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CN110813007A - Waste gas waste heat recovery and purification process of mixed gas heating system - Google Patents

Waste gas waste heat recovery and purification process of mixed gas heating system Download PDF

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CN110813007A
CN110813007A CN201911215152.2A CN201911215152A CN110813007A CN 110813007 A CN110813007 A CN 110813007A CN 201911215152 A CN201911215152 A CN 201911215152A CN 110813007 A CN110813007 A CN 110813007A
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waste
flue gas
gas
waste flue
heat
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王满
李旭东
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Acre Coking and Refractory Engineering Consulting Corp MCC
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    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
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    • B01D53/34Chemical or biological purification of waste gases
    • B01D53/46Removing components of defined structure
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    • B01D53/50Sulfur oxides
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    • BPERFORMING OPERATIONS; TRANSPORTING
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    • 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
    • B01D53/74General processes for purification of waste gases; Apparatus or devices specially adapted therefor
    • B01D53/86Catalytic processes
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    • CCHEMISTRY; METALLURGY
    • C10PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
    • C10BDESTRUCTIVE DISTILLATION OF CARBONACEOUS MATERIALS FOR PRODUCTION OF GAS, COKE, TAR, OR SIMILAR MATERIALS
    • C10B39/00Cooling or quenching coke
    • C10B39/02Dry cooling outside the oven
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
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    • F22BMETHODS OF STEAM GENERATION; STEAM BOILERS
    • F22B1/00Methods of steam generation characterised by form of heating method
    • F22B1/02Methods of steam generation characterised by form of heating method by exploitation of the heat content of hot heat carriers
    • F22B1/18Methods of steam generation characterised by form of heating method by exploitation of the heat content of hot heat carriers the heat carrier being a hot gas, e.g. waste gas such as exhaust gas of internal-combustion engines
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
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    • F22D1/00Feed-water heaters, i.e. economisers or like preheaters
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    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
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    • Y02A50/00TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE in human health protection, e.g. against extreme weather
    • Y02A50/20Air quality improvement or preservation, e.g. vehicle emission control or emission reduction by using catalytic converters
    • 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
    • Y02ATECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
    • Y02A50/00TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE in human health protection, e.g. against extreme weather
    • Y02A50/20Air quality improvement or preservation, e.g. vehicle emission control or emission reduction by using catalytic converters
    • Y02A50/2351Atmospheric particulate matter [PM], e.g. carbon smoke microparticles, smog, aerosol particles, dust
    • 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
    • Y02P20/129Energy recovery, e.g. by cogeneration, H2recovery or pressure recovery turbines

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Abstract

The invention relates to a waste gas waste heat recovery and purification process of a mixed gas heating system, wherein coke oven waste flue gas generated in the heating process of a coke oven is sent into a dry quenching furnace to cool high-temperature coke after heat exchange, temperature reduction and carbon dioxide removal treatment; dry quenching fire grateThe discharged waste flue gas enters a primary dust remover, a desulfurizer is sprayed into the primary dust remover, and SO in the waste flue gas is removed2Removing; the desulfurized waste flue gas enters a waste heat boiler to recover heat carried by the waste flue gas, and the outlet temperature of the waste flue gas is controlled by the waste heat boiler, so that the waste flue gas discharged after heat exchange directly enters an SCR denitration device for denitration; and the waste flue gas after denitration is sent to a chimney for discharging after heat exchange, temperature reduction and secondary dust removal. The invention can realize the recovery of the waste heat of the red coke and the waste heat of the waste flue gas of the coke oven, and simultaneously, can complete the purification of the waste flue gas of the coke oven, so that the flue gas emission meets the national standard, the air pollution is reduced, the greenhouse gas emission is reduced, and the quality of the coke is ensured.

Description

一种混合煤气加热系统废气余热回收及净化工艺A kind of waste heat recovery and purification process of mixed gas heating system waste gas

技术领域technical field

本发明涉及炼焦余热回收及烟气净化技术领域,尤其涉及一种混合煤气加热系统废气余热回收及净化工艺。The invention relates to the technical field of coking waste heat recovery and flue gas purification, in particular to a waste heat recovery and purification process of waste gas of a mixed gas heating system.

