WO2014110883A1 - 一种对颗粒燃料锅炉烟气进行干法脱硫的工艺系统 - Google Patents

一种对颗粒燃料锅炉烟气进行干法脱硫的工艺系统 Download PDF

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Publication number
WO2014110883A1
WO2014110883A1 PCT/CN2013/075698 CN2013075698W WO2014110883A1 WO 2014110883 A1 WO2014110883 A1 WO 2014110883A1 CN 2013075698 W CN2013075698 W CN 2013075698W WO 2014110883 A1 WO2014110883 A1 WO 2014110883A1
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WIPO (PCT)
Prior art keywords
flue gas
fuel boiler
heat
pellet fuel
process system
Prior art date
Application number
PCT/CN2013/075698
Other languages
English (en)
French (fr)
Inventor
吴道洪
吴玉林
鲁光明
王胜美
陈琳
沈大平
Original Assignee
北京神雾环境能源科技集团股份有限公司
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Priority claimed from CN201310018584.0A external-priority patent/CN103672941B/zh
Priority claimed from CN201310019500.5A external-priority patent/CN103940275B/zh
Priority claimed from CN2013200279133U external-priority patent/CN203068557U/zh
Application filed by 北京神雾环境能源科技集团股份有限公司 filed Critical 北京神雾环境能源科技集团股份有限公司
Publication of WO2014110883A1 publication Critical patent/WO2014110883A1/zh

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Classifications

    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23CMETHODS OR APPARATUS FOR COMBUSTION USING FLUID FUEL OR SOLID FUEL SUSPENDED IN  A CARRIER GAS OR AIR 
    • F23C10/00Fluidised bed combustion apparatus
    • F23C10/02Fluidised bed combustion apparatus with means specially adapted for achieving or promoting a circulating movement of particles within the bed or for a recirculation of particles entrained from the bed
    • F23C10/04Fluidised bed combustion apparatus with means specially adapted for achieving or promoting a circulating movement of particles within the bed or for a recirculation of particles entrained from the bed the particles being circulated to a section, e.g. a heat-exchange section or a return duct, at least partially shielded from the combustion zone, before being reintroduced into the combustion zone
    • F23C10/08Fluidised bed combustion apparatus with means specially adapted for achieving or promoting a circulating movement of particles within the bed or for a recirculation of particles entrained from the bed the particles being circulated to a section, e.g. a heat-exchange section or a return duct, at least partially shielded from the combustion zone, before being reintroduced into the combustion zone characterised by the arrangement of separation apparatus, e.g. cyclones, for separating particles from the flue gases
    • F23C10/10Fluidised bed combustion apparatus with means specially adapted for achieving or promoting a circulating movement of particles within the bed or for a recirculation of particles entrained from the bed the particles being circulated to a section, e.g. a heat-exchange section or a return duct, at least partially shielded from the combustion zone, before being reintroduced into the combustion zone characterised by the arrangement of separation apparatus, e.g. cyclones, for separating particles from the flue gases the separation apparatus being located outside the combustion chamber
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D53/00Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
    • B01D53/34Chemical or biological purification of waste gases
    • B01D53/46Removing components of defined structure
    • B01D53/48Sulfur compounds
    • B01D53/50Sulfur oxides
    • B01D53/508Sulfur oxides by treating the gases with solids
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23LSUPPLYING AIR OR NON-COMBUSTIBLE LIQUIDS OR GASES TO COMBUSTION APPARATUS IN GENERAL ; VALVES OR DAMPERS SPECIALLY ADAPTED FOR CONTROLLING AIR SUPPLY OR DRAUGHT IN COMBUSTION APPARATUS; INDUCING DRAUGHT IN COMBUSTION APPARATUS; TOPS FOR CHIMNEYS OR VENTILATING SHAFTS; TERMINALS FOR FLUES
    • F23L15/00Heating of air supplied for combustion
    • F23L15/02Arrangements of regenerators
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F28HEAT EXCHANGE IN GENERAL
    • F28DHEAT-EXCHANGE APPARATUS, NOT PROVIDED FOR IN ANOTHER SUBCLASS, IN WHICH THE HEAT-EXCHANGE MEDIA DO NOT COME INTO DIRECT CONTACT
    • F28D19/00Regenerative heat-exchange apparatus in which the intermediate heat-transfer medium or body is moved successively into contact with each heat-exchange medium
    • F28D19/04Regenerative heat-exchange apparatus in which the intermediate heat-transfer medium or body is moved successively into contact with each heat-exchange medium using rigid bodies, e.g. mounted on a movable carrier
    • F28D19/041Regenerative heat-exchange apparatus in which the intermediate heat-transfer medium or body is moved successively into contact with each heat-exchange medium using rigid bodies, e.g. mounted on a movable carrier with axial flow through the intermediate heat-transfer medium
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2257/00Components to be removed
    • B01D2257/30Sulfur compounds
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23JREMOVAL OR TREATMENT OF COMBUSTION PRODUCTS OR COMBUSTION RESIDUES; FLUES 
    • F23J2215/00Preventing emissions
    • F23J2215/20Sulfur; Compounds thereof
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23JREMOVAL OR TREATMENT OF COMBUSTION PRODUCTS OR COMBUSTION RESIDUES; FLUES 
    • F23J2219/00Treatment devices
    • F23J2219/60Sorption with dry devices, e.g. beds
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02EREDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
    • Y02E20/00Combustion technologies with mitigation potential
    • Y02E20/34Indirect CO2mitigation, i.e. by acting on non CO2directly related matters of the process, e.g. pre-heating or heat recovery

Definitions

  • the present invention relates to the field of heat exchange technology, and more particularly to an improved particulate fuel boiler and dry desulfurization process system. Background technique
  • boilers in the field of thermoelectrics use tubular air preheaters to heat the air.
  • the tail desulfurization tower is desulfurized by spraying water to cool down.
  • Circulating popularized bed boiler technology is a highly efficient and low-pollution clean combustion technology that has developed rapidly in the past decade. Internationally, this technology has been widely used in power station boilers, industrial boilers and waste treatment and utilization, and has been developed to large-scale circulating fluidized bed boilers of several hundred thousand kilowatt scale; domestic research and development in this area And applications have gradually emerged, and thousands of fluidized bed and circulating fluidized bed boilers have been put into operation. The future will also be an important period for the rapid development of circulating fluidized beds.
  • the present invention aims to solve at least one of the technical problems existing in the prior art. Accordingly, it is an object of the present invention to provide a particulate fuel boiler and a dry desulfurization process system having a low exhaust gas temperature and high boiler efficiency.
