coal-water slurry gasifies the synthesis gas in a large amount of CO 2 and water vapor, the combustion chamber outlet gas volume is about 1.2 times that of the Shell gasification chamber outlet gas volume. The temperature of the chilled cycle synthesis gas is higher than that of Shell process, which results in the compression of the cycle gas compressor is much larger than that of Shell process, the compressor operating temperature is higher, and the energy consumption is higher.
德士古发展公司的专利CN1037503C公布了一种制备冷却和清洗合成气以除去所夹带的颗粒状物质的方法,该方法包括闪蒸、脱气、气体冷却和洗涤水的节能过滤。对高温气体合成气的冷却提到了a)水激冷直接接触降温和b)间接换热(辐射和/或对流冷却)两种方法,其中,采用a)方法对高温合成气进行冷却,高温合成气的显热大部分进入到低温水中,能量浪费严重。采用b) 方法对高温合成气进行冷却,因合成气中颗粒含量高,对流废锅磨蚀和积灰问题严重,则会导致装置长周期稳定运行困难。高温合成气产生的黑水可通过三级闪蒸进行脱气,具体为:一级闪蒸蒸汽通过灰水加热器间接换热加热灰水,二级闪蒸蒸汽在除氧器中与灰水直接接触去除灰水中溶解的氧气,三级闪蒸的蒸汽全部用冷却水冷却。在工业应用中,由于合成气高温显热大量进入黑水中,黑水排放量大,系统往往要采用3-4级闪蒸系统回收黑水中的低温热量,系统配置复杂。同时,由于一级闪蒸汽中含有大量酸性气体(H 2S和CO 2等)且灰水中悬浮物浓度、碱度和硬度都很高,灰水加热器腐蚀、结垢问题突出,设备材料费用昂贵且很难保证长周期稳定运行,运行费用高。末级闪蒸蒸汽量大,全部采用冷却水冷却,冷却水消耗量大。 Texaco Development's patent CN1037503C discloses a method for preparing cooling and cleaning synthesis gas to remove entrained particulate matter, which method includes flash evaporation, degassing, gas cooling and energy-saving filtration of wash water. For the cooling of high-temperature gas synthesis gas, a) water-cooled direct contact cooling and b) indirect heat transfer (radiation and / or convection cooling) are mentioned. Among them, a) method is used to cool high-temperature synthesis gas and high-temperature synthesis. Most of the sensible heat of gas enters low-temperature water, and energy waste is serious. The b) method is used to cool the high-temperature synthesis gas. Due to the high content of particles in the synthesis gas, the problems of abrasion and ash accumulation in the convection waste pot will cause serious long-term stable operation of the device. The black water produced by the high-temperature synthesis gas can be degassed by three-stage flash steam. Specifically, the first-stage flash steam heats the grey water indirectly through the grey water heater, and the second-stage flash steam is mixed with the grey water in the deaerator. Direct contact removes dissolved oxygen in grey water, and all three-stage flash steam is cooled with cooling water. In industrial applications, due to the large amount of high temperature sensible heat of the synthesis gas entering the black water and the large amount of black water discharge, the system often uses a 3-4 level flash evaporation system to recover the low temperature heat in the black water, and the system configuration is complicated. At the same time, because the first-level flash steam contains a large amount of acidic gas (H 2 S, CO 2 etc.) and the suspended solids concentration, alkalinity and hardness in the gray water are very high, the problem of corrosion and scaling of the gray water heater is prominent, and the cost of equipment and materials It is expensive and difficult to guarantee long-term stable operation, and the running cost is high. The final stage flash steam has a large amount, and all are cooled by cooling water, which consumes a large amount of cooling water.
除了上述冷却方法,美国专利US4859213还公开了一种有关合成气制备和净化工艺系统,该系统中的高温合成气首先与来自循环气压缩机的低温合成气混合,混合后的温度应低至可使熔融的飞灰颗粒固化,混合气夹带飞灰颗粒首先进入废锅进行热量回收,然后进入干灰分离设备(如旋风分离器)中分离出大部分细灰颗粒,最后气体进入湿洗系统进一步洗涤降温,最后经冷却换热及酸性气移除后,得到下游用户所需要的产品气。冷却灰渣和湿洗得到的黑水采用汽提方法除去其中溶解的酸性气后,可循环使用。该系统采用循环气激冷+废锅回收热量的方法,可将合成气中高温位热能可转化为动力蒸汽,有用功效率高,但在工业应用中存在以下问题:1)为使高温合成气温度降至适宜温度,需要补充大量的循环气,循环气压缩机昂贵故障率高,且功耗高;2)合成气需激冷至900℃以下后进入废锅,以对流换热为主,因气体中颗粒含量较高,易造成废锅堵塞和磨蚀;3)固体分离在工业应中通常采用陶瓷过滤器,易损坏且造价高昂。分离后的飞灰需消耗大量高压氮气进行气提和冷却。整个飞灰脱除系统复杂,操作难度高,高压氮气消耗量大。In addition to the above cooling method, US Patent No. 4,589,213 also discloses a system for preparing and purifying synthesis gas. The high-temperature synthesis gas in the system is first mixed with the low-temperature synthesis gas from the cycle gas compressor. The temperature after mixing should be as low as possible. The molten fly ash particles are solidified. The mixed gas entrained fly ash particles first enter the waste pot for heat recovery, and then enter the dry ash separation equipment (such as a cyclone separator) to separate most of the fine ash particles. Finally, the gas enters the wet washing system to further After washing and cooling, after cooling and heat exchange and acid gas removal, the product gas required by downstream users is obtained. The black water obtained by cooling the slag and wet washing can be recycled after removing the acid gas dissolved therein by a stripping method. This system adopts the method of circulating gas quenching and waste heat recovery, which can convert the high-temperature thermal energy in the synthesis gas into power steam, which has high useful work efficiency, but has the following problems in industrial applications: 1) In order to make high-temperature synthesis gas When the temperature drops to a suitable temperature, a large amount of circulating gas needs to be replenished. The circulating gas compressor has a high failure rate and high power consumption. 2) Syngas needs to be chilled to below 900 ° C and then enters the waste pot. It is mainly convective heat exchange. Due to the high content of particles in the gas, it is easy to cause waste pot clogging and abrasion; 3) Ceramic filters are usually used in solid separation in industrial applications, which are easy to damage and costly. The separated fly ash needs a large amount of high-pressure nitrogen for stripping and cooling. The entire fly ash removal system is complicated, the operation is difficult, and the high-pressure nitrogen consumption is large.
发明内容Summary of the Invention
本发明解决的是现有技术中的合成气气化工艺和系统的显热的回收和利用效率低、废锅磨蚀情况严重导致使用寿命短、飞灰脱除系统复杂的技术问题,进而提供一种能够显著降低进入黑水的显热、提高废锅使用效率、飞灰脱除系 统精简的合成气气化系统及工艺。The invention solves the technical problems of low sensible heat recovery and utilization efficiency of the syngas gasification process and system in the prior art, severe waste pot abrasion, leading to short service life, and complex fly ash removal system. This is a synthesis gasification system and process that can significantly reduce the sensible heat entering the black water, improve the use efficiency of the waste pot, and simplify the fly ash removal system.
本发明解决上述技术问题采用的技术方案为:The technical solutions adopted by the present invention to solve the above technical problems are:
一种高效热能回收的气化系统,包括:用于制备合成气和进行辐射换热的气化炉,所述气化炉包括气化室和位于所述气化室下游的辐射换热室,在所述辐射换热室内的换热面上设置有喷射装置,形成贴近换热面的低温区和位于所述低温区远离所述换热面一侧的核心高温区,在所述低温区和核心高温区的下游设置有激冷集渣装置,所述激冷集渣装置内存有激冷液,所述激冷集渣装置设置有黑水排放口;气固分离及冷灰设备,与所述气化炉的合成气出口连通设置;对流换热装置,与所述气固分离及冷却设备的气体出口连通,用于回收合成气的显热并产生蒸汽;气体洗涤设备,与所述对流换热装置的气体出口连通设置,包括串联设置的文丘里洗涤器和洗涤塔,所述洗涤塔设置有黑水排放口;黑水处理系统,包括串联设置的一级闪蒸装置和二级闪蒸装置,所述激冷集渣装置和所述洗涤塔的黑水排放口与所述一级闪蒸装置连接设置。A gasification system for efficient thermal energy recovery, comprising: a gasification furnace for preparing syngas and performing radiation heat exchange, the gasification furnace comprising a gasification chamber and a radiation heat exchange chamber located downstream of the gasification chamber, A spraying device is provided on the heat exchange surface of the radiation heat exchange chamber to form a low temperature region close to the heat exchange surface and a core high temperature region located on the side of the low temperature region away from the heat exchange surface. A chilled slag collecting device is provided downstream of the core high-temperature region, and the chilled slag collecting device contains a chilled liquid, and the chilled slag collecting device is provided with a black water discharge port; a gas-solid separation and cold ash device is connected with all The syngas outlet of the gasification furnace is provided in communication; a convective heat exchange device is in communication with the gas outlet of the gas-solid separation and cooling equipment for recovering the sensible heat of the synthesis gas and generating steam; a gas washing device is connected with the convection The gas outlet of the heat exchange device is connected and includes a Venturi scrubber and a washing tower arranged in series, and the washing tower is provided with a black water discharge port; the black water treatment system includes a first-stage flash evaporation device and a second-stage flash device arranged in series. Steaming device, Said slag quench means and said discharge port black water wash column with a flash device is connected to the set.
所述气固分离及冷却设备包括旋风分离器。The gas-solid separation and cooling equipment includes a cyclone separator.