背景技术Background technique

在焦炉生产过程中,煤气(焦炉煤气或混合煤气)在燃烧室燃烧同时向炭化室供热,燃烧产生的高温烟气经蓄热室换热后外排,此时烟气温度达200-300℃,称为焦炉废烟气。焦炉生产使用以高炉煤气为主掺烧焦炉煤气的混合煤气加热系统产生的废烟气中除空气中携带的N2、燃烧后生成的CO2和H2O外,还含有少量的剩余O2及燃烧过程中生成的SO2、NOX,焦炉废烟气中所含SO2是大气的重要污染源之一,NOX是引起光化学雾污染源之一,二者对大气环境造成的污染和危害甚大。In the coke oven production process, the gas (coke oven gas or mixed gas) is burned in the combustion chamber while supplying heat to the carbonization chamber. -300℃, called coke oven exhaust gas. In coke oven production, in addition to the N 2 carried in the air, the CO 2 and H 2 O generated after combustion, the waste flue gas generated by the mixed gas heating system with blast furnace gas as the main blending coke oven gas also contains a small amount of residual gas. O 2 and SO 2 , NO X generated in the combustion process, SO 2 contained in coke oven flue gas is one of the important pollution sources of the atmosphere, and NO X is one of the sources of photochemical fog pollution, both of which cause pollution to the atmospheric environment. and very dangerous.

《炼焦化学工业污染物排放标准》(GB16171-2012)中明确规定:从2015年1月1日起焦炉烟气中二氧化硫排放不得超过50mg/m3,氮氧化物排放不得超过500mg/m3,而随着我国对生态环保的重视程度增加,越来越多的地方和行业开始执行更加严格的特别排放标准,对焦炉废烟气中的污染物进行综合治理已成为对焦化生产企业的基本要求。目前对焦炉废烟气的净化,多采用碳酸钠法脱硫+SCR脱硝的工艺流程。选择性催化还原技术(SCR)是目前最成熟的烟气脱硝技术,它是利用还原剂(NH3,尿素)在金属催化剂作用下,选择性地与NOx反应生成N2和H2O,从而使烟气达到排放要求。主流SCR反应器又分为中温(260℃~380℃)催化脱硝和低温(120℃~300℃)催化脱硝。由于焦炉废烟气进入脱硫脱硝装置前,一般输送过程距离较长,管道散热量大导致降温明显,因此需要配置烟气加热系统以确保焦炉废烟气的温度满足SCR脱硝反应的条件。"Coking Chemical Industry Pollutant Emission Standards" (GB16171-2012) clearly stipulates that from January 1, 2015, the emission of sulfur dioxide in coke oven flue gas shall not exceed 50mg/m 3 and the emission of nitrogen oxides shall not exceed 500mg/m 3 However, with the increasing emphasis on ecological environmental protection in China, more and more places and industries have begun to implement more stringent special emission standards. basic requirements. At present, the purification of coke oven waste flue gas mostly adopts the process of sodium carbonate desulfurization + SCR denitration. Selective Catalytic Reduction (SCR) is the most mature flue gas denitrification technology. It uses reducing agents (NH3, urea) to selectively react with NOx under the action of metal catalysts to generate N2 and H2O , so that The flue gas meets the emission requirements. Mainstream SCR reactors are further divided into medium temperature (260℃~380℃) catalytic denitrification and low temperature (120℃~300℃) catalytic denitrification. Before the coke oven exhaust flue gas enters the desulfurization and denitrification device, the conveying distance is generally long, and the pipeline heat dissipation is large, which leads to obvious cooling. Therefore, it is necessary to configure a flue gas heating system to ensure that the temperature of the coke oven exhaust flue gas meets the conditions of SCR denitration reaction.