  • a particulate fuel boiler and a dry desulfurization process system comprising: a particulate fuel boiler, the particulate fuel boiler defining a furnace; a regenerative rotary reversing heater, the regenerative rotary reversing heater
  • the method includes: a heat exchanger body; a driving device, wherein the driving device is configured to drive the heat exchanger body to rotate about a central axis thereof; and a partition member, wherein the partitioning member is disposed in the heat exchange direction along a direction of the central axis Inside the body, and dividing the heat exchanger body into at least one pair of receiving portions, the pair of receiving portions being disposed diametrically opposite to the central axis; and a heat carrier, the heat carrier being respectively accommodated in the housing
  • the heat carrier is formed of a non-metallic solid material; a first flue gas passage, an inlet end of the first flue gas passage is in communication with a top of the furnace, and an outlet end and the
  • a particulate fuel boiler and a dry desulfurization process system by providing a regenerative rotary commutation Heater and WCFB flue gas desulfurization equipment, regenerative rotary reversing heater can reduce high temperature flue gas to about 65-75 °C, thus improving the efficiency of the boiler system, while desulfurizing WCFB flue gas in subsequent flue gas purification treatment
  • the water spray device can be omitted in the equipment, which not only optimizes the process, saves cost and reduces the corrosion effect, but also effectively solves the problems of ash adherence after water spray.
  • particulate fuel boiler and dry desulfurization process system in accordance with the present invention may also have the following additional technical features:
  • the first flue gas passage includes a first tail flue communicating with the furnace and a hot flue flue communicating with the first tail flue, the hot flue flue The outlet end is in communication with the regenerative rotary reversing heater.
  • a plurality of superheaters are disposed in the first tail flue.
  • the cycle thermal efficiency of the entire steam power unit can be effectively improved.
  • the particulate fuel boiler and dry desulfurization process system further includes: a cyclone separator, the cyclone separator being in communication with a top of the furnace and the first tail flue, respectively.
  • the cyclone separator further includes a return pipe that communicates with the main body of the cyclone and the lower portion of the furnace, respectively.
  • a return pipe that communicates with the main body of the cyclone and the lower portion of the furnace, respectively.
  • the flue gas velocity entering the regenerative rotary reversing heater from the hot flue is adjustable. Thereby, the temperature of the air to be preheated is effectively increased.
  • the heat carrier is SiC or ceramic and has a small spherical, sheet or porous structure.
  • the regenerative rotary reversing heater is resistant to high temperatures, corrosion and wear.
  • the temperature of the flue gas after heat exchange by the regenerative rotary commutation heater is 65-75 °C. While the boiler exhaust gas temperature has dropped to 65-75 °C, there is a major change in the tail desulfurization process. That is to use the WCFB dry desulfurization process, so that the tail does not need to spray water to cool down, to avoid corrosion problems, the flue gas is reduced to 65 ⁇ 75 °C, which is the inlet smoke temperature of the WCFB dry desulfurization process, and the original exhaust gas above 12CTC The temperature must be sprayed to cool down to 65 ⁇ 75 °C, which saves a water spray process and saves energy, avoiding the unfavorable problem of ash adherence after water spray. Therefore, the flue gas entering the subsequent WCFB flue gas desulfurization equipment does not need to be sprayed and cooled.
  • the WCFB flue gas desulfurization apparatus includes: an absorption tower, the second flue gas passage is in communication with a bottom of the absorption tower; a lime removal silo, the decalcification silo is disposed in the absorption tower An upper portion for injecting slaked lime into the absorption tower; and a dust remover, wherein the dust remover is in communication with the absorption tower for dedusting the flue gas after the slaked lime absorption reaction, and the dust after the dust removal The gas is discharged to the atmosphere through the second tail flue.
  • the flue gas can be absorbed and reacted with the slaked lime sprayed from the slaked lime silo in the absorption tower.
  • the flue gas after desulfurization can be purified into the dust remover.
  • the particulate fuel boiler and dry desulfurization process system further includes: a recirculation pipe that is disposed obliquely and used to recycle slaked lime at the bottom of the precipitator into the absorption tower.
  • a recirculation pipe that is disposed obliquely and used to recycle slaked lime at the bottom of the precipitator into the absorption tower.
  • the particulate fuel boiler and the dry desulfurization process system further include: a water tank connected to the absorption tower for selectively spraying water into the absorption tower. Therefore, by providing the water tank, it is possible to effectively prevent the temperature of the flue gas in the absorption tower from being excessively high due to an accident.
  • Figure 1 is a schematic illustration of a particulate fuel boiler and dry desulfurization process system in accordance with one embodiment of the present invention
  • Figure 2 is a top plan view of a regenerative rotary commutator in a powdered solid fuel boiler in accordance with one embodiment of the present invention.
  • first and second are used for descriptive purposes only and are not to be construed as indicating or implying a relative importance or implicitly indicating the number of technical features indicated. Thus, features defining “first” and “second” may explicitly or implicitly include one or more of the features. In the description of the present invention, “multiple” means two or more unless otherwise stated.
  • connection should be understood broadly, and may be fixed or detachable, for example, unless otherwise explicitly defined and defined.
  • Connected, or connected integrally can be mechanical or electrical; can be directly connected, or indirectly connected through an intermediate medium, can be the internal communication of the two components.
  • the specific meaning of the above terms in the present invention can be understood in a specific case by those skilled in the art.
  • a particulate fuel boiler and a dry desulfurization process system 100 in accordance with an embodiment of the present invention includes: a particulate fuel boiler 1, a regenerative rotary commutation heater 2, a first flue gas passage 3, an air passage 4, and WCFB flue gas desulfurization equipment 5.
  • the regenerative rotary reversing heater 2 is used for exchanging heat between the high temperature flue gas and the air to be preheated, thereby raising the temperature of the air to be preheated to a certain value.
  • the regenerative rotary reversing heater 2 comprises: a heat exchanger body 21, a drive package
  • the separator 22 and the heat carrier 23 are as shown in Figs.
  • the drive means is used to drive the heat exchanger body 21 to rotate about its central axis 24.
  • the partition 22 is disposed in the heat exchanger body 21 in the direction of the central axis 24, and divides the heat exchanger body 21 into at least one pair of accommodating portions 25, each pair of accommodating portions 25 being disposed diametrically opposite to the central axis.
  • the heat carriers are respectively housed in the accommodating portion 25, and the heat carrier 23 is formed of a non-metallic solid material.
  • the heat exchanger body 21 may be formed as a hollow cylinder, and the partition 22 may be substantially plate-shaped, and the partition extends in the direction of the center line axis of the heat exchanger body 21, thereby
  • the heat exchanger body 21 is partitioned into a pair of receiving portions, the heat carriers are respectively disposed in the two receiving portions, and the heat carrier can be made of a non-metallic solid material, and the flue gas and the air to be preheated are respectively introduced into the two receiving portions, and then passed through
  • the driving device drives the heat exchanger main body 21 to rotate, the flue gas exchanges heat with the heat carrier in the accommodating portion in which it is located, heats the air to be preheated, and the heat carrier in the accommodating portion therewith, thereby causing the air to be preheated The temperature rises.