所述对流换热装置包括过热器,所述气化室和辐射换热室的换热面上设置有水冷换热装置,所述水冷换热装置的蒸汽出口与所述过热器连通设置,所述合成气进入所述过热器与所述蒸汽进行换热,将所述水冷换热装置出来的蒸汽加热为过热蒸汽。The convection heat exchange device includes a superheater, and a water-cooled heat exchange device is provided on the heat exchange surfaces of the gasification chamber and the radiation heat exchange chamber. A steam outlet of the water-cooled heat exchange device is provided in communication with the superheater. The syngas enters the superheater to exchange heat with the steam, and heats the steam from the water-cooled heat exchange device to superheated steam.
所述对流换热装置包括串联设置的过热器、多级饱和蒸汽发生器和锅炉水预热器,由所述过热器出来的合成气依次进入所述多级饱和蒸汽发生器和锅炉水预热器。The convective heat exchange device includes a superheater, a multi-stage saturated steam generator, and a boiler water preheater arranged in series, and the synthesis gas from the superheater enters the multistage saturated steam generator and the boiler water preheating in order. Device.
与所述一级闪蒸装置和二级闪蒸装置的气体出口分别连通设置有冷凝分离装置,所述冷凝分离装置的酸性气体出口与酸性气体处理装置连接;与所述一级闪蒸装置连通设置的冷凝分离装置的液体出口与除氧器连通;所述二级闪蒸装置以及与所述二级闪蒸装置连通设置的冷凝分离装置的液体出口均与沉降槽连通,所述沉降槽的液体出口与所述除氧器连通设置与所述沉降槽的固体排出口连接设置有过滤装置。A condensing and separating device is provided in communication with the gas outlets of the first-level flashing device and the second-level flashing device, and the acid gas outlet of the condensing and separating device is connected to the acid gas processing device; it is in communication with the first-level flashing device The liquid outlet of the condensing and separating device provided is in communication with the deaerator; the liquid exit of the secondary flashing device and the liquid and condensing device provided in communication with the secondary flashing device are in communication with the sedimentation tank. A liquid outlet is in communication with the deaerator, and a filtering device is provided in connection with the solid discharge outlet of the sedimentation tank.
一种高效热能回收的气化工艺,包括:(1)气化制备合成气,将所述合成气送入辐射换热室进行换热,所述辐射换热室的换热面上设置有喷射装置,所述喷射装置喷射流体,形成贴近换热面的低温区和位于所述低温区远离所述换热面一侧的核心高温区,所述合成气经所述辐射换热室换热后温度降至700℃以上排出,利用激冷液对合成气中的高温灰渣进行激冷,形成黑水排出;(2)对经所述辐射换热室换热后的合成气进行气固分离,对分离出的细灰进行冷却处理;(3)对步骤(2)中分离出的合成气进行对流换热处理,回收合成气的显热并产生蒸汽;(4)对步骤(3)中对流换热处理后的合成气进行洗涤,洗涤液形成黑水排出;(5)对步骤(1)和步骤(4)中排出的黑水进行两级闪蒸处理。A gasification process for efficient thermal energy recovery includes: (1) gasification to prepare synthesis gas, and sending the synthesis gas to a radiation heat exchange chamber for heat exchange, and a spray is arranged on a heat exchange surface of the radiation heat exchange chamber; The spraying device sprays fluid to form a low-temperature region close to the heat exchange surface and a core high-temperature region located on the side away from the heat exchange surface of the low-temperature region, and the syngas is heat-exchanged by the radiation heat exchange chamber The temperature is lowered to above 700 ° C and discharged, and the high-temperature ash and slag in the synthesis gas are chilled with a chilled liquid to form black water discharge; (2) gas-solid separation is performed on the synthesis gas after heat exchange by the radiation heat exchange chamber , Cooling the separated fine ash; (3) performing convective heat exchange treatment on the synthesis gas separated in step (2) to recover the sensible heat of the synthesis gas and generating steam; (4) in step (3) The syngas after the convective heat exchange treatment is washed, and the washing liquid is discharged as black water; (5) The black water discharged in step (1) and step (4) is subjected to two-stage flash evaporation treatment.
步骤(4)中将合成气洗涤至颗粒含量小于或者等于1mg/Nm 3In step (4), the synthesis gas is washed until the particle content is less than or equal to 1 mg / Nm 3 .
步骤(1)中所述低温区的温度为小于900℃,所述核心高温区的温度在900℃以上。In step (1), the temperature in the low temperature region is less than 900 ° C, and the temperature in the core high temperature region is above 900 ° C.
步骤(2)中对所述合成气进行气固分离,将所述合成气中的颗粒粒径控制在小于或者等于5μm的范围内。In step (2), the synthesis gas is subjected to gas-solid separation, and the particle size of the particles in the synthesis gas is controlled within a range of less than or equal to 5 μm.
步骤(2)中采用干法方式实现对所述细灰的冷却处理。In step (2), the dry ash is cooled by a dry method.
步骤(1)中制备合成气产生的热量及辐射换热室内合成气的热量通过换热面对水冷却介质进行加热产生蒸汽;步骤(3)中将所述合成气与所述蒸汽进行对流换热,将所述蒸汽加热成压力为4.0-12MPa,温度为320-540℃的过热蒸汽。The heat generated in the synthesis gas produced in step (1) and the heat generated in the radiant heat exchange chamber is heated by the heat exchange to face the water cooling medium to generate steam; in step (3), the synthesis gas and the steam are convected. Heat, the steam is heated into superheated steam with a pressure of 4.0-12 MPa and a temperature of 320-540 ° C.
对步骤(5)中两级闪蒸处理过程中产生的气体进行冷凝分离,分离出的酸性气体送下游的酸性气体处理装置,对一级闪蒸后冷凝分离出的液体进行除氧处理;二级闪蒸后冷凝分离出的液体与二级闪蒸后的剩余液体经沉降处理后,再进行除氧处理,对沉降处理产生的固体进行过滤。The gas generated during the two-stage flash evaporation process in step (5) is condensed and separated, and the separated acid gas is sent to the downstream acid gas processing device, and the liquid separated and condensed after the first-stage flash evaporation is deoxidized; The liquid separated by condensation after the first-stage flash evaporation and the remaining liquid after the second-stage flash evaporation are subjected to sedimentation treatment, and then subjected to oxygen removal treatment, and the solid produced by the sedimentation treatment is filtered.
本申请中的高效热能回收的气化系统及其工艺,优点在于:The gasification system and technology for high-efficiency heat recovery in the present application have the following advantages:
(1)本申请方式中的气化炉,采用边区控温技术的辐射换热室,即可保 证换热管的安全,又可保证高辐射强度下热量回收效率更高,饱和蒸汽产量高,设备体积更小;相比于采用整体喷水降温方式的热回收装置,本申请中采用边区控温技术的辐射换热室的热回收率可提高10-50%。(1) The gasification furnace in the method of the present application adopts a radiant heat exchange chamber with a side zone temperature control technology, which can ensure the safety of heat exchange tubes, and also ensure higher heat recovery efficiency and high saturated steam output under high radiation intensity. The equipment volume is smaller; compared with the heat recovery device adopting the overall water spray cooling method, the heat recovery rate of the radiant heat exchange chamber using the edge zone temperature control technology in this application can be increased by 10-50%.
本申请采用辐射+对流换热装置回收合成气中的高温余热,进一步使进入黑水系统中的显热减少,与水激冷流程相比,转移到黑水中的显热降低了约49%,黑水闪蒸系统负荷显著降低,仅需配置两级闪蒸系统即可。一级闪蒸除去黑水中溶解的酸性气体,二级闪蒸降低黑水温度。本申请采用干法冷灰流程,因90%的细灰以干灰形式回收,进入到黑水中的总灰量仅为水激冷流程的45%,则黑水循环量仅为水激冷流程的50%,黑水带走显热约为水激冷流程的51%,循环冷却水用量减少约50%。This application uses a radiation + convection heat exchange device to recover the high-temperature waste heat in the synthesis gas, which further reduces the sensible heat entering the black water system. Compared with the water quenching process, the sensible heat transferred to the black water is reduced by about 49%. The load of the black water flash system is significantly reduced, and only a two-stage flash system needs to be configured. The first stage flash evaporation removes the dissolved acid gas in the black water, and the second stage flash evaporation reduces the temperature of the black water. This application adopts a dry cold ash process. Because 90% of the fine ash is recovered in the form of dry ash, the total amount of ash entering the black water is only 45% of the water quench process, and the black water circulation is only the water quench process. 50%, the sensible heat taken away by black water is about 51% of the water chilling process, and the amount of circulating cooling water is reduced by about 50%.
(2)通过设置旋风分离冷却装置,可实现分级控制合成气中飞灰粒径和降低颗粒浓度的目的。旋风可以为一级,也可以为二级。如采用一级旋风配置,可控制合成气中飞灰粒径≤5μm,可有效解决传统流程中对流废锅磨蚀和堵塞的问题,保证装置的长周期稳定运行;如采用二级旋风配置,则可控制合成气中飞灰粒径≤1μm,进一步降低合成气中颗粒浓度,降低洗涤塔除灰负荷和黑水浓度,改善水质,减少废水排放量。作为可选择的实施方式,气固分离装置也可以是陶瓷过滤器、烧结金属过滤器、静电除尘器等其它分离方法。(2) The cyclone separation cooling device can be used to achieve the purpose of controlling the particle size of the fly ash in the synthesis gas and reducing the particle concentration. The whirlwind can be first or second level. If a first-level cyclone configuration is adopted, the particle size of fly ash in the syngas can be controlled ≤5μm, which can effectively solve the problems of abrasion and blockage of the convection waste pot in the traditional process, and ensure long-term stable operation of the device. If a second-level cyclone configuration is used, It can control the particle size of fly ash in the synthesis gas ≤1μm, further reduce the particle concentration in the synthesis gas, reduce the ash removal load of the washing tower and the concentration of black water, improve water quality, and reduce waste water discharge. As an alternative embodiment, the gas-solid separation device may be other separation methods such as a ceramic filter, a sintered metal filter, and an electrostatic precipitator.