干熄焦工艺是一种高效的利用惰性气体对高温(950~1100℃)红焦显热连续进行回收和利用的技术,其主要由干熄炉、循环风机、一次除尘器、锅炉、二次除尘器等设备及管道连接组成。在熄焦过程中,红焦由干熄炉顶部进入与循环冷却气体逆向流动完成对流换热过程,冷却后的固体颗粒由竖炉底部排出,充分吸收了红焦显热的高温气体经干熄炉排气口进入后续装置进行余热利用,如产生蒸汽或发电等。该工艺具有余热回收率高、运行环保等优点被广泛使用。但在干熄焦过程中,因红焦中残余挥发分的燃烧及部分焦粉的烧损,循环气体中含有一定量的二氧化硫,在运行过程中不断积累,致使风机后放散的循环气体中二氧化硫含量较高,因此要求对放散部分的循环气体在排入大气前需进行脱硫净化处理。对这部分放散循环气体的脱硫净化处理,目前做法不一,有为其单独设置脱硫净化装置的,但需要投入设施完备的全套系统,增加一定的投资。也有将其导入焦炉废烟气脱硫脱硝系统的,但因该部分放散气体含有较高浓度的粉尘,需要增设必要的除尘设施,同时还会在一定程度上降低焦炉废烟气的温度,从而给焦炉废烟气脱硫脱硝系统的运行造成不利影响。The CDQ process is a high-efficiency technology that uses inert gas to continuously recover and utilize the sensible heat of high temperature (950-1100℃) red coke. It mainly consists of CDQ furnace, circulating fan, primary dust collector, boiler, secondary Dust collector and other equipment and pipeline connections. In the process of coke quenching, the red coke enters from the top of the CDQ furnace and flows in the opposite direction with the circulating cooling gas to complete the convective heat exchange process. The cooled solid particles are discharged from the bottom of the shaft furnace, and the high temperature gas that fully absorbs the sensible heat of the red coke is passed through the CDQ. The exhaust port of the furnace enters the subsequent device for waste heat utilization, such as steam generation or power generation. This process has the advantages of high waste heat recovery rate and environmentally friendly operation and is widely used. However, in the process of CDQ, due to the burning of residual volatiles in red coke and the burning loss of part of coke powder, the circulating gas contains a certain amount of sulfur dioxide, which accumulates continuously during operation, resulting in sulfur dioxide in the circulating gas released after the fan. The content is relatively high, so it is required to carry out desulfurization and purification treatment on the circulating gas of the dissipated part before it is discharged into the atmosphere. For the desulfurization and purification treatment of this part of the released circulating gas, the current methods are different. Some of them have a separate desulfurization and purification device, but they need to invest in a complete system with complete facilities and increase a certain amount of investment. It is also introduced into the coke oven waste flue gas desulfurization and denitrification system, but because this part of the released gas contains a high concentration of dust, it is necessary to add necessary dust removal facilities, and at the same time, it will reduce the temperature of the coke oven waste flue gas to a certain extent. This will adversely affect the operation of the coke oven waste flue gas desulfurization and denitrification system.

为了对红焦余热及焦炉废烟气余热的有效回收,同时完成对焦炉废烟气的净化,可采取将混合煤气加热燃烧后产生的废烟气余热回收及脱硫脱硝净化工艺与干熄焦工艺融合形成一个工艺系统,但由于废烟气中因燃烧而生成的CO2体积占到了废气的约20%左右,当废烟气中的CO2在干熄炉内与炽热的焦炭接触时,会与焦炭发生一定程度的碳熔反应,生成CO,不但增加了废烟气中可燃成分的含量,给系统的运行带来一定的安全隐患,同时还因碳熔反应的发生而消耗掉一定数量的焦炭,造成焦炭的“烧损”和焦炭质量的降低。因此,需要采取必要的措施解决上述问题。In order to effectively recover the waste heat of red coke and coke oven waste flue gas, and at the same time complete the purification of coke oven waste flue gas, the waste flue gas waste heat recovery and desulfurization and denitration purification process and dry quenching process can be adopted after heating and burning the mixed gas. The coke process is integrated to form a process system, but since the volume of CO 2 generated by combustion in the waste flue gas accounts for about 20% of the exhaust gas, when the CO 2 in the waste flue gas contacts the hot coke in the CDQ furnace , it will have a certain degree of carbon melting reaction with coke to generate CO, which not only increases the content of combustible components in the flue gas, but also brings certain safety hazards to the operation of the system. The amount of coke causes the "burning loss" of the coke and the reduction of the quality of the coke. Therefore, it is necessary to take necessary measures to solve the above problems.