  • the partition 22 may also divide the heat exchanger body 21 into two pairs, three pairs or even pairs of receiving portions.
  • the outlet temperature of the flue gas after passing through the gas heat exchanger cannot be lowered below 130 ° C, because this causes the sulfuric acid to precipitate, resulting in the metal in the gas heat exchanger. Severe corrosion of the manufactured parts.
  • the heat carrier is formed of a non-metallic solid material such as SiC or ceramic, there is no need to worry about sulfur.
  • the outlet temperature of the high-temperature flue gas can be lowered to a temperature below the dew point of sulfur to maximize heat exchange.
  • the high temperature The outlet temperature of the flue gas leaving the gas heat exchanger is less than 130 ° C. Further, the outlet temperature of the high temperature flue gas leaving the gas heat exchanger is less than 70 ° C. This temperature is almost impossible to achieve in a conventional gas heat exchange system.
  • the water vapor condenses out as liquid water, releasing a large amount of latent heat (the amount of heat absorbed by the water vapor from 100 ° C to 10 CTC is equivalent to the water from 0 ° C 3 times the amount of heat absorbed when it is raised to 100 °C).
  • the heat carrier is formed of a non-metallic solid material, after the sulfur deposition is performed to some extent, the heat carrier accommodated in the accommodating portion can be continuously used, thereby reducing the components existing in the conventional gas heat exchange system. The problem of increased costs caused by replacement.
  • the efficiency of the entire boiler can be increased by 0.5% for every 10 °C decrease in the outlet temperature, and the latent heat released is equivalent to Increases the efficiency of the entire boiler by 1.5%, so that when the flue gas temperature is lowered to, for example, 70 ° C, the efficiency of the entire boiler is increased by 4.5% or more (0.5% X6 + 1.5), thereby saving a large amount in the boiler.
  • Coal combustion while expanding the scope of application of coal, can reduce the grade of coal used, further reducing production costs.
  • the particulate fuel boiler 1 is defined with a furnace 11 .
  • the inlet end of the first flue gas passage 3 communicates with the top of the furnace 11 and the outlet end communicates with the regenerative rotary reversing heater 2 to pass the flue gas generated in the furnace 11 into at least a pair of heat storage. Rotating one of the accommodating portions of the reversing heater 2 and exchanging heat with the heat carrier accommodated in the accommodating portion.
  • the air passage 4 is for introducing at least air into the other of the pair of receiving portions such that the heat carrier accommodated in the accommodating portion exchanges heat with the air, and the heat-exchanged air is supplied to the inside of the furnace 11.
  • the flue gas after heat exchange by the regenerative rotary reversing heater 2 flows into the WCFB flue gas desulfurization through the second flue gas passage 101 Device 5.
  • the heat exchanger body 21 is rotated counterclockwise, and the flue gas is introduced into the heat exchanger body 21 along the right side of the central axis, and the preheated air is introduced into the heat exchanger along the left side of the central axis.
  • the main body 21 will be described as an example.
  • a furnace 11 is defined in the particulate fuel boiler 1 for accommodating pulverized coal.
  • One end of the flue gas passage 3 communicates with the furnace 11 and the other end thereof communicates with the regenerative rotary reversing heater 2 to
  • the flue gas generated in the furnace 11 is introduced into the first accommodating portion 211 of the regenerative rotary reversing heater 2 (for example, the right side of the regenerative rotary reversing heater 2 shown in Fig. 1), and the heat storage is performed.
  • the second accommodating portion 212 of the rotary reversing heater 2 for example, the left side of the regenerative rotary reversing heater 2 shown in Fig.
  • the flue gas exchanges heat with the heat carrier in the first accommodating portion 211 to raise the temperature of the heat carrier, and after the heat carrier absorbs heat, the heat exchanger body 21 rotates counterclockwise, and the first accommodating portion 211 Rotating to the left side of the central axis, the second receiving portion 212 is rotated to the right side of the central axis, and the heat carrier rotating into the first receiving portion 211 on the left side exchanges heat with the air to be heated to raise the temperature of the heated air. At the same time, the smoke is rotated to A second heat carrier within the receiving portion 212 side is heated.
  • the heat exchanger body 21 continues to rotate counterclockwise, at which time the first receiving portion 211 is rotated back to the right side of the central axis, the second receiving portion 212 is rotated back to the left side of the central axis, and rotated back to the second accommodation on the left side.
  • the heat carrier in the portion 212 exchanges heat with the air to be heated, and the flue gas heats the heat carrier in the first accommodating portion 211 which is rotated back to the right side, and the cycle is repeated to complete the heating of the preheated air.
  • the air to be preheated may be supplied to the furnace 11 from the bottom of the particulate fuel boiler 1 after being heated to a certain temperature, thereby performing high temperature oxidation combustion with the particulate fuel in the furnace, and the particulate fuel may be from the fuel.
  • the inlet 13 enters the furnace 11.
  • the bottom of the particulate fuel boiler 1 is provided with a wind deflecting plate 12, and the preheated air enters the furnace 11 through the air distribution plate 12 at the bottom of the boiler.
  • the flue gas after heat exchange with the preheated air enters the WCFB flue gas desulfurization apparatus 5 through the second flue gas passage 101 for purification.
  • the regenerative rotary reversing heater 2 and the WCFB flue gas desulfurization device 5 are provided, and the regenerative rotary reversing heater 2 can be used for high temperature flue gas. Reduce to about 65 ⁇ 75 °C. While the boiler exhaust temperature has dropped to 65-75 °C, there is a need for major changes in the tail desulfurization process.
  • the flue gas is reduced to 65 ⁇ 75 °C, which is just the inlet smoke temperature of the WCFB dry desulfurization process, the original 120 °C or more
  • the exhaust gas temperature must be sprayed to cool down to 65 ⁇ 75 °C, which saves a water spray process and saves energy, avoiding the unfavorable problem of ash adherence after water spray.
  • the first flue gas passage 3 includes a first tail flue 31 communicating with the furnace 11 and a hot flue duct 32 communicating with the first tail flue 31, and the outlet end of the hot flue duct 32 is
  • the hot rotary commutator heater 2 is in communication. That is, the first flue gas passage 3 includes a first tail flue 31 and a hot flue flute 32, wherein one end of the first tail flue 31 communicates with the furnace 11 and the other end communicates with the hot flue 32, hot air smoke The other end of the passage 32, that is, the outlet end, communicates with the regenerative rotary reversing heater 2.
  • a plurality of superheaters 311 are disposed in the first tail flue 31. In other words, a plurality of superheaters 311 spaced apart from each other may be provided in the first tail flue 31.
  • the cycle thermal efficiency of the entire steam power unit can be effectively improved.