本申请进一步限定采用干法方式进行气固分离和冷却,系统配置和操作简单,设备投资小,共用工程消耗低。旋风分离器内壁设水冷盘管,即可保护旋风外壁不超温,又可产出饱和蒸汽回收部分合成气中的余热。This application further restricts the use of a dry method for gas-solid separation and cooling, simple system configuration and operation, small equipment investment, and low shared engineering consumption. The inner wall of the cyclone separator is provided with a water cooling coil, which can protect the outer wall of the cyclone from over-temperature, and can also produce saturated steam to recover part of the residual heat in the synthesis gas.
(3)本申请中的所述对流换热装置仅配置过热器时,可使得合成气具有一定的水气比,满足下游以做化工产品为目标的要求;所述对流换热装置配置为过热器+多级饱和蒸汽发生器+锅炉水加热器时,则可最大限度回收高温合成气中的余热,产出的合成气满足下游以做燃料气或IGCC为目标的要求。(3) When the convection heat exchange device in this application is only equipped with a superheater, the synthesis gas can have a certain water-to-gas ratio, which can meet the downstream requirements for chemical products; the convection heat exchange device is configured to be superheated. When the generator + multi-stage saturated steam generator + boiler water heater, the waste heat in the high-temperature synthesis gas can be recovered to the maximum, and the produced synthesis gas can meet the downstream requirements for fuel gas or IGCC.
(4)本申请中所述系统和工艺具有高动力蒸汽产出。当所述对流换热装置仅配置过热器时,每1000Nm 3(CO+H 2)可外送0.5-0.65吨过热蒸汽;当所述对流换热装置配置为过热器+多级饱和蒸汽发生器+锅炉水加热器时,每 1000Nm 3(CO+H 2)可外送0.7-0.8吨过热蒸汽。 (4) The systems and processes described in this application have high power steam output. When the convection heat exchange device is only equipped with a superheater, 0.5-0.65 tons of superheated steam can be delivered per 1000Nm 3 (CO + H 2 ); when the convection heat exchange device is configured as a superheater + a multi-stage saturated steam generator + Boiler water heater can deliver 0.7-0.8 tons of superheated steam per 1000Nm 3 (CO + H 2 ).
为了使本发明所述的高效热能回收的气化系统及工艺的技术方案更加清楚明白,以下结合具体附图和实施例,对本发明进行进一步详细说明。In order to make the technical scheme of the highly efficient thermal energy recovery gasification system and process described in the present invention clearer, the present invention will be further described in detail below with reference to specific drawings and embodiments.
附图说明BRIEF DESCRIPTION OF THE DRAWINGS
如图1所示是本发明所述的用于制备下游化工产品的气化系统的流程示意图;FIG. 1 is a schematic flowchart of a gasification system for preparing downstream chemical products according to the present invention;
如图2所示是本发明所述的气化系统中的气化炉的结构示意图;FIG. 2 is a schematic structural diagram of a gasification furnace in a gasification system according to the present invention;
如图3所示为本发明所述的辐射换热室的内筒处的截面的结构示意图;FIG. 3 is a schematic structural diagram of a cross section at an inner cylinder of a radiation heat exchange chamber according to the present invention;
如图4所示为本发明所述的换热装置的喉部通道处的截面的结构示意图;FIG. 4 is a schematic structural view of a cross section at a throat passage of the heat exchange device according to the present invention;
如图5所示是本发明所述的用于制备下游燃料气或IGCC产品的气化系统的流程示意图。FIG. 5 is a schematic flowchart of a gasification system for preparing a downstream fuel gas or an IGCC product according to the present invention.
其中,附图标记为:Among them, the reference numerals are:
1-气化炉;11-气化室;111-原料入口;112-喉部通道;113-第二喷射装置;1- gasification furnace; 11- gasification chamber; 111- raw material inlet; 112- throat passage; 113- second injection device;
12-辐射换热室;12- Radiation heat exchange chamber;
121-第一喷射装置;122-第三喷射装置;124-外筒;125-辐射换热室出口;126-内筒;121-first injection device; 122-third injection device; 124-outer tube; 125-radiation heat exchange chamber outlet; 126-inner tube;
13-渣池;14-破渣机;15-渣锁斗;13-slag tank; 14-slag breaker; 15-slag lock bucket;
2-气固分离及冷灰设备;21-旋风分离器;3-对流换热装置;31-过热器;32-多级饱和蒸汽发生器;33-锅炉水预热器;41-文丘里洗涤器;42-洗涤塔;51-一级闪蒸装置;52-二级闪蒸装置;61-连接在一级闪蒸装置后的冷凝分离装置;62-除氧器;63-连接在二级闪蒸装置后的冷凝分离装置;64-沉降槽;65-灰水槽;66-过滤装置。2-Gas-solid separation and cold ash equipment; 21-Cyclone separator; 3-Convection heat exchange device; 31-Superheater; 32-Multi-stage saturated steam generator; 33-Boiler water preheater; 41- Venturi washing 42-washing tower; 51-first stage flash device; 52-second stage flash device; 61- condensation separation device connected to the first stage flash device; 62- deaerator; 63- connected to the second stage Condensation separation device after flash device; 64-settling tank; 65-ash water tank; 66-filtration device.
具体实施方式detailed description
实施例1Example 1
本实施例提供了一种高效热能回收的气化系统,可用于制备下游的化工产品,如图1所示,所述气化系统包括:用于制备合成气和进行辐射换热的气化炉1,所述气化炉1包括气化室11和辐射换热室12,本实施例中所述气化炉1采用气化室11和辐射换热室12一体设置的结构,如图2所示。This embodiment provides a gasification system for efficient thermal energy recovery, which can be used to prepare downstream chemical products. As shown in FIG. 1, the gasification system includes a gasification furnace for preparing synthesis gas and performing radiation heat exchange. 1. The gasification furnace 1 includes a gasification chamber 11 and a radiation heat exchange chamber 12. The gasification furnace 1 in this embodiment adopts a structure in which the gasification chamber 11 and the radiation heat exchange chamber 12 are integrated, as shown in FIG. 2 Show.
本实施例中所述的辐射换热室12设置在所述气化室11的下方,在气化室11的顶部设置有原料入口111,所述辐射换热室12包括设置在壳体内的内筒126与外筒124;所述内筒126的内侧和外侧壁面与外筒124的内侧壁面均为换热面,在所述气化室11和辐射换热室12的换热面上设置有水冷换热装置,本实施方式中所述的水冷换热装置为水冷管,所述气化室11和辐射换热室12内的热量通过换热面与水冷管中的水冷却介质进行换热,所述水冷管内的水冷却介质蒸发形成蒸汽,所述水冷却介质采用的是锅炉水。The radiation heat exchange chamber 12 described in this embodiment is disposed below the gasification chamber 11, and a raw material inlet 111 is provided on the top of the gasification chamber 11. The radiation heat exchange chamber 12 includes an inner portion disposed in a casing. The inner and outer side walls of the inner cylinder 126 and the inner side surface of the outer cylinder 124 are heat exchange surfaces. The heat exchange surfaces of the gasification chamber 11 and the radiation heat exchange chamber 12 are provided. A water-cooled heat exchange device. The water-cooled heat exchange device described in this embodiment is a water-cooled pipe. The heat in the gasification chamber 11 and the radiant heat exchange chamber 12 is exchanged with the water cooling medium in the water-cooled pipe through a heat exchange surface. The water cooling medium in the water cooling pipe is evaporated to form steam, and the water cooling medium is boiler water.