发明内容SUMMARY OF THE INVENTION

本发明提供了一种混合煤气加热系统废气余热回收及净化工艺,通过将混合煤气加热燃烧后产生的废烟气余热回收及脱硫脱硝净化工艺与干熄焦工艺有机融合,并对废烟气中二氧化碳进行脱除,在实现红焦余热及焦炉废烟气余热回收的同时,完成对焦炉废烟气的净化,使烟气排放满足国家标准,减少大气污染,降低温室气体排放,保证焦炭的质量。The invention provides a waste heat recovery and purification process of the waste gas of a mixed gas heating system. The waste heat recovery and desulfurization and denitration purification process of the waste flue gas generated after the heating and combustion of the mixed gas is organically integrated with the coke dry quenching process. The carbon dioxide is removed to realize the recovery of the waste heat of the red coke and the waste heat of the coke oven waste flue gas, and at the same time complete the purification of the coke oven waste flue gas, so that the flue gas emissions meet the national standards, reduce air pollution, reduce greenhouse gas emissions, and ensure coke coke emissions. the quality of.

为了达到上述目的,本发明采用以下技术方案实现:In order to achieve the above object, the present invention adopts the following technical solutions to realize:

一种混合煤气加热系统废气余热回收及净化工艺,焦炉加热过程中产生的焦炉废烟气经换热降温、脱二氧化碳处理后送入干熄炉,对高温焦炭进行冷却;干熄炉排出的废烟气进入一次除尘器,向一次除尘器中喷入脱硫剂,将废烟气中的SO2脱除;脱硫后的废烟气进入余热锅炉对其携带的热量进行回收,通过余热锅炉对废烟气的出口温度进行控制,使换热后排出的废烟气直接进入SCR脱硝装置进行脱硝;脱硝后的废烟气再经换热降温及二次除尘后送往烟囱外排。A process for recovering and purifying waste heat from waste gas of a mixed gas heating system. The coke oven waste flue gas produced in the coke oven heating process is sent to a dry quenching furnace after heat exchange, cooling, and decarbonation treatment to cool high-temperature coke; The waste flue gas enters the primary dust collector, and the desulfurizer is sprayed into the primary dust collector to remove SO 2 in the waste flue gas; the waste flue gas after desulfurization enters the waste heat boiler to recover the heat carried by it, and passes through the waste heat boiler. The outlet temperature of the waste flue gas is controlled, so that the waste flue gas discharged after heat exchange directly enters the SCR denitrification device for denitration; the waste flue gas after denitration is cooled by heat exchange and secondary dust is sent to the chimney for discharge.

一种混合煤气加热系统废气余热回收及净化工艺,具体包括如下步骤:A waste heat recovery and purification process of waste gas of a mixed gas heating system, specifically comprising the following steps:

1)通过焦炉废烟气引入系统,将焦炉加热过程中产生的焦炉废烟气从焦炉总烟道中引出,进入热交换器一;1) Through the coke oven waste flue gas introduction system, the coke oven waste flue gas generated during the coke oven heating process is led out from the coke oven general flue and enters the first heat exchanger;

2)在热交换器一内,温度为200℃~300℃的焦炉废烟气通过间接换热的方式被来自余热锅炉的除盐水冷却至70℃以下,焦炉废烟气携带的部分热量被除盐水回收后送入余热锅炉,换热后的焦炉废烟气进入脱二氧化碳装置;2) In heat exchanger 1, the coke oven exhaust gas with a temperature of 200℃~300℃ is cooled to below 70℃ by the demineralized water from the waste heat boiler through indirect heat exchange, and part of the heat carried by the coke oven exhaust gas After being recovered by demineralized water, it is sent to the waste heat boiler, and the coke oven waste flue gas after heat exchange enters the decarbonation device;

3)在脱二氧化碳装置内,废烟气中的二氧化碳气体被分离回收,剩余的废烟气由干熄炉下部的供气装置进入干熄炉内;3) In the decarbonation device, the carbon dioxide gas in the waste flue gas is separated and recovered, and the remaining waste flue gas enters the CD quenching furnace from the gas supply device at the lower part of the CD quenching furnace;

4)在干熄炉内,焦炉废烟气与高温焦炭逆向接触,吸收焦炭热量后的废烟气从干熄炉上段排出后进入一次除尘器,经过冷却的焦炭通过干熄炉下部的排焦系统排出;4) In the CDQ furnace, the coke oven waste flue gas is in reverse contact with the high-temperature coke, and the waste flue gas after absorbing the coke heat is discharged from the upper section of the CDQ furnace and then enters the primary dust collector, and the cooled coke passes through the lower part of the CDQ furnace. coke system discharge;