  • the particulate fuel boiler and dry desulfurization process system 100 further includes: a cyclone separator 6, and a cyclone separator 6 in communication with the top of the furnace 11 and the first tail flue 31, respectively.
  • a cyclone separator 6 is provided at the junction of the furnace 11 and the first tail flue 31, and communicates with the furnace 11 and the first tail flue 31, respectively.
  • the cyclone separator 6 further includes a return pipe 61 that communicates with the main body of the cyclone separator 6 and the lower portion of the furnace casing 11, respectively. As shown in Fig. 1, one end of the return pipe 61 communicates with the bottom of the cyclone 6, and the other end thereof communicates with the lower portion of the furnace. Thus, by providing the return pipe 61, the larger particulate fuel and ash particles can pass through the return pipe 61, circulate into the furnace 11 for combustion and heat exchange.
  • the velocity of the flue gas entering the regenerative rotary reversing heater 2 from the hot air flue 32 is adjustable.
  • the velocity of the flue gas entering the regenerative rotary reversing heater 2 from the hot flue flue 32 is high, the temperature of the air to be preheated can be greatly increased.
  • the heat carrier is SiC or ceramic and has a small spherical, sheet-like or porous structure.
  • the regenerative rotary reversing heater 2 is resistant to high temperatures, corrosion, and wear.
  • the temperature of the flue gas after heat exchange by the regenerative rotary commutation heater 2 is 65-75 °C. Therefore, the flue gas entering the subsequent WCFB flue gas desulfurization device 5 does not need to be sprayed and cooled.
  • the WCFB flue gas desulfurization apparatus 5 includes: an absorption tower 51, a slaked lime tank 52, and a dust remover 53.
  • the second flue gas passage 101 communicates with the bottom of the absorption tower 51.
  • the slaked lime tank 52 is disposed at the upper portion of the absorption tower 51 for injecting slaked lime into the absorption tower 51.
  • the dust remover 53 is connected to the absorption tower 51 for dedusting the flue gas after the slaked lime absorption reaction, and the dust after the dust removal is discharged to the atmosphere through the second tail flue.
  • the flue gas can be absorbed and reacted with the slaked lime sprayed from the slaked lime silo 52 in the absorption tower 51.
  • the dust remover 53 By providing the dust remover 53, the desulfurized flue gas can enter the dust remover 53. Purify.
  • one end of the second flue gas passage 101 communicates with the regenerative rotary reversing heater 2, and the other end thereof communicates with the bottom of the absorption tower 51, thereby regeneratively rotating the reversing heater 2
  • the temperature-reduced flue gas is introduced into the absorption tower 51, and the flue gas rises to the upper portion of the absorption tower 51 to absorb the slaked lime sprayed from the slaked lime silo 52, and then enters the dust remover 53 for dust removal, and the desulfurized purified flue gas leaves the dust remover 53. Enter the second tail flue and finally drain into the atmosphere by the chimney.
  • the particulate fuel boiler and dry desulfurization process system 100 further includes: a recirculation pipe 54 disposed obliquely and for recycling the slaked lime at the bottom of the precipitator 53 into the absorption tower 51.
  • a recirculation pipe 54 disposed obliquely and for recycling the slaked lime at the bottom of the precipitator 53 into the absorption tower 51.
  • one end of the recirculation pipe 54 communicates with the bottom of the precipitator 53, and the other end thereof communicates with the absorption tower 51, and the slaked granules returned from the recirculation pipe 54 to the absorption tower 51 are again entered into the absorption tower 51.
  • Low temperature flue gas reaction Thereby, the utilization efficiency of slaked lime is effectively improved by a plurality of cycles, thereby improving the desulfurization efficiency.
  • At least one fluidizing fan 541 may be provided at the bottom of the recirculation pipe 54 to function as a smooth return.
  • Two fluidizing fans 541 are shown in the example of Fig. 1, and two fluidizing fans 541 are spaced apart in the left-right direction. It can be understood that the number of fluidizing fans 541 can be set according to actual requirements to better meet actual requirements.
  • the particulate fuel boiler and dry desulfurization process system 100 further includes: a water tank 55 coupled to the absorption tower 51 for selectively spraying water into the absorption tower 51.
  • a water tank 55 coupled to the absorption tower 51 for selectively spraying water into the absorption tower 51.
  • the particulate fuel boiler and the dry desulfurization process system 100 are equipped with a regenerative rotary commutation heater.
  • a regenerative rotary reversing heater by carrying a regenerative rotary reversing heater, the cold air is heated to the hot air to facilitate combustion, and the exhaust gas temperature is lowered to 65 to 75 ° C, and the waste heat of the fuel is effectively utilized, and the boiler is used. The efficiency is increased by more than 3 percentage points.
  • the boiler exhaust gas temperature is lowered to 65 ⁇ 75 °C
  • the tail desulfurization process needs to undergo major changes. That is to use the WCFB dry desulfurization process, so that the tail does not need to spray water to cool down, avoid corrosion problems, and save a water spray process, which can save energy and avoid the disadvantage of ash adherence after water spray.