本实施例中的所述内筒126与外筒124均为圆柱形筒体,作为可选择的实施方式,所述内筒126与外筒124也可设置为截面为方形或其它任意形状的筒体。在所述内筒126的顶端设置有辐射换热室入口,所述辐射换热室入口与所述气化室11出口连通设置;在所述内筒126的上游的换热面上设置有第一喷射装置121,形成贴近所述换热面的低温区和位于低温区远离所述换热面一侧即内侧的核心高温区,由于本实施方式中所述内筒126的换热面为筒体,因此形成的核心高温区位于筒体内的中间位置。所述第一喷射装置121优选为第一喷嘴组,所述第一喷嘴组环绕所述内筒126的上游的换热面的一周设置,且可沿流体流动方向设置多层或者单层,本实施方式中的流体流动方向为由上向下。本实施方式中述第一喷嘴组设置有3层,相邻2层喷嘴采用交错排列,如图3所示,每层喷嘴中的多个喷嘴均匀设置,每层喷嘴中的每个喷嘴的喷射半径d 1大于0且小于喷嘴所在处内筒的当量半径,作为优选的实施方式,所述每个喷嘴的喷射半径d 1大于0且小于喷嘴所在处内筒126的当量半径的60%,更优选地,所述每个喷嘴的喷射半径d 1大于0且小于喷嘴所在处内筒126的当量半径的30%,从而有利于提高核心高温区的体积;每层喷嘴中的每个喷嘴喷出的流体流在距离其所在换热面位置第一垂直距离d 1处与位于同一层的相邻喷嘴喷出的流体流汇聚,所述第一垂直距离d 1大于0且小于喷嘴的喷射半径 rs 1。作为可选择的实施方式,层与层之间的所述喷嘴也可采用非交错排列方式;每层喷嘴中的多个喷嘴也可采用非均匀设置,层与层之间的所述喷嘴喷射出的流体流可汇聚,也可相互不汇聚。本实施方式中,分散式的喷嘴喷出的流体形成一个有效隔离,从而在贴近换热面处形成低温区。进入低温区的灰渣颗粒经冷却后失去粘性,不会在壁面形成难以清除的硬渣;同时,核心高温区仍保持900℃以上的高温,从而保持较高的辐射换热能力。因为核心高温区的辐射换热量占辐射换热室12总换热量的大部分,相对于合成气整体降温方法,本发明中的边区降温、核心高温的方法可以有效地提高射换热量。 In this embodiment, the inner cylinder 126 and the outer cylinder 124 are both cylindrical cylinders. As an optional implementation manner, the inner cylinder 126 and the outer cylinder 124 may also be provided as cylinders having a square cross-section or other arbitrary shapes. body. An inlet of a radiation heat exchange chamber is provided at the top of the inner tube 126, and the inlet of the radiation heat exchange chamber is in communication with the outlet of the gasification chamber 11; a heat exchange surface upstream of the inner tube 126 is provided with a first An injection device 121 forms a low-temperature area close to the heat exchange surface and a core high-temperature area located on a side of the low-temperature area away from the heat exchange surface, that is, inside. Since the heat exchange surface of the inner cylinder 126 in this embodiment is a cylinder Body, so the core high temperature zone formed is located in the middle of the barrel. The first spraying device 121 is preferably a first nozzle group, and the first nozzle group is arranged around a circle of the heat exchange surface upstream of the inner cylinder 126, and multiple layers or single layers can be provided along the fluid flow direction. The direction of fluid flow in the embodiment is from top to bottom. In this embodiment, the first nozzle group is provided with three layers, and the adjacent two layers of nozzles are arranged in a staggered manner. As shown in FIG. 3, multiple nozzles in each layer of nozzles are evenly arranged, and each nozzle in each layer of sprays sprays. The radius d 1 is greater than 0 and smaller than the equivalent radius of the inner cylinder where the nozzle is located. As a preferred embodiment, the spray radius d 1 of each nozzle is greater than 0 and less than 60% of the equivalent radius of the inner cylinder 126 where the nozzle is located. Preferably, the spray radius d 1 of each nozzle is greater than 0 and less than 30% of the equivalent radius of the inner cylinder 126 where the nozzle is located, thereby helping to increase the volume of the core high-temperature region; each nozzle in each layer of the nozzle ejects The fluid flow converges with the fluid flow ejected from an adjacent nozzle located on the same layer at a first vertical distance d 1 from the position of the heat transfer surface, and the first vertical distance d 1 is greater than 0 and smaller than the spraying radius rs of the nozzle. 1 . As an alternative embodiment, the nozzles between layers can also be arranged in a non-staggered manner; multiple nozzles in each layer of nozzles can also be arranged non-uniformly, and the nozzles between layers can spray out The fluid streams may or may not converge with each other. In this embodiment, the fluid sprayed by the dispersed nozzle forms an effective isolation, thereby forming a low temperature region near the heat exchange surface. The ash and slag particles entering the low temperature area lose their viscosity after cooling, and hard slag that is difficult to be removed will not be formed on the wall surface. At the same time, the core high temperature area still maintains a high temperature above 900 ° C, thereby maintaining a high radiation heat transfer capacity. Because the radiant heat exchange amount in the core high-temperature region accounts for most of the total heat exchange amount in the radiant heat exchange chamber 12, compared with the overall temperature reduction method of the synthesis gas, the method of cooling the edge region and the core high temperature in the present invention can effectively increase the radiant heat exchange amount. .
作为优选的实施方式,在所述辐射换热室12的入口处或入口的上游设置有第二喷射装置113,所述第二喷射装置113优选为第二喷嘴组。所述第二喷嘴组可以设置在所述辐射换热室12的入口处,也可以设置在所述入口的上游,即所述气化室11与所述辐射换热室12入口之间的喉部通道112上。所述第二喷射装置113优选为第二喷嘴组,如图4所示,所述第二喷嘴组中喷嘴的喷射半径rs 2大于所述喉部通道112处的半径的50%(即50%R 2)小于所述喉部通道112处的半径R 2,所述第二喷嘴组可设置单层或者多层,每一层喷嘴的每个喷嘴喷出的流体流在距离其所在换热面第二垂直距离d 2处与位于同一层的相邻喷嘴喷出的流体流汇聚,所述距离d 2小于喷嘴的喷射半径。从而实现整体截面的降温所述第二喷嘴组沿所述喉部通道112的周向均匀设置。 As a preferred embodiment, a second injection device 113 is provided at the inlet of the radiation heat exchange chamber 12 or upstream of the inlet, and the second injection device 113 is preferably a second nozzle group. The second nozzle group may be disposed at the entrance of the radiation heat exchange chamber 12 or may be disposed upstream of the entrance, that is, a throat between the gasification chamber 11 and the entrance of the radiation heat exchange chamber 12 Ministry channel 112. The second spraying device 113 is preferably a second nozzle group. As shown in FIG. 4, the spraying radius rs 2 of the nozzles in the second nozzle group is greater than 50% (ie, 50%) of the radius at the throat passage 112. R 2 ) is smaller than the radius R 2 at the throat passage 112, the second nozzle group may be provided with a single layer or multiple layers, and the fluid flow ejected from each nozzle of each layer of nozzles is away from the heat exchange surface where it is located The second vertical distance d 2 converges with the fluid flow ejected from an adjacent nozzle located on the same layer, and the distance d 2 is smaller than the spray radius of the nozzle. Thereby, the overall cross-section is cooled, and the second nozzle group is uniformly disposed along the circumferential direction of the throat passage 112.
本实施例中所述内筒126与外筒124之间形成流体通道,所述流体由所述内筒126的下游即所述内筒126的底部进入所述流体通道。在所述内筒126位于所述第一喷射装置121的下游的内壁面上还设置有第三喷射装置122,所述第三喷射装置122为第三喷嘴组,所述第三喷嘴组中每个喷嘴的喷射半径为50%R~90%R,其中R为喷嘴所在位置处的内筒126的当量半径。In this embodiment, a fluid passage is formed between the inner cylinder 126 and the outer cylinder 124, and the fluid enters the fluid passage downstream from the inner cylinder 126, that is, the bottom of the inner cylinder 126. A third spraying device 122 is further provided on an inner wall surface of the inner cylinder 126 downstream of the first spraying device 121. The third spraying device 122 is a third nozzle group. The spray radius of each nozzle is 50% R to 90% R, where R is the equivalent radius of the inner cylinder 126 at the position where the nozzle is located.
在所述流体通道上还设置有第四喷射装置,所述第四喷射装置优选为第四喷嘴组,所述第四喷嘴组分布在所述内筒126的外壁面或对应的所述外筒124的内壁面上,所述第四喷嘴组靠近所述内筒126和外筒124的底端设置;在位于所述第四喷嘴组下游的外筒124上设置有辐射换热室出口125。A fourth spraying device is also provided on the fluid passage. The fourth spraying device is preferably a fourth nozzle group, and the fourth nozzle group is distributed on the outer wall surface of the inner cylinder 126 or the corresponding outer cylinder. On the inner wall surface of 124, the fourth nozzle group is disposed near the bottom ends of the inner tube 126 and the outer tube 124; and the outer tube 124 located downstream of the fourth nozzle group is provided with a radiation heat exchange chamber outlet 125.
本实施例中的第一喷嘴组、第二喷嘴组、第三喷嘴组和第四喷嘴组喷出的流体采用的是冷却液,具体为锅炉水,作为可选择的实施方式,所述流体也可以为氮气、二氧化碳、冷却后的合成气、水蒸气、水中的任意一种或多种的组合。In this embodiment, the fluid sprayed by the first nozzle group, the second nozzle group, the third nozzle group, and the fourth nozzle group is a cooling liquid, specifically, boiler water. As an alternative embodiment, the fluid is also It can be any one or more of nitrogen, carbon dioxide, cooled syngas, water vapor, and water.
本实施例中的气化炉1,在所述辐射换热室12的合成气流动路径上设置有激冷集渣装置,激冷集渣装置的作用在于对合成气中的高温灰渣进行水激冷,从而将其从合成气中去除。所述激冷集渣装置设置在所述第一喷射装置121形成的低温区和核心高温区的下游。本实施方式中所述所述激冷集渣装置采用的是渣池13,所述渣池13设置在所述辐射换热室12的底部,所述渣池13内存有激冷液,所述合成气由内筒126进入外筒124时发生转折,高温灰渣在重力作用下进入渣池13,快速被激冷液冷却,所述渣池13设置有黑水排放口。In the gasification furnace 1 in this embodiment, a chilled slag collecting device is provided on the synthesis gas flow path of the radiation heat exchange chamber 12, and the role of the chilled slag collecting device is to water the high temperature ash and slag in the synthesis gas. It is chilled to remove it from the syngas. The chilled slag collecting device is disposed downstream of a low-temperature region and a core high-temperature region formed by the first spraying device 121. In the present embodiment, the chilled slag collection device uses a slag pool 13, which is disposed at the bottom of the radiation heat exchange chamber 12, and the slag pool 13 contains a chilled liquid. The synthesis gas turns from the inner cylinder 126 to the outer cylinder 124. The high-temperature slag enters the slag pool 13 under the action of gravity and is quickly cooled by the chilled liquid. The slag pool 13 is provided with a black water discharge port.
本实施例中所述气化系统还设置有:The gasification system described in this embodiment is further provided with:
气固分离及冷灰设备2,与所述气化炉1的合成气出口连通设置;本实施例中所述气固分离及冷却设备包括旋风分离器21,作为可选择的实施方式,除了旋风分离器21,气固分离装置也可以是陶瓷过滤器、烧结金属过滤器、静电除尘器等其它分离装置。The gas-solid separation and cold ash equipment 2 is provided in communication with the synthesis gas outlet of the gasification furnace 1. The gas-solid separation and cooling equipment in this embodiment includes a cyclone separator 21 as an alternative embodiment, except for a cyclone The separator 21 and the gas-solid separation device may be other separation devices such as a ceramic filter, a sintered metal filter, and an electrostatic precipitator.