1)5)干法脱硫装置采用NaHCO3作为脱硫剂,通过NaHCO3输送管道向一次除尘器内喷入NaHCO3,在一次除尘器中,NaHCO3与废烟气中的SO2充分接触发生反应,生成NaHSO3、Na2SO3,实现废烟气中SO2的脱除;生成的NaHSO3、Na2SO3及废烟气携带的焦粉在一次除尘器内通过惯性碰撞和沉降作用从烟气中分离;1) 5) The dry desulfurization device uses NaHCO 3 as the desulfurizing agent, and injects NaHCO 3 into the primary dust collector through the NaHCO 3 conveying pipeline. In the primary dust collector, NaHCO 3 fully contacts and reacts with SO 2 in the exhaust gas. , generate NaHSO 3 , Na 2 SO 3 , and realize the removal of SO 2 in the waste flue gas; the generated NaHSO 3 , Na 2 SO 3 and the coke powder carried by the waste flue gas are removed from the primary dust collector by inertial collision and sedimentation. separation from flue gas;

6)经过一次除尘后的废烟气进入余热锅炉,余热锅炉利用废烟气携带的热量产生高温高压蒸汽用于发电或设备的驱动,实现炼焦余热的回收利用;经过余热锅炉回收热量后的废烟气通过管道直接进入SCR脱硝装置进行脱硝处理;6) The waste flue gas after a dust removal enters the waste heat boiler, and the waste heat boiler uses the heat carried by the waste flue gas to generate high-temperature and high-pressure steam for power generation or equipment driving, so as to realize the recovery and utilization of coking waste heat; the waste heat after the heat recovery by the waste heat boiler The flue gas directly enters the SCR denitration device through the pipeline for denitration treatment;

7)经SCR脱硝装置脱硝处理后的废烟气进入热交换器二进行降温处理;在热交换器二内,废烟气通过间接换热的方式被来自余热锅炉的除盐水冷却,废烟气携带的部分热量被除盐水回收后送入余热锅炉,降温后的废烟气进入二次除尘器;7) The waste flue gas after being denitrified by the SCR denitration device enters the second heat exchanger for cooling treatment; in the second heat exchanger, the waste flue gas is cooled by the demineralized water from the waste heat boiler through indirect heat exchange, and the waste flue gas is cooled by the demineralized water from the waste heat boiler. Part of the carried heat is recovered by the demineralized water and sent to the waste heat boiler, and the cooled waste flue gas enters the secondary dust collector;

8)在二次除尘器内,采用过滤除尘方式脱除废烟气中携带的固体颗粒物及粉尘,所捕集到的颗粒物和粉尘经二次除尘器下部的粉尘收集装置回收后外排处理;过滤除尘后的废烟气通过引风机输送后送往烟囱排放。8) In the secondary dust collector, the solid particulate matter and dust carried in the waste flue gas are removed by filtering and dust removal, and the captured particulate matter and dust are recovered by the dust collection device at the lower part of the secondary dust collector and then discharged for treatment; The filtered and dedusted waste flue gas is transported by the induced draft fan and sent to the chimney for discharge.

所述余热锅炉的烟气出口温度控制在300℃~400℃之间。The flue gas outlet temperature of the waste heat boiler is controlled between 300°C and 400°C.

所述一次除尘器为惯性重力除尘器。The primary dust collector is an inertial gravity dust collector.

所述二次除尘器为袋式除尘器。The secondary dust collector is a bag filter.

所述脱二氧化碳装置采用物理化学溶剂吸收法、固体吸附法或膜气体分离法对二氧化碳进行分离回收。The carbon dioxide removal device adopts a physical and chemical solvent absorption method, a solid adsorption method or a membrane gas separation method to separate and recover carbon dioxide.

与现有技术相比,本发明的有益效果是:Compared with the prior art, the beneficial effects of the present invention are:

1)本发明利用焦炉废烟气作为换热介质对高温焦炭进行冷却,将炼焦生产过程中高温红焦和焦炉废烟气两大余热资源的余热回收有机地整合在一个余热回收系统内,在提高焦炉废烟气余热回收热品质、增加干熄焦余热利用能力的同时,实现了焦炉废烟气的脱硫脱硝净化处理,减少了除尘设施、风机等相关烟气处理设备和动力设施的配置,整体工艺布局简单,占地少,一次性建设成本及运行成本低;1) The present invention uses coke oven waste flue gas as a heat exchange medium to cool high-temperature coke, and organically integrates the waste heat recovery of the two waste heat resources of high temperature red coke and coke oven waste flue gas in the coking production process into a waste heat recovery system. , while improving the heat quality of waste heat recovery from coke oven waste flue gas and increasing the utilization capacity of CDQ waste heat, the desulfurization and denitration purification treatment of coke oven waste flue gas is realized, and the related flue gas treatment equipment and power such as dust removal facilities and fans are reduced. The configuration of facilities, the overall process layout is simple, the land occupation is small, and the one-time construction cost and operation cost are low;