Abstract

一种对颗粒燃料锅炉烟气进行干法脱硫的工艺系统(100),该系统包括:颗粒燃料锅炉(1),颗粒燃料锅炉(1)限定有炉膛(11);蓄热式旋转换向加热器(2);第一烟气通路(3),第一烟气通路(3)的入口端与炉膛(11)的顶部相连通,且出口端与蓄热式旋转换向加热器(2)相连通,以将烟气通入换热器主体(21)至少成对的容纳部分(25)中的一个内并与其中容纳的热载体(23)换热;空气通路(4),空气通路(4)用于将空气至少通入换热器主体(21)成对的容纳部分(25)中的另一个内,以使得其中容纳的热载体(23)与空气进行换热,经换热后的空气被供入炉膛(11)内部;以及WCFB烟气脱硫设备(5)。该颗粒燃料锅炉及干法脱硫工艺系统不仅排烟温度低,而且锅炉的效率高,优化工艺、节约成本,而且降低了腐蚀的影响。

Description

一种对颗粒燃料锅炉烟气进行干法脱硫的工艺系统
技术领域
本发明涉及热交换技术领域, 尤其涉及一种改进的颗粒燃料锅炉及干法脱硫工艺系 统。 背景技术
目前热电领域锅炉采用管式空预器加热空气。 除了炉内脱硫外, 尾部脱硫塔采用喷 水降温后脱硫。循环流行化床锅炉技术是近十几年来迅速发展的一项高效低污染清洁燃 烧技术。 国际上这项技术在电站锅炉、工业锅炉和废弃物处理利用等领域已得到广泛的 商业应用, 并向几十万千瓦级规模的大型循环流化床锅炉发展; 国内在这方面的研究、 开发和应用也逐渐兴起, 已有数千台流化床和循环流化床锅炉投入运行中。未来的也将 是循环流化床飞速发展的一个重要时期。 其特点如下: (1)循环流化床锅炉着火、 燃烧 条件好; (2)燃烧效率高; (3)高效脱硫、 氮氧化物 (NOx)排放低; (4)燃烧强度高; (5)负 荷调节范围大, 负荷调节快; (6)易于实现灰渣综合利用; (7)燃料预处理系统简单; (8 ) 燃烧调整范围大, 负荷调整稳, 升降速度快。
但是, 这种锅炉效率受到排烟温度高的制约。 锅炉效率提高 1个百分点都是很困难 的。 发明内容
本发明旨在至少解决现有技术中存在的技术问题之一。 为此, 本发明的一个目的在 于提出一种排烟温度低且锅炉效率高的颗粒燃料锅炉及干法脱硫工艺系统。
根据本发明实施例的颗粒燃料锅炉及干法脱硫工艺系统, 包括: 颗粒燃料锅炉, 所 述颗粒燃料锅炉限定有炉膛;蓄热式旋转换向加热器,所述蓄热式旋转换向加热器包括: 换热器主体; 驱动装置, 所述驱动装置用于驱动所述换热器主体绕其中心轴线旋转; 分 隔件, 所述分隔件沿着所述中心轴线的方向设置在所述换热器主体内, 且将所述换热器 主体分隔成至少一对容纳部分, 所述每对容纳部分相对所述中心轴线成径向相对设置; 热载体,所述热载体分别容纳在所述容纳部分中,所述热载体由非金属固体材料所形成; 第一烟气通路, 所述第一烟气通路的入口端与所述炉膛的顶部相连通, 且出口端与所述 蓄热式旋转换向加热器相连通,以将炉膛内产生的烟气通入至少所述成对的所述容纳部 分中的一个内并与其中容纳的所述热载体换热; 空气通路, 所述空气通路用于将空气至 少通入所述成对的所述容纳部分中的另一个内,以使得其中容纳的所述热载体与所述空 气进行换热, 经过换热后的空气被供给至所述炉膛的内部; 以及 WCFB烟气脱硫设备, 经过所述蓄热式旋转换向加热器换热后的烟气通过第二烟气通路流入所述 WCFB烟气 脱硫设备。
根据本发明实施例的颗粒燃料锅炉及干法脱硫工艺系统, 通过设置蓄热式旋转换向 加热器和 WCFB烟气脱硫设备,蓄热式旋转换向加热器可将高温烟气降低至 65-75 °C左 右, 从而提高了锅炉系统的效率, 同时在后续烟气净化处理 WCFB烟气脱硫设备中可 以省去喷水装置, 既优化了工艺、 节约了成本又降低了腐蚀影响, 同时还有效解决了喷 水后的灰分贴壁等问题。
另外, 根据本发明的颗粒燃料锅炉及干法脱硫工艺系统还可具有如下附加技术特 征:
根据本发明的一个实施例, 所述第一烟气通路包括与所述炉膛相连通的第一尾部烟 道和与所述第一尾部烟道相连通的热风烟道,所述热风烟道的出口端与所述蓄热式旋转 换向加热器相连通。
可选地, 所述第一尾部烟道内设置有多个过热器。 由此, 通过设置过热器, 可有效 提高整个蒸汽动力装置的循环热效率。
根据本发明的一个实施例, 所述颗粒燃料锅炉及干法脱硫工艺系统进一步包括: 旋 风分离器, 所述旋风分离器分别与所述炉膛的顶部和所述第一尾部烟道相连通。 由此, 通过设置旋风分离器, 可有效地将烟气和较大的颗粒燃料、 灰粒进行分离。
进一步地, 所述旋风分离器进一步包括回料管, 所述回料管分别与所述旋风分离器 的主体以及所述炉膛的下部相连通。 由此, 通过设置回料管, 较大的颗粒燃料和灰粒可 经过回料管, 循环进入炉膛燃烧和换热。
根据本发明的一个实施例, 从所述热风烟道进入所述蓄热式旋转换向加热器内的烟 气速度可调节。 由此, 有效地提高了待预热空气的温度。
可选地, 所述热载体为 SiC或者陶瓷, 且具有小球状、 片状或者多孔状的结构。 由 此, 蓄热式旋转换向加热器可耐高温、 耐腐蚀且耐磨损。
可选地, 经过所述蓄热式旋转换向加热器换热后的烟气的温度为 65-75 °C。 在锅炉 排烟温度降低到 65~75 °C的同时, 对尾部的脱硫工艺需要产生重大变革。 即采用 WCFB 干法脱硫工艺, 从而使得尾部不需要喷水降温, 避免腐蚀问题, 烟气被降低到 65~75 °C 正好是 WCFB干法脱硫工艺的进口烟温,原来的 12CTC以上的排烟温度必须要喷水降温 到 65~75 °C, 这样节省了一道喷水工艺, 同时节能, 避免了喷水后灰贴壁的不利问题。 由此, 进入后续 WCFB烟气脱硫设备的烟气无需喷水降温。
根据本发明的一个实施例, 所述 WCFB烟气脱硫设备包括: 吸收塔, 所述第二烟气 通路与所述吸收塔的底部相连通; 消石灰仓, 所述消石灰仓设置在所述吸收塔的上部, 用于将消石灰喷入所述吸收塔; 以及除尘器, 所述除尘器与所述吸收塔相连通, 用于对 经过消石灰吸收反应后的烟气进行除尘,且经过除尘后的烟气经过第二尾部烟道排至大 气中。 由此, 通过设置吸收塔和消石灰仓, 烟气可在吸收塔中与消石灰仓喷入的消石灰 进行吸收反应, 通过设置除尘器, 脱硫后的烟气可进入除尘器中进行净化。