对流换热装置3,与所述旋风分离器21的气体出口连通,用于回收合成气的显热并产生动力蒸汽;本实施例中所述对流换热装置3为过热器31,所述气化炉1的水冷换热装置的蒸汽出口与所述过热器31连通设置,所述合成气则进入所述过热器31与所述蒸汽进行换热,将所述水冷换热装置出来的蒸汽加热为过热蒸汽。The convective heat exchange device 3 is in communication with the gas outlet of the cyclone separator 21, and is used to recover the sensible heat of the syngas and generate power steam; the convective heat exchange device 3 in this embodiment is a superheater 31, and the gas The steam outlet of the water-cooled heat exchange device of the chemical furnace 1 is arranged in communication with the superheater 31, and the synthesis gas enters the superheater 31 to exchange heat with the steam, and heats the steam from the water-cooled heat exchange device. For superheated steam.
气体洗涤设备,与所述对流换热装置3的气体出口连通设置,包括串联设置的文丘里洗涤器41和洗涤塔42;A gas washing device, which is arranged in communication with the gas outlet of the convection heat exchange device 3 and includes a Venturi scrubber 41 and a washing tower 42 arranged in series;
黑水处理系统,包括串联设置的一级闪蒸装置51和二级闪蒸装置52,所述气化炉1和所述洗涤塔42的黑水排放口与所述一级闪蒸装置51连接设置。与所述一级闪蒸装置51和二级闪蒸装置52的气体出口分别连通设置有冷凝分离装置61、63,所述冷凝分离装置的酸性气体出口与酸性气体处理装置连接, 所述酸性气体处理装置对所述酸性气体出口排出的酸性气体进行处理,作为可选择的实施方式,可采用燃烧处理;与所述一级闪蒸装置51连通设置的冷凝分离装置的液体出口与除氧器62连通;所述二级闪蒸装置52以及与所述二级闪蒸装置52连通设置的冷凝分离装置的液体出口均与沉降槽64连通,所述沉降槽64的液体出口与所述除氧器62连通设置,作为优选的实施方式,在所述沉降槽64与所述除氧器62之间设置有用于起缓冲作用的灰水槽65,与所述沉降槽64的固体排出口连接设置有过滤装置66,所述过滤装置66的液体出口与所述沉降槽64连通设置,用于部分液体的回流。The black water treatment system includes a first-stage flash steaming device 51 and a second-stage flash steaming device 52 arranged in series. The black water discharge ports of the gasification furnace 1 and the washing tower 42 are connected to the first-stage flash steaming device 51. Settings. Condensation and separation devices 61 and 63 are respectively provided in communication with the gas outlets of the first-stage flash evaporation device 51 and the second-stage flash evaporation device 52. The acid gas outlet of the condensation separation device is connected to the acid gas processing device, and the acid gas The processing device processes the acid gas discharged from the acid gas outlet. As an alternative embodiment, a combustion treatment may be adopted; the liquid outlet and the deaerator 62 of the condensation separation device provided in communication with the first-stage flash evaporation device 51 Communication; the liquid outlet of the secondary flash device 52 and the condensation separation device provided in communication with the secondary flash device 52 are in communication with the sedimentation tank 64, and the liquid outlet of the sedimentation tank 64 and the deaerator 62 is provided in communication. As a preferred embodiment, a gray water tank 65 for buffering is provided between the sedimentation tank 64 and the deaerator 62, and a filter is connected to the solid discharge port of the sedimentation tank 64. Device 66, the liquid outlet of the filtering device 66 is provided in communication with the sedimentation tank 64, and is used for the backflow of part of the liquid.
作为优选的实施方式,本实施例中的除氧器62的液体出口连通设置有两路管道,其中一路与洗涤塔42连通,用于将液体回流至洗涤塔42用作洗涤液;另一路与渣池13连通,被泵升压后送入所述激冷集渣装置内,用于补充渣池13中的激冷液,保持渣池13中的激冷液维持在一定的量。As a preferred implementation manner, the liquid outlet of the deaerator 62 in this embodiment is provided with two pipelines, one of which is in communication with the washing tower 42 for returning the liquid to the washing tower 42 as the washing liquid; the other is The slag pool 13 is communicated, and after being boosted by a pump, it is sent into the chilled slag collection device for replenishing the chilled liquid in the slag pool 13 and maintaining the chilled liquid in the slag pool 13 to a certain amount.
基于本实施例中所述气化系统的高效热能回收的气化工艺,包括如下步骤:The gasification process based on the efficient thermal energy recovery of the gasification system described in this embodiment includes the following steps:
(1)将气化剂与氧化剂送入气化室11进行气化反应生成合成气,其中气化剂为含碳燃料,所述氧化剂为含氧气体与蒸汽;合成气由喉部通道112进入所述辐射换热室12的内筒126,在进入过程中利用所述第二喷嘴组喷射流体进行预降温,控制进入辐射换热室12的内筒126内的流体的温度不高于1500℃;合成气进入所述内筒126,利用第一喷射装置121喷射流体,保持所述辐射换热室12的所述低温区的温度低于900℃,核心高温区的温度在900℃以上,从而保证高效的换热效率。其中所述核心高温区的当量半径占其所在位置处的辐射换热室12的当量半径的30%~95%,并进一步优选为30~60%。由所述低温区和核心高温区继续下行的流体在第三喷射装置122的进一步喷射作用下进行降温,从而使得流体截面温度整体降低,进而降低粘性,防止颗粒在由内筒126转弯进入外筒124时与壁面发生碰撞粘结,进入所述内筒与外筒124之间后,再由所述第四喷嘴组进一步喷射降温,使未充分冷却的灰渣颗粒在碰撞壁面之前进一步冷却,以减少或阻止粘附。在所述辐射换热室12中,随着合成气的气体温度下降,合成气中的液渣迅速固化,大的灰渣颗粒落入底部渣池13,经 破渣机14、渣锁斗15、捞渣机排出,剩余部分形成黑水排出。(1) The gasification agent and oxidant are sent to the gasification chamber 11 for gasification reaction to generate synthesis gas, wherein the gasification agent is a carbon-containing fuel, and the oxidant is an oxygen-containing gas and steam; the synthesis gas enters through the throat passage 112 The inner cylinder 126 of the radiation heat exchange chamber 12 is pre-cooled by using the second nozzle group spray fluid during the entry process, and the temperature of the fluid entering the inner cylinder 126 of the radiation heat exchange chamber 12 is controlled to be not higher than 1500 ° C. Synthetic gas enters the inner cylinder 126, and the first spraying device 121 is used to spray fluid to keep the temperature in the low-temperature region of the radiation heat exchange chamber 12 lower than 900 ° C and the temperature in the core high-temperature region above 900 ° C. Ensure efficient heat exchange efficiency. Wherein, the equivalent radius of the core high-temperature region occupies 30% to 95% of the equivalent radius of the radiation heat exchange chamber 12 at the position where it is, and more preferably 30 to 60%. The fluid that continues to descend from the low-temperature region and the core high-temperature region is cooled by the further injection of the third injection device 122, so that the overall cross-sectional temperature of the fluid is lowered, thereby reducing the viscosity, and preventing particles from turning into the outer cylinder from the inner cylinder 126. At 1200, it collided with the wall surface. After entering between the inner cylinder and the outer cylinder 124, the fourth nozzle group was further sprayed to reduce the temperature, so that the slag particles that were not sufficiently cooled were further cooled before they hit the wall surface. Reduce or prevent adhesion. In the radiation heat exchange chamber 12, as the gas temperature of the synthesis gas decreases, the liquid slag in the synthesis gas rapidly solidifies, and large ash and slag particles fall into the bottom slag pool 13, and pass through the slag breaker 14, the slag lock bucket 15 3. The slag-fishing machine discharges, and the remaining part forms black water discharge.
(2)利用旋风分离器21对经所述辐射换热室12换热后的合成气进行气固分离,将所述合成气中的颗粒粒径控制在小于或者等于5μm的范围内;利用干法冷却的方式对旋风分离器21分离出的高温干灰进行冷却处理,所述干法冷却是指利用气体、循环水、脱盐水等作为冷却介质对高温干灰进行对流换热,这种方式可将旋风分离出的占细灰总量90%的细灰以干灰形式回收,同时可将高温干灰中的能量进一步回收,回收的能量可进一步综合利用,如热的脱盐水可以作为汽包补水,热循环水可以作为厂内热水使用、热气体可用于对粉料进行加热或干燥使用。(2) The cyclone separator 21 is used to perform gas-solid separation on the synthesis gas that has been heat exchanged by the radiation heat exchange chamber 12, and the particle size of the synthesis gas is controlled within a range of less than or equal to 5 μm; The cooling method is to cool the high-temperature dry ash separated by the cyclone separator 21. The dry cooling refers to the convective heat exchange of high-temperature dry ash by using gas, circulating water, desalinated water, etc. as a cooling medium. The ash separated by the cyclone, which accounts for 90% of the total ash, can be recovered as dry ash. At the same time, the energy in the high-temperature dry ash can be further recovered, and the recovered energy can be further comprehensively used. For example, hot demineralized water can be used as steam Including make-up water, thermal circulating water can be used as hot water in the factory, and hot gas can be used to heat or dry the powder.