进一步地, 所述颗粒燃料锅炉及干法脱硫工艺系统进一步包括: 再循环管, 所述再 循环管倾斜设置且用于将所述除尘器底部的消石灰再循环至所述吸收塔内。 由此, 通过 多次循环, 有效地提高了消石灰的利用效率, 从而提高了脱硫效率。 根据本发明的一个实施例, 所述颗粒燃料锅炉及干法脱硫工艺系统进一步包括: 水 箱, 所述水箱与所述吸收塔相连, 用于选择性地向所述吸收塔内喷水。 由此, 通过设置 水箱, 可有效防止意外事故所导致的吸收塔内烟气温度过高的情况。
本发明的附加方面和优点将在下面的描述中部分给出, 部分将从下面的描述中变得 明显, 或通过本发明的实践了解到。 附图说明
本发明的上述和 /或附加的方面和优点从结合下面附图对实施例的描述中将变得明 显和容易理解, 其中:
图 1是根据本发明一个实施例的颗粒燃料锅炉及干法脱硫工艺系统的示意图; 图 2是根据本发明的一个实施例的粉状固体燃料锅炉中蓄热式旋转换向加热器的俯 视图。 具体实施方式
下面详细描述本发明的实施例, 所述实施例的示例在附图中示出, 其中自始至终相 同或类似的标号表示相同或类似的元件或具有相同或类似功能的元件。下面通过参考附 图描述的实施例是示例性的, 仅用于解释本发明, 而不能理解为对本发明的限制。
在本发明的描述中, 需要理解的是, 术语"中心"、 "上"、 "下"、 "前"、 "后"、 "左" 、 "右" 、 "竖直" 、 "水平" 、 "顶" 、 "底" 、 "内" 、 "外"等指示的方 位或位置关系为基于附图所示的方位或位置关系, 仅是为了便于描述本发明和简化描 述, 而不是指示或暗示所指的装置或元件必须具有特定的方位、 以特定的方位构造和操 作, 因此不能理解为对本发明的限制。 此外, 术语 "第一" 、 "第二 "仅用于描述目的, 而不能理解为指示或暗示相对重要性或者隐含指明所指示的技术特征的数量。 由此, 限 定有 "第一" 、 "第二" 的特征可以明示或者隐含地包括一个或者更多个该特征。 在本 发明的描述中, 除非另有说明, "多个" 的含义是两个或两个以上。
在本发明的描述中, 需要说明的是, 除非另有明确的规定和限定, 术语 "安装" 、 "相连" 、 "连接 "应做广义理解, 例如, 可以是固定连接, 也可以是可拆卸连接, 或 一体地连接; 可以是机械连接, 也可以是电连接; 可以是直接相连, 也可以通过中间媒 介间接相连, 可以是两个元件内部的连通。 对于本领域的普通技术人员而言, 可以具体 情况理解上述术语在本发明中的具体含义。
下面参考图 1描述根据本发明实施例的颗粒燃料锅炉及干法脱硫工艺系统 100。 如图 1所示, 根据本发明实施例的颗粒燃料锅炉及干法脱硫工艺系统 100包括: 颗 粒燃料锅炉 1、 蓄热式旋转换向加热器 2、 第一烟气通路 3、 空气通路 4以及 WCFB烟 气脱硫设备 5。
蓄热式旋转换向加热器 2用于将高温烟气和待预热空气进行热交换, 从而使待预热 空气的温度升高到某一定值。 蓄热式旋转换向加热器 2包括: 换热器主体 21、 驱动装 置、 分隔件 22和热载体 23, 如图 1、 2中所示。 其中, 驱动装置用于驱动换热器主体 21绕其中心轴线 24旋转。分隔件 22沿着中心轴线 24的方向设置在换热器主体 21内, 且将换热器主体 21分隔成至少一对容纳部分 25, 每对容纳部分 25相对中心轴线成径 向相对设置。 热载体分别容纳在容纳部分 25中, 热载体 23由非金属固体材料所形成。
在本发明的其中一个示例中, 换热器主体 21可形成为中空的圆柱体, 分隔件 22可 大致呈板形, 该分隔间沿着换热器主体 21中心线轴线的方向延伸, 从而将换热器主体 21 分隔成一对容纳部分, 热载体分别设在两个容纳部分中, 热载体可由非金属固体材 料制成, 烟气和待预热空气分别通入两个容纳部分中, 然后通过驱动装置驱动换热器主 体 21旋转、 烟气和与其所在的容纳部分中的热载体进行热交换、 待预热空气和与其所 在的容纳部分中的热载体进行热交换, 从而使得待预热空气温度升高。
当然, 本发明不限于此, 在本发明的另一些示例中, 分隔件 22还可将换热器主体 21分隔成两对、 三对甚至多对容纳部分。
在现有的气体换热系统中, 烟气在通过该气体换热器之后的出口温度是不能降低到 130 °C以下, 因为这会导致硫酸析出, 从而导致对该气体换热器内由金属制造的部件的 严重腐蚀。 但是, 在本发明的上述蓄热式旋转换向加热器 2中 (针对例如含硫的高温烟 气),由于热载体由例如 SiC、陶瓷等的非金属固体材料所形成,从而不用顾虑硫在 130 °C 存在露点所导致的腐蚀性问题,而可以把高温烟气的出口温度降低到硫的露点之下的温 度, 从而最大程度地进行换热, 根据本发明的一个实施例, 所述高温烟气离开所述气体 换热器的出口温度小于 130 °C, 进一步地, 所述高温烟气离开所述气体换热器的出口温 度小于 70 °C。 该温度在传统的气体换热系统中是几乎不可能实现的。 此外, 在将出口 温度降低到露点的温度之下, 水蒸汽冷凝析出为液体水, 释放了大量的潜热(液体水从 100 °C变为 10CTC的水蒸汽吸收的热量相当于水从 0°C升高至 100 °C时所吸收热量的 3 倍) 。 由于热载体由非金属固体材料所形成, 所以在硫沉积一定程度之后, 对该容纳部 分中所容纳的热载体清洗即可以继续使用,从而降低了传统的气体换热系统中所存在的 零部件替换所导致的成本增加的问题。此外, 根据发明人使用该领域内的公认计算方法 计算, 在例如燃烧锅炉的尾气换热过程中, 出口温度每降低 10 °C, 整个锅炉的效率可 以提高 0.5%, 而所释放的潜热相当于提高了整个锅炉效率的 1.5%, 从而在烟气温度降 低到例如 70°C时, 则整个锅炉的效率提高了 4.5%或者更多 (0.5%X6+1.5 ) , 从而节省 了在锅炉中的大量煤炭燃烧, 同时扩大了煤炭的适用范围, 即可以降低所使用的煤的品 位, 进一步地降低了生产成本。
其中, 颗粒燃料锅炉 1限定有炉膛 11。 第一烟气通路 3的入口端与炉膛 11的顶部 相连通, 且出口端与蓄热式旋转换向加热器 2相连通, 以将炉膛 11内产生的烟气通入 至少成对的蓄热式旋转换向加热器 2的容纳部分中的一个内,并与容纳部分中容纳的热 载体换热。空气通路 4用于将空气至少通入成对的容纳部分中的另一个内, 以使得容纳 部分中容纳的热载体与空气进行换热, 经过换热后的空气被供给至炉膛 11的内部。 经 过蓄热式旋转换向加热器 2换热后的烟气通过第二烟气通路 101流入 WCFB烟气脱硫 设备 5。
在下面的描述中, 以换热器主体 21 逆时针转动, 且烟气沿着中心轴线的右侧通入 换热器主体 21内, 待预热空气沿着中心轴线的左侧通入换热器主体 21为例进行说明。
如图 1所示, 颗粒燃料锅炉 1 内限定出炉膛 11 以用于容纳煤粉, 烟气通道 3的一 端与炉膛 11相通, 其另一端与蓄热式旋转换向加热器 2相通, 以将炉膛 11内产生的烟 气通入蓄热式旋转换向加热器 2的第一容纳部分 211中(例如为图 1中所示的蓄热式旋 转换向加热器 2的右侧) , 蓄热式旋转换向加热器 2的第二容纳部分 212中 (例如为图 1 中所示的蓄热式旋转换向加热器 2 的左侧) 用于通入待预热空气, 在换热器主体 21 处于未旋转状态时, 烟气和第一容纳部分 211中的热载体换热以使热载体的温度升高, 热载体吸收热量后, 换热器主体 21逆时针旋转, 第一容纳部分 211旋转到中心轴线的 左侧, 第二容纳部分 212旋转到中心轴线的右侧, 旋转到左侧的第一容纳部分 211内的 热载体与待加热空气进行换热以使带加热空气温度升, 同时, 烟气对旋转到右侧的第二 容纳部分 212内的热载体进行加热。
换热器主体 21继续逆时针转动, 此时第一容纳部分 211被旋转回到中心轴线的右 侧, 第二容纳部分 212 被旋转回到中心轴线的左侧, 旋转回左侧的第二容纳部分 212 内的热载体与待加热空气进行热交换,烟气对旋转回右侧的第一容纳部分 211内的热载 体进行加热, 如此循环重复, 以完成对待预热空气的加热。
在本发明的其中一个示例中, 待预热空气加热到一定温度后可从颗粒燃料锅炉 1的 底部供入炉膛 11内, 从而与颗粒燃料在炉膛 Π内进行高温氧化燃烧, 颗粒燃料可从燃 料入口 13进入炉膛 11内。
进一步地, 颗粒燃料锅炉 1 底部设有布风板 12, 预热空气经过锅炉底部的布风板 12进入炉膛 11内。
与待预热空气进行换热后的烟气通过第二烟气通路 101进入 WCFB烟气脱硫设备 5 以进行净化。
根据本发明实施例的颗粒燃料锅炉及干法脱硫工艺系统 100, 通过设置蓄热式旋转 换向加热器 2和 WCFB烟气脱硫设备 5,蓄热式旋转换向加热器 2可将高温烟气降低至 65~75 °C左右。 在锅炉排烟温度降低到 65~75 °C的同时, 对尾部的脱硫工艺需要产生重 大变革。 即采用 WCFB干法脱硫工艺, 从而使得尾部不需要喷水降温, 避免腐蚀问题, 烟气被降低到 65~75 °C正好是 WCFB干法脱硫工艺的进口烟温,原来的 120 °C以上的排 烟温度必须要喷水降温到 65~75 °C, 这样节省了一道喷水工艺, 同时节能, 避免了喷水 后灰贴壁的不利问题。
如图 1所示, 第一烟气通路 3包括与炉膛 11相连通的第一尾部烟道 31和与第一尾 部烟道 31相连通的热风烟道 32, 热风烟道 32的出口端与蓄热式旋转换向加热器 2相 连通。 也就是说, 第一烟气通路 3包括第一尾部烟道 31和热风烟道 32, 其中, 第一尾 部烟道 31的一端与炉膛 11相通, 其另一端与热风烟道 32相通, 热风烟道 32的另一端 即出口端与蓄热式旋转换向加热器 2相通。 可选地, 第一尾部烟道 31内设置有多个过热器 311。 换言之, 第一尾部烟道 31 内 可设有多个彼此间隔开的过热器 311。 由此, 通过设置过热器 311, 可有效提高整个蒸 汽动力装置的循环热效率。
在本发明的一个实施例中, 颗粒燃料锅炉及干法脱硫工艺系统 100进一步包括: 旋 风分离器 6, 旋风分离器 6分别与炉膛 11的顶部和第一尾部烟道 31相连通。 例如在图 1的示例中, 旋风分离器 6设在炉膛 11和第一尾部烟道 31的连接处, 且分别与炉膛 11 和第一尾部烟道 31相通。 由此, 通过设置旋风分离器 6, 可有效地将烟气和较大的颗 粒燃料、 灰粒进行分离。
进一步地, 旋风分离器 6进一步包括回料管 61, 回料管 61分别与旋风分离器 6的 主体以及炉膛 11的下部相连通。如图 1所示, 回料管 61的一端与旋风分离器 6的底部 相通, 其另一端与炉膛 11的下部相通。 由此, 通过设置回料管 61, 较大的颗粒燃料和 灰粒可经过回料管 61, 循环进入炉膛 11燃烧和换热。
在本发明的一个实施例中, 从热风烟道 32进入蓄热式旋转换向加热器 2内的烟气 速度可调节。 当从热风烟道 32进入蓄热式旋转换向加热器 2内的烟气速度较高时, 可 极大地提高待预热空气的温度。
可选地, 热载体为 SiC或者陶瓷, 且具有小球状、 片状或者多孔状的结构。 由此, 蓄热式旋转换向加热器 2可耐高温、 耐腐蚀且耐磨损。
可选地, 经过蓄热式旋转换向加热器 2换热后的烟气的温度为 65-75 °C。 由此, 进 入后续 WCFB烟气脱硫设备 5的烟气无需喷水降温。
在本发明的一个实施例中, WCFB烟气脱硫设备 5包括: 吸收塔 51、 消石灰仓 52 以及除尘器 53。 其中, 第二烟气通路 101与吸收塔 51的底部相连通。 消石灰仓 52设 置在吸收塔 51的上部, 用于将消石灰喷入吸收塔 51。 除尘器 53与吸收塔 51相连通, 用于对经过消石灰吸收反应后的烟气进行除尘,且经过除尘后的烟气经过第二尾部烟道 排至大气中。 由此, 通过设置吸收塔 51和消石灰仓 52, 烟气可在吸收塔 51 中与消石 灰仓 52喷入的消石灰进行吸收反应, 通过设置除尘器 53, 脱硫后的烟气可进入除尘器 53中进行净化。
在图 1的示例中, 第二烟气通路 101的一端与蓄热式旋转换向加热器 2相通, 其另 一端与吸收塔 51的底部相通, 从而将蓄热式旋转换向加热器 2中温度降低的烟气通入 吸收塔 51中,烟气上升到吸收塔 51的上部与消石灰仓 52喷入的消石灰进行吸收反应, 然后进入除尘器 53除尘, 脱硫后的净化烟气离开除尘器 53进入第二尾部烟道, 最后由 烟囱排入大气。