(3)利用过热器31对步骤(2)中分离出的合成气进行对流换热处理,合成气作为过热器31中的加热介质,对气化炉1产生的的蒸汽进行过热处理,将所述蒸汽加热成压力为4.0-12MPa,温度为320-540℃的高品质过热蒸汽,从而回收合成气的显热并产生优质动力蒸汽,本实施方式设置过热器31进行换热处理,由过热器31出来的合成气可用于下游制备化工产品。(3) The superheater 31 is used to perform convective heat exchange treatment on the synthesis gas separated in step (2). The synthesis gas is used as the heating medium in the superheater 31, and the steam generated by the gasification furnace 1 is subjected to superheat treatment. The steam is heated into high-quality superheated steam with a pressure of 4.0-12MPa and a temperature of 320-540 ° C, so as to recover the sensible heat of the synthesis gas and generate high-quality power steam. In this embodiment, a superheater 31 is provided for heat exchange treatment. The synthesis gas from 31 can be used for downstream preparation of chemical products.
(4)依次利用文丘里洗涤器41和洗涤塔42对步骤(4)中对流换热处理后的合成气进行洗涤,将合成气洗涤至颗粒含量小于或者等于1mg/Nm 3,洗涤水则形成黑水排出; (4) The venturi scrubber 41 and the washing tower 42 are used to sequentially wash the syngas after the convective heat exchange treatment in step (4), and the syngas is washed until the particle content is less than or equal to 1 mg / Nm 3 , and the washing water is formed. Black water discharge
(5)对步骤(1)和步骤(4)中产生的黑水进行两级闪蒸处理,利用冷凝分离装置对两级闪蒸处理过程中产生的气体进行冷凝分离,对分离出的酸性气进行燃烧处理,将一级闪蒸后冷凝分离出的液体送入除氧器62进行除氧处理;二级闪蒸后冷凝分离出的液体与二级闪蒸后的剩余液体则先进入沉降槽64,经沉降处理后的上层清液再送入所述除氧器62进行除氧处理,沉降处理产生的沉降固体部分则送入过滤装置66进行过滤,过滤产生的滤液再回流至沉降槽64;本实施例中除氧器62出来的液体回流至洗涤塔42和渣池13,实现水的循环利用;沉降槽排出的液体,一部分送入除氧器,一部分送回锁渣斗,用于促进排渣,一部分形成废水排出以平衡灰水系统中溶解的盐分。(5) The black water generated in step (1) and step (4) is subjected to two-stage flash evaporation, and a condensation separation device is used to condense and separate the gas generated during the two-stage flash evaporation process, and the separated acid gas Combustion treatment is performed, and the liquid separated and condensed after the first stage flash evaporation is sent to the deaerator 62 for deaeration treatment; the liquid separated and condensed after the second stage flash evaporation and the remaining liquid after the second stage flashed enter the sedimentation tank first. 64. The supernatant liquid after the sedimentation treatment is sent to the deaerator 62 for deoxygenation treatment, and the sedimented solid part generated by the sedimentation treatment is sent to the filtering device 66 for filtration, and the filtrate generated by the filtration is returned to the sedimentation tank 64; In this embodiment, the liquid from the deaerator 62 is returned to the washing tower 42 and the slag tank 13 to realize water recycling; part of the liquid discharged from the sedimentation tank is sent to the deaerator and part of it is returned to the slag lock hopper for promoting Slag discharge, part of the wastewater is formed to balance the dissolved salt in the grey water system.
实施例2Example 2
本实施例提供了一种高效热能回收的气化系统,可用于制备下游的燃料气或IGCC产品,如图5所示,所述气化系统包括:This embodiment provides a high-efficiency thermal energy recovery gasification system that can be used to prepare downstream fuel gas or IGCC products. As shown in FIG. 5, the gasification system includes:
用于制备合成气和进行辐射换热的气化炉1,本实施例中所述的气化炉1同实施例1。The gasification furnace 1 used for preparing syngas and performing radiative heat exchange, the gasification furnace 1 described in this embodiment is the same as the embodiment 1.
气固分离及冷灰设备2,与所述气化炉1的合成气出口连通设置;本实施例中所述气固分离及冷却设备包括旋风分离器21,本实施例采用二级旋风配置,可控制合成气中飞灰粒径≤1μm。The gas-solid separation and cold ash equipment 2 is provided in communication with the synthesis gas outlet of the gasification furnace 1. The gas-solid separation and cooling equipment in this embodiment includes a cyclone separator 21. This embodiment adopts a two-stage cyclone configuration. Can control fly ash particle size ≤1μm in syngas.
对流换热装置3,与所述旋风分离器21的气体出口连通,用于回收合成气的显热并产生动力蒸汽;本实施例中所述对流换热装置3为串联设置的过热器31、多级饱和蒸汽发生器32和锅炉水预热器33。本实施例中所述气化炉1的水冷换热装置的蒸汽出口与所述过热器31连通设置,所述合成气则进入所述过热器31与所述蒸汽进行换热,将所述水冷换热装置出来的蒸汽加热为过热蒸汽,所述合成气由所述过热器31出来后再依次进入多级饱和蒸汽发生器32和锅炉水预热器33,用于产生饱和蒸汽和对锅炉水进行预热,从而进一步回收合成气中的热量,其中预热后的锅炉水用作气化炉1中的水冷却介质和喷射装置喷出的冷却液;所述多级饱和蒸汽发生器32适宜采用二级到四级饱和蒸汽发生器中的任意一种。The convective heat exchange device 3 is in communication with the gas outlet of the cyclone separator 21 and is used to recover the sensible heat of the synthesis gas and generate power steam. The convective heat exchange device 3 in this embodiment is a superheater 31, Multi-stage saturated steam generator 32 and boiler water preheater 33. In this embodiment, the steam outlet of the water-cooled heat exchange device of the gasification furnace 1 is provided in communication with the superheater 31, and the synthesis gas enters the superheater 31 to exchange heat with the steam to cool the water. The steam from the heat exchange device is heated to superheated steam. After the synthesis gas comes out of the superheater 31, it enters the multi-stage saturated steam generator 32 and the boiler water preheater 33 in order to generate saturated steam and the boiler water. Preheating to further recover the heat in the synthesis gas, wherein the preheated boiler water is used as the water cooling medium in the gasifier 1 and the cooling liquid sprayed from the injection device; the multi-stage saturated steam generator 32 is suitable Any of two to four-stage saturated steam generators is used.
气体洗涤设备,与所述对流换热装置3的气体出口连通设置,包括串联设置的文丘里洗涤器41和洗涤塔42,对完成对流换热的合成气进行洗涤。The gas washing device is arranged in communication with the gas outlet of the convective heat exchange device 3 and includes a Venturi scrubber 41 and a washing tower 42 arranged in series to wash the syngas that has completed convective heat exchange.
黑水处理系统,包括串联设置的一级闪蒸装置51和二级闪蒸装置52,所述气化炉1和所述洗涤塔42的黑水排放口与所述一级闪蒸装置51连接设置。与所述一级闪蒸装置51和二级闪蒸装置52的气体出口分别连通设置有冷凝分离装置,所述冷凝分离装置的酸性气体出口与酸性气体处理装置连接;与所述一级闪蒸装置51连通设置的冷凝分离装置的液体出口与除氧器62连通;所述二级闪蒸装置52以及与所述二级闪蒸装置52连通设置的冷凝分离装置的液体出口均与沉降槽64连通,所述沉降槽64的液体出口与所述除氧器62连通设置,作为优选的实施方式,在所述沉降槽64与所述除氧器62之间设置有用于 起缓冲作用的灰水槽65,与所述沉降槽64的固体排出口连接设置有过滤装置66,所述过滤装置66的液体出口与所述沉降槽64连通设置,用于部分液体的回流。The black water treatment system includes a first-stage flash steaming device 51 and a second-stage flash steaming device 52 arranged in series. The black water discharge ports of the gasification furnace 1 and the washing tower 42 are connected to the first-stage flash steaming device 51. Settings. A condensation separation device is provided in communication with the gas outlets of the first-stage flash evaporation device 51 and the second-stage flash evaporation device 52, and the acid gas outlet of the condensation separation device is connected to the acid gas processing device; The liquid outlet of the condensation separation device provided in communication with the device 51 is in communication with the deaerator 62; the liquid outlet of the secondary flash device 52 and the liquid separation in the condensation separation device provided in communication with the secondary flash device 52 are connected to the sedimentation tank 64 The liquid outlet of the sedimentation tank 64 is in communication with the deaerator 62. As a preferred embodiment, a gray water tank for buffering is provided between the sedimentation tank 64 and the deaerator 62. 65. A filtering device 66 is provided in connection with the solid discharge port of the sedimentation tank 64, and a liquid outlet of the filtering device 66 is provided in communication with the sedimentation tank 64 for returning part of the liquid.