进一步地, 颗粒燃料锅炉及干法脱硫工艺系统 100进一步包括: 再循环管 54, 再循 环管 54倾斜设置且用于将除尘器 53底部的消石灰再循环至吸收塔 51内。如图 1所示, 再循环管 54的一端与除尘器 53的底部相通, 其另一端与吸收塔 51相通, 从再循环管 54返回到吸收塔 51的含消石灰颗粒再次与进入吸收塔 51的低温烟气反应。 由此, 通 过多次循环, 有效地提高了消石灰的利用效率, 从而提高了脱硫效率。 在本发明的其中一个示例中, 再循环管 54 的底部还可设有至少一个流化风机 541 以起到顺利返料的作用。 在图 1的示例中示出了两个流化风机 541, 两个流化风机 541 在左右方向上间隔开设置。可以理解的是,流化风机 541的数量可以根据实际要求设置, 以更好地满足实际要求。
在本发明的一个实施例中, 颗粒燃料锅炉及干法脱硫工艺系统 100进一步包括: 水 箱 55, 水箱 55与吸收塔 51相连, 用于选择性地向吸收塔 51内喷水。 当经过蓄热式旋 转换向加热器 2换热后的烟气的温度为 65-75 °C时, 由于 65-75 °C是 WCFB的理想反应 温度, 此时无需对吸收塔 51内的烟气进行喷水降温。 由此, 通过设置水箱 55, 可有效 防止意外事故所导致的吸收塔 51内烟气温度过高的情况。
综上, 根据本发明的颗粒燃料锅炉及干法脱硫工艺系统 100搭载了蓄热式旋转换向 加热器。 根据发明人的计算, 通过搭载蓄热式旋转换向加热器, 将冷风加热到热风利于 燃烧的同时, 将排烟温度降到 65~75 °C, 有效的利用了燃料的余热, 并将锅炉的效率提 高 3个百分点以上。 此外, 由于在锅炉排烟温度降低到 65~75 °C的同时, 对尾部的脱硫 工艺需要产生重大变革。 即采用 WCFB干法脱硫工艺, 从而使得尾部不需要喷水降温, 避免腐蚀问题, 同时节省了一道喷水工艺, 起到节能的作用, 避免了喷水后灰贴壁的不 利问题。
在本说明书的描述中, 参考术语 "一个实施例"、 "一些实施例"、 "示意性实施例"、 "示 例"、 "具体示例"、 或 "一些示例"等的描述意指结合该实施例或示例描述的具体特征、 结 构、 材料或者特点包含于本发明的至少一个实施例或示例中。 在本说明书中, 对上述术语 的示意性表述不一定指的是相同的实施例或示例。 而且, 描述的具体特征、 结构、 材料或 者特点可以在任何的一个或多个实施例或示例中以合适的方式结合。
尽管已经示出和描述了本发明的实施例, 本领域的普通技术人员可以理解: 在不脱 离本发明的原理和宗旨的情况下可以对这些实施例进行多种变化、 修改、 替换和变型, 本发明的范围由权利要求及其等同物限定。

Claims

权利要求书
1、 一种颗粒燃料锅炉及干法脱硫工艺系统, 其特征在于, 包括:
颗粒燃料锅炉, 所述颗粒燃料锅炉限定有炉膛;
蓄热式旋转换向加热器, 所述蓄热式旋转换向加热器包括:
换热器主体;
驱动装置, 所述驱动装置用于驱动所述换热器主体绕其中心轴线旋转; 分隔件, 所述分隔件沿着所述中心轴线的方向设置在所述换热器主体内, 且将 所述换热器主体分隔成至少一对容纳部分,所述每对容纳部分相对所述中心轴线成径向 相对设置;
热载体, 所述热载体分别容纳在所述容纳部分中, 所述热载体由非金属固体材 料所形成;
第一烟气通路, 所述第一烟气通路的入口端与所述炉膛的顶部相连通, 且出口端与 所述蓄热式旋转换向加热器相连通,以将炉膛内产生的烟气通入至少所述成对的所述容 纳部分中的一个内并与其中容纳的所述热载体换热;
空气通路, 所述空气通路用于将空气至少通入所述成对的所述容纳部分中的另一个 内, 以使得其中容纳的所述热载体与所述空气进行换热, 经过换热后的空气被供给至所 述炉膛的内部; 以及
WCFB烟气脱硫设备, 经过所述蓄热式旋转换向加热器换热后的烟气通过第二烟气 通路流入所述 WCFB烟气脱硫设备。
2、 根据权利要求 1 所述的颗粒燃料锅炉及干法脱硫工艺系统, 其特征在于, 所述 第一烟气通路包括与所述炉膛相连通的第一尾部烟道和与所述第一尾部烟道相连通的 热风烟道, 所述热风烟道的出口端与所述蓄热式旋转换向加热器相连通。
3、 根据权利要求 2所述的颗粒燃料锅炉及干法脱硫工艺系统, 其特征在于, 所述 第一尾部烟道内设置有多个过热器。
4、 根据权利要求 3 所述的颗粒燃料锅炉及干法脱硫工艺系统, 其特征在于, 进一 步包括: 旋风分离器, 所述旋风分离器分别与所述炉膛的顶部和所述第一尾部烟道相连 通。
5、 根据权利要求 4所述的颗粒燃料锅炉及干法脱硫工艺系统, 其特征在于, 所述 旋风分离器进一步包括回料管,所述回料管分别与所述旋风分离器的主体以及所述炉膛 的下部相连通。
6、 根据权利要求 2所述的颗粒燃料锅炉及干法脱硫工艺系统, 其特征在于, 从所 述热风烟道进入所述蓄热式旋转换向加热器内的烟气速度可调节。
7、 根据权利要求 1 所述的颗粒燃料锅炉及干法脱硫工艺系统, 其特征在于, 所述 热载体为 SiC或者陶瓷。
8、 根据权利要求 1 所述的颗粒燃料锅炉及干法脱硫工艺系统, 其特征在于, 经过 所述蓄热式旋转换向加热器换热后的烟气的温度为 65-75 °C。
9、 根据权利要求 1 所述的颗粒燃料锅炉及干法脱硫工艺系统, 其特征在于, 所述 WCFB烟气脱硫设备包括:
吸收塔, 所述第二烟气通路与所述吸收塔的底部相连通;
消石灰仓,所述消石灰仓设置在所述吸收塔的上部,用于将消石灰喷入所述吸收塔; 以及
除尘器, 所述除尘器与所述吸收塔相连通, 用于对经过消石灰吸收反应后的烟气进 行除尘, 且经过除尘后的烟气经过第二尾部烟道排至大气中。
10、 根据权利要求 9所述的颗粒燃料锅炉及干法脱硫工艺系统, 其特征在于, 进一 步包括:
再循环管, 所述再循环管倾斜设置且用于将所述除尘器底部的消石灰再循环至所述 吸收塔内。
11、 根据权利要求 10所述的颗粒燃料锅炉及干法脱硫工艺系统, 其特征在于, 进 一步包括:
水箱, 所述水箱与所述吸收塔相连, 用于选择性地向所述吸收塔内喷水。
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