基于本实施例中所述气化系统的高效热能回收的气化工艺,包括如下步骤:The gasification process based on the efficient thermal energy recovery of the gasification system described in this embodiment includes the following steps:
(1)将气化剂与氧化剂送入气化室11进行气化反应生成合成气,其中气化剂为含碳燃料,所述氧化剂为含氧气体与蒸汽;合成气由喉部通道112进入所述辐射换热室12的内筒,在进入过程中利用所述第二喷嘴组喷射流体进行预降温,控制进入辐射换热室12的内筒内的流体的温度不高于1500℃;合成气进入所述内筒,利用第一喷射装置121喷射流体,保持所述辐射换热室123的所述低温区的温度低于900℃,核心高温区的温度在900℃以上,从而保证高效的换热效率。其中所述核心高温区的当量半径占其所在位置处的辐射换热室12的当量半径的30%~95%,并进一步优选为30~60%。由所述低温区和核心高温区继续下行的流体在第三喷射装置122的进一步喷射作用下进行降温,从而使得流体截面温度整体降低,进而降低粘性,防止颗粒在由内筒转弯进入外筒124时与壁面发生碰撞粘结,进入所述内筒与外筒124之间后,再由所述第四喷嘴组进一步喷射降温,使未充分冷却的灰渣颗粒在碰撞壁面之前进一步冷却,以减少或阻止粘附。在所述辐射换热室12中,随着合成气的气体温度下降,合成气中的液渣迅速固化,大的灰渣颗粒落入底部渣池13,经破渣机14、渣锁斗15、捞渣机排出,剩余部分形成黑水。(1) The gasification agent and oxidant are sent to the gasification chamber 11 for gasification reaction to generate synthesis gas, wherein the gasification agent is a carbon-containing fuel, and the oxidant is an oxygen-containing gas and steam; the synthesis gas enters through the throat passage 112 The inner cylinder of the radiation heat exchange chamber 12 is pre-cooled by using the second nozzle group spray fluid during the entry process, and the temperature of the fluid entering the inner cylinder of the radiation heat exchange chamber 12 is controlled to be not higher than 1500 ° C; The gas enters the inner cylinder, and the first spraying device 121 is used to spray the fluid to keep the temperature in the low temperature region of the radiation heat exchange chamber 123 lower than 900 ° C and the temperature in the core high temperature region above 900 ° C, thereby ensuring efficient Heat transfer efficiency. Wherein, the equivalent radius of the core high-temperature region occupies 30% to 95% of the equivalent radius of the radiation heat exchange chamber 12 at the position where it is, and more preferably 30 to 60%. The fluid that continues to descend from the low-temperature region and the core high-temperature region is cooled by the further spraying effect of the third spraying device 122, so that the overall cross-sectional temperature of the fluid is lowered, thereby reducing the viscosity, and preventing particles from turning from the inner cylinder into the outer cylinder 124 When it collides with the wall surface, it enters between the inner cylinder and the outer cylinder 124, and then the fourth nozzle group is further sprayed to cool down, so that the slag particles that are not sufficiently cooled are further cooled before hitting the wall surface to reduce Or prevent adhesion. In the radiation heat exchange chamber 12, as the gas temperature of the synthesis gas decreases, the liquid slag in the synthesis gas rapidly solidifies, and large ash and slag particles fall into the bottom slag pool 13, and pass through the slag breaker 14, the slag lock bucket 15 The slag-fishing machine discharges, and the remaining part forms black water.
(2)利用旋风分离器21对经所述辐射换热室12换热后的合成气进行气固分离,将所述合成气中的颗粒粒径控制在小于或者等于1μm的范围内;利用干法方式对分离出的细灰进行冷却处理,将占细灰总量90%的细灰以干灰形式回收。(2) The cyclone separator 21 is used to perform gas-solid separation on the syngas that has been heat-exchanged by the radiation heat exchange chamber 12, and the particle size of the syngas is controlled to be less than or equal to 1 μm; The separated fine ash is subjected to cooling treatment in a method, and the fine ash, which accounts for 90% of the total fine ash, is recovered in the form of dry ash.
(3)利用过热器31对步骤(2)中分离出的合成气进行对流换热处理,将所述合成气依次送入过热器31、多级饱和蒸汽发生器32和锅炉水预热器33,合成气作为过热器31和蒸汽发生器、锅炉水预热器33中的加热介质,用于产 生动力蒸汽、饱和蒸汽,并进一步对锅炉水进行预热,从而充分回收合成气的显热。本实施例中的过热器31对气化炉1和多级饱和蒸汽发生器32产生的的蒸汽进行过热处理,可将所述蒸汽加热成压力为4.0-12MPa,温度为320-540℃的高品质过热蒸汽。(3) Use the superheater 31 to perform convective heat exchange treatment on the synthesis gas separated in step (2), and send the synthesis gas to the superheater 31, the multi-stage saturated steam generator 32, and the boiler water preheater 33 in this order. As a heating medium in the superheater 31, the steam generator and the boiler water preheater 33, the synthesis gas is used to generate power steam and saturated steam, and further preheat the boiler water, thereby fully recovering the sensible heat of the synthesis gas. The superheater 31 in this embodiment performs a heat treatment on the steam generated by the gasification furnace 1 and the multi-stage saturated steam generator 32, and can heat the steam to a pressure of 4.0-12MPa and a temperature of 320-540 ° C. Superheated steam quality.
(4)依次利用文丘里洗涤器41和洗涤塔42对步骤(4)中对流换热处理后的合成气进行洗涤,将合成气洗涤至颗粒含量小于或者等于1mg/Nm 3,洗涤水则形成黑水。 (4) The Venturi scrubber 41 and the washing tower 42 are used to sequentially wash the syngas after the convective heat exchange treatment in step (4), and the syngas is washed to a particle content of 1 mg / Nm 3 or less, and the washing water is formed Black water.
(5)对步骤(1)和步骤(4)中产生的黑水进行两级闪蒸处理,利用冷凝分离装置对两级闪蒸处理过程中产生的气体进行冷凝分离,对分离出的酸性气体进行燃烧处理,将一级闪蒸后冷凝分离出的液体送入除氧器62进行除氧处理;二级闪蒸后冷凝分离出的液体与二级闪蒸后的剩余液体则先进入沉降槽64,经沉降处理后的上层清液再送入所述除氧器62进行除氧处理,沉降处理产生的沉降固体部分则送入过滤装置66进行过滤,过滤产生的滤液再回流至沉降槽64;本实施例中除氧器62出来的液体回流至洗涤塔42和渣池13,实现水的回收利用。(5) The black water generated in steps (1) and (4) is subjected to a two-stage flash evaporation process, and a condensation separation device is used to condense and separate the gas generated during the two-stage flash evaporation process, and the separated acid gas Combustion treatment is performed, and the liquid separated and condensed after the first stage flash evaporation is sent to the deaerator 62 for deaeration treatment; the liquid separated and condensed after the second stage flash evaporation and the remaining liquid after the second stage flashed enter the sedimentation tank 64. The supernatant liquid after the sedimentation treatment is sent to the deaerator 62 for deoxygenation treatment, and the sedimented solid part generated by the sedimentation treatment is sent to the filtering device 66 for filtration, and the filtrate generated by the filtration is returned to the sedimentation tank 64; In this embodiment, the liquid from the deaerator 62 is returned to the washing tower 42 and the slag tank 13 to realize water recycling.
实验例Experimental example
本申请中的工艺系统可有效回收合成气中高温位热能,以(CO+H 2)的产出量为100,000Nm 3/h、气化室11内的平均反应温度为1400℃、年操作时间为8000小时为基础估算实施例1和实施例2中的产值,结果如下表所示: The process system in the present application can effectively recover the high-temperature heat energy in the synthesis gas, with an output of (CO + H 2 ) of 100,000 Nm 3 / h, an average reaction temperature in the gasification chamber 11 of 1400 ° C., and an annual operating time. The output values in Example 1 and Example 2 were estimated based on 8000 hours. The results are shown in the following table:
Figure PCTCN2018122283-appb-000001
Figure PCTCN2018122283-appb-000001
注:10MPag动力蒸汽价格按120元/吨计,循环冷却水价格按0.1元/吨计。Note: The price of 10MPag power steam is calculated at 120 yuan / ton, and the price of circulating cooling water is calculated at 0.1 yuan / ton.
由上表可知合成气中高温显热转化为10.0MPag等级动力蒸汽的比例可达50-70%。采用本工艺可产10.0MPag等级动力蒸汽50-65吨/h(非化工产品方案为70-80吨/h),年增加产值4862-6302万元(非化工产品方案为6778-7738万元),同时循环冷却水消耗减少约780吨/h(非化工产品方案为720吨/h), 年可节约费用62万元(燃料气或IGCC产品方案为58万元),经济效益和节能降耗效果均十分显著。It can be known from the above table that the proportion of high-temperature sensible heat converted into 10.0 MPag grade power steam in the synthesis gas can reach 50-70%. Using this process can produce 10.0MPag grade power steam 50-65 tons / h (non-chemical products scheme is 70-80 tons / h), and the annual output value is increased to 48.62-6302 million yuan (non-chemical products scheme is 67.78-7738 million yuan) At the same time, the circulating cooling water consumption is reduced by about 780 tons / h (720 tons / h for non-chemical products), and annual savings can be 620,000 yuan (580,000 yuan for fuel gas or IGCC product solutions), economic benefits and energy saving The effects are very significant.
以上所述实施例仅表达了本发明的几种实施方式,其描述较为具体和详细,但并不能因此而理解为对本发明专利范围的限制。应当指出的是,对于本领域的普通技术人员来说,在不脱离本发明构思的前提下,还可以做出若干变形和改进,这些都属于本发明的保护范围。因此,本发明专利的保护范围应以权利要求为准。The above-mentioned embodiments only express several implementation manners of the present invention, and their descriptions are more specific and detailed, but they cannot be understood as limiting the scope of the patent of the present invention. It should be noted that, for those of ordinary skill in the art, without departing from the concept of the present invention, several modifications and improvements can be made, which all belong to the protection scope of the present invention. Therefore, the protection scope of the patent of the present invention shall be subject to the claims.

Claims (12)

  1. 一种高效热能回收的气化系统,其特征在于,包括:A gasification system for efficient thermal energy recovery, which is characterized by:
    用于制备合成气和进行辐射换热的气化炉,所述气化炉包括气化室和位于所述气化室下游的辐射换热室,在所述辐射换热室内的换热面上设置有喷射装置,形成贴近换热面的低温区和位于所述低温区远离所述换热面一侧的核心高温区,在所述低温区和核心高温区的下游设置有激冷集渣装置,所述激冷集渣装置内存有激冷液,所述激冷集渣装置设置有黑水排放口;A gasification furnace for preparing syngas and performing radiation heat exchange, the gasification furnace includes a gasification chamber and a radiation heat exchange chamber located downstream of the gasification chamber, and on a heat exchange surface of the radiation heat exchange chamber A spraying device is provided to form a low-temperature area close to the heat exchange surface and a core high-temperature area located on the side of the low-temperature area away from the heat exchange surface, and a chilled slag collecting device is provided downstream of the low-temperature area and the core high-temperature area. A chilled liquid is stored in the chilled slag collection device, and the chilled slag collection device is provided with a black water discharge port;
    气固分离及冷灰设备,与所述气化炉的合成气出口连通设置;Gas-solid separation and cold ash equipment is provided in communication with the synthesis gas outlet of the gasifier;
    对流换热装置,与所述气固分离及冷却设备的气体出口连通,用于回收合成气的显热并产生蒸汽;A convection heat exchange device, which is in communication with the gas outlet of the gas-solid separation and cooling device and is used to recover the sensible heat of the synthesis gas and generate steam;
    气体洗涤设备,与所述对流换热装置的气体出口连通设置,包括串联设置的文丘里洗涤器和洗涤塔,所述洗涤塔设置有黑水排放口;A gas washing device, which is arranged in communication with the gas outlet of the convection heat exchange device and includes a Venturi scrubber and a washing tower arranged in series, and the washing tower is provided with a black water discharge port;
    黑水处理系统,包括串联设置的一级闪蒸装置和二级闪蒸装置,所述激冷集渣装置和所述洗涤塔的黑水排放口与所述一级闪蒸装置连接设置。The black water treatment system includes a first-stage flash evaporation device and a second-stage flash evaporation device arranged in series, and the chilled slag collection device and the black water discharge port of the washing tower are connected to the first-stage flash evaporation device.
  2. 根据权利要求1所述的高效热能回收的气化系统,其特征在于,所述气固分离及冷却设备包括旋风分离器。The gasification system for efficient thermal energy recovery according to claim 1, wherein the gas-solid separation and cooling equipment comprises a cyclone separator.
  3. 根据权利要求1或2所述的高效热能回收的气化系统,其特征在于,所述对流换热装置包括过热器,所述气化室和辐射换热室的换热面上设置有水冷换热装置,所述水冷换热装置的蒸汽出口与所述过热器连通设置,所述合成气进入所述过热器与所述蒸汽进行换热,将所述水冷换热装置出来的蒸汽加热为过热蒸汽。The gasification system for efficient heat energy recovery according to claim 1 or 2, characterized in that the convection heat exchange device comprises a superheater, and water-cooled heat exchangers are provided on the heat exchange surfaces of the gasification chamber and the radiation heat exchange chamber. A heat device, a steam outlet of the water-cooled heat exchange device is provided in communication with the superheater, the synthesis gas enters the superheater and exchanges heat with the steam, and heats the steam from the water-cooled heat exchange device to superheat steam.
  4. 根据权利要求3所述的高效热能回收的气化系统,其特征在于,所述对流换热装置包括串联设置的过热器、多级饱和蒸汽发生器和锅炉水预热器,由所述过热器出来的合成气依次进入所述多级饱和蒸汽发生器和锅炉水预热器。The gasification system for efficient thermal energy recovery according to claim 3, wherein the convection heat exchange device comprises a superheater, a multi-stage saturated steam generator, and a boiler water preheater arranged in series, and the superheater The resultant syngas enters the multi-stage saturated steam generator and the boiler water preheater in sequence.
  5. 根据权利要求1或2或3或4所述的高效热能回收的气化系统,其特征在于,与所述一级闪蒸装置和二级闪蒸装置的气体出口分别连通设置有冷凝分离装置,所述冷凝分离装置的酸性气体出口与酸性气体处理装置连接;与所述 一级闪蒸装置连通设置的冷凝分离装置的液体出口与除氧器连通;所述二级闪蒸装置以及与所述二级闪蒸装置连通设置的冷凝分离装置的液体出口均与沉降槽连通,所述沉降槽的液体出口与所述除氧器连通设置与所述沉降槽的固体排出口连接设置有过滤装置。The gasification system for high-efficiency thermal energy recovery according to claim 1 or 2 or 3 or 4, characterized in that a condensation separation device is provided in communication with the gas outlets of the primary flash device and the secondary flash device, The acid gas outlet of the condensation separation device is connected to the acid gas processing device; the liquid outlet of the condensation separation device provided in communication with the first-stage flash evaporation device is in communication with the deaerator; the second-stage flash evaporation device and The liquid outlets of the condensing and separating devices provided in communication with the two-stage flash evaporation device are all in communication with the sedimentation tank. The liquid outlets of the sedimentation tank are in communication with the deaerator and are connected with the solid discharge ports of the sedimentation tank. A filtering device is provided.
  6. 一种高效热能回收的气化工艺,其特征在于,包括:A gasification process for efficient thermal energy recovery, which is characterized by:
    (1)气化制备合成气,将所述合成气送入辐射换热室进行换热,所述辐射换热室的换热面上设置有喷射装置,所述喷射装置喷射流体,形成贴近换热面的低温区和位于所述低温区远离所述换热面一侧的核心高温区,所述合成气经所述辐射换热室换热后温度降至700℃以上排出,利用激冷液对合成气中的高温灰渣进行激冷,形成黑水排出;(1) Synthesis gas is prepared by gasification, and the synthesis gas is sent to a radiation heat exchange chamber for heat exchange. The heat exchange surface of the radiation heat exchange chamber is provided with an injection device, and the injection device sprays fluid to form a close exchange. The low-temperature area of the hot surface and the core high-temperature area located on the side away from the heat-exchange surface of the low-temperature area. After the heat exchange of the synthesis gas through the radiation heat exchange chamber, the temperature drops to more than 700 ° C and is discharged. Chill the high temperature ash in the synthesis gas to form black water discharge;
    (2)对经所述辐射换热室换热后的合成气进行气固分离,对分离出的细灰进行冷却处理;(2) performing gas-solid separation on the synthesis gas that has been heat exchanged by the radiation heat exchange chamber, and cooling the separated fine ash;
    (3)对步骤(2)中分离出的合成气进行对流换热处理,回收合成气的显热并产生蒸汽;(3) performing convective heat exchange treatment on the synthesis gas separated in step (2), recovering the sensible heat of the synthesis gas and generating steam;
    (4)对步骤(3)中对流换热处理后的合成气进行洗涤,洗涤液形成黑水排出;(4) washing the syngas after the convective heat exchange treatment in step (3), and the washing liquid forms black water to be discharged;
    (5)对步骤(1)和步骤(4)中排出的黑水进行两级闪蒸处理。(5) The black water discharged in steps (1) and (4) is subjected to a two-stage flash treatment.
  7. 根据权利要求6所述的高效热能回收的气化工艺,其特征在于,步骤(4)中将合成气洗涤至颗粒含量小于或者等于1mg/Nm 3The gasification process for efficient thermal energy recovery according to claim 6, characterized in that in step (4), the synthesis gas is washed until the particle content is less than or equal to 1 mg / Nm 3 ,
  8. 根据权利要求6或7所述的高效热能回收的气化工艺,其特征在于,步骤(1)中所述低温区的温度为小于900℃,所述核心高温区的温度在900℃以上。The gasification process for efficient thermal energy recovery according to claim 6 or 7, characterized in that the temperature in the low temperature region in step (1) is less than 900 ° C, and the temperature in the core high temperature region is above 900 ° C.
  9. 根据权利要求8所述的高效热能回收的气化工艺,其特征在于,步骤(2)中对所述合成气进行气固分离,将所述合成气中的颗粒粒径控制在小于或者等于5μm的范围内。The gasification process for efficient thermal energy recovery according to claim 8, characterized in that the synthesis gas is subjected to gas-solid separation in step (2), and the particle diameter of the synthesis gas is controlled to be less than or equal to 5 μm In the range.
  10. 根据权利要求6-9任一所述的高效热能回收的气化工艺,其特征在于, 步骤(2)中采用干法方式实现对所述细灰的冷却处理。The gasification process for high-efficiency thermal energy recovery according to any one of claims 6 to 9, characterized in that, in step (2), the dry ash cooling process is implemented by a dry method.
  11. 根据权利要求6-10任一所述的高效热能回收的气化工艺,其特征在于,步骤(1)中制备合成气产生的热量及辐射换热室内合成气的热量通过换热面对水冷却介质进行加热产生蒸汽;步骤(3)中将所述合成气与所述蒸汽进行对流换热,将所述蒸汽加热成压力为4.0-12MPa,温度为320-540℃的过热蒸汽。The gasification process for efficient thermal energy recovery according to any one of claims 6 to 10, characterized in that the heat generated in the preparation of the syngas in step (1) and the heat of the radiant heat exchange chamber synthesizes the water through the heat exchange surface to cool the water The medium is heated to generate steam; in step (3), the syngas and the steam are subjected to convective heat exchange, and the steam is heated to superheated steam having a pressure of 4.0-12 MPa and a temperature of 320-540 ° C.
  12. 根据权利要求6-11任一所述的高效热能回收的气化工艺,其特征在于,对步骤(5)中两级闪蒸处理过程中产生的气体进行冷凝分离,分离出的酸性气体送下游的酸性气体处理装置,对一级闪蒸后冷凝分离出的液体进行除氧处理;二级闪蒸后冷凝分离出的液体与二级闪蒸后的剩余液体经沉降处理后,再进行除氧处理,对沉降处理产生的固体进行过滤。The gasification process for high-efficiency thermal energy recovery according to any one of claims 6 to 11, characterized in that the gas generated during the two-stage flash evaporation process in step (5) is condensed and separated, and the separated acid gas is sent downstream Acid gas treatment device, which deoxidizes the liquid condensed and separated after the first stage flash evaporation; the liquid separated by the second stage flashed condensation and the remaining liquid after the second stage flash evaporation are deoxidized Treatment, filtering the solid produced by the sedimentation treatment.
PCT/CN2018/122283 2018-08-21 2018-12-20 Gasification system and process for efficient heat energy recovery WO2020037905A1 (en)

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