2)利用脱二氧化碳装置对焦炉废烟气中的二氧化碳气体进行回收,减少因废气中二氧化碳跟红焦发生的碳溶反应造成的焦炭损失,同时降低温室气体的排放,保护环境。2) The carbon dioxide gas in the coke oven exhaust flue gas is recovered by the decarbonation device to reduce the coke loss caused by the carbon-dissolving reaction between the carbon dioxide in the exhaust gas and the red coke, and at the same time reduce the emission of greenhouse gases and protect the environment.

3)利用高温焦炭对焦炉废烟气进行加热,通过控制余热锅炉后焦炉废烟气的温度,形成适合于中温SCR脱硝催化反应的烟气环境,无需再另外增设加热系统,降低了脱硝催化剂成本,提高了脱硝效率;3) Use high-temperature coke coke oven waste flue gas for heating, and by controlling the temperature of coke oven waste flue gas behind the waste heat boiler, a flue gas environment suitable for the catalytic reaction of medium-temperature SCR denitration is formed, and there is no need to add additional heating systems, reducing denitrification. Catalyst cost, improved denitration efficiency;

4)SCR脱硝后采用袋式除尘装置对废烟气进行净化处理,除尘效率高,二次除尘器排出粉尘浓度在10mg/m3以下,从而使设置在二次除尘器后的引风机无需配置专用的耐磨损措施,与传统的干熄焦循环风机相比,可显著降低风机的更换和维护成本,减少故障发生率,提高干熄焦连续运转的稳定性;4) After SCR denitration, a bag-type dust removal device is used to purify the waste flue gas. The dust removal efficiency is high. The dust concentration of the secondary dust collector is below 10mg/ m3 , so that the induced draft fan installed after the secondary dust collector does not need to be configured. The special wear-resistant measures, compared with the traditional CDQ circulating fan, can significantly reduce the replacement and maintenance costs of the fan, reduce the failure rate, and improve the stability of CDQ continuous operation;

5)本发明在对焦炉废烟气进行脱硫脱硝净化处理的同时,与现有干熄焦工艺相比,无需考虑放散循环气体的脱硫问题,排入烟囱的气体完全能够达到环保标准要求。5) The present invention performs desulfurization and denitrification purification treatment of coke oven waste flue gas. Compared with the existing CDQ process, the present invention does not need to consider the desulfurization problem of releasing circulating gas, and the gas discharged into the chimney can fully meet the requirements of environmental protection standards.

附图说明Description of drawings

图1是本发明所述一种混合煤气加热系统废气余热回收及净化工艺的流程示意图。FIG. 1 is a schematic flow chart of the waste heat recovery and purification process of waste gas of a mixed gas heating system according to the present invention.

图中:1.干熄炉 2.干法脱硫装置 3.一次除尘器 4.余热锅炉 5.SCR脱硝装置 6.二次除尘器 7.粉尘收集装置 8.热交换器二 9.引风机 10.热交换器一 11.焦炉总烟道12.烟囱 13.烟道翻板 14.高温焦炭 15.脱二氧化碳装置In the picture: 1. CDQ furnace 2. Dry desulfurization device 3. Primary dust collector 4. Waste heat boiler 5. SCR denitration device 6. Secondary dust collector 7. Dust collection device 8. Heat exchanger II 9. Induced draft fan 10 . Heat exchanger one 11. Coke oven general flue 12. Chimney 13. Flue flap 14. High temperature coke 15. Decarbonation device

具体实施方式Detailed ways

下面结合附图对本发明的具体实施方式作进一步说明:The specific embodiments of the present invention will be further described below in conjunction with the accompanying drawings:

如图1所示,本发明所述一种混合煤气加热系统废气余热回收及净化工艺,焦炉加热过程中产生的焦炉废烟气经换热降温、脱二氧化碳处理后送入干熄炉1,对高温焦炭14进行冷却;干熄炉1排出的废烟气进入一次除尘器3,向一次除尘器3中喷入脱硫剂,将废烟气中的SO2脱除;脱硫后的废烟气进入余热锅炉4对其携带的热量进行回收,通过余热锅炉4对废烟气的出口温度进行控制,使换热后排出的废烟气直接进入SCR脱硝装置5进行脱硝;脱硝后的废烟气再经换热降温及二次除尘后送往烟囱12外排。As shown in Figure 1, the waste heat recovery and purification process of the waste gas of a mixed gas heating system according to the present invention, the coke oven waste gas produced in the coke oven heating process is sent to the CDQ 1 after heat exchange cooling and decarbonation treatment , to cool the high temperature coke 14; the waste flue gas discharged from the CDQ furnace 1 enters the primary dust collector 3, and a desulfurizer is sprayed into the primary dust collector 3 to remove SO 2 in the waste flue gas; the waste smoke after desulfurization The gas enters the waste heat boiler 4 to recover the heat carried by it, and the outlet temperature of the waste flue gas is controlled by the waste heat boiler 4, so that the waste flue gas discharged after heat exchange directly enters the SCR denitration device 5 for denitrification; The gas is then sent to the chimney 12 for external discharge after being cooled by heat exchange and secondary dust removal.

一种混合煤气加热系统废气余热回收及净化工艺,具体包括如下步骤:A waste heat recovery and purification process of waste gas of a mixed gas heating system, specifically comprising the following steps:

1)通过焦炉废烟气引入系统,将焦炉加热过程中产生的焦炉废烟气从焦炉总烟道11中引出,进入热交换器一10;1) Through the coke oven waste flue gas introduction system, the coke oven waste flue gas generated during the coke oven heating process is led out from the coke oven general flue 11 and enters the heat exchanger one 10;

2)在热交换器一10内,温度为200℃~300℃的焦炉废烟气通过间接换热的方式被来自余热锅炉4的除盐水冷却至70℃以下,焦炉废烟气携带的部分热量被除盐水回收后送入余热锅炉4,换热后的焦炉废烟气进入脱二氧化碳装置15;2) In the heat exchanger 10, the coke oven waste flue gas with a temperature of 200°C to 300°C is cooled to below 70°C by the demineralized water from the waste heat boiler 4 through indirect heat exchange. Part of the heat is recovered by the demineralized water and sent to the waste heat boiler 4, and the coke oven waste flue gas after heat exchange enters the decarbonation device 15;

3)在脱二氧化碳装置15内,废烟气中的二氧化碳气体被分离回收,剩余的废烟气由干熄炉1下部的供气装置进入干熄炉1内;3) In the decarbonation device 15, the carbon dioxide gas in the waste flue gas is separated and recovered, and the remaining waste flue gas enters the CDQ furnace 1 from the gas supply device at the lower part of the CDQ furnace 1;

4)在干熄炉1内,焦炉废烟气与高温焦炭14逆向接触,吸收焦炭热量后的废烟气从干熄炉1上段排出后进入一次除尘器3,经过冷却的焦炭通过干熄炉1下部的排焦系统排出;4) In the CDQ furnace 1, the coke oven waste flue gas is in reverse contact with the high-temperature coke 14, and the waste flue gas after absorbing the coke heat is discharged from the upper section of the CDQ furnace 1 and then enters the primary dust collector 3, and the cooled coke passes through the CDQ. The coke removal system at the lower part of furnace 1 is discharged;

2)5)干法脱硫装置2采用NaHCO3作为脱硫剂,通过NaHCO3输送管道向一次除尘器3内喷入NaHCO3,在一次除尘器3中,NaHCO3与废烟气中的SO2充分接触发生反应,生成NaHSO3、Na2SO3,实现废烟气中SO2的脱除;生成的NaHSO3、Na2SO3及废烟气携带的焦粉在一次除尘器3内通过惯性碰撞和沉降作用从烟气中分离;2) 5) The dry desulfurization device 2 uses NaHCO 3 as the desulfurizing agent, and injects NaHCO 3 into the primary dust collector 3 through the NaHCO 3 conveying pipeline. In the primary dust collector 3, NaHCO 3 and SO 2 in the waste flue gas are sufficient. The contact reacts to generate NaHSO 3 , Na 2 SO 3 to realize the removal of SO 2 in the waste flue gas; the generated NaHSO 3 , Na 2 SO 3 and the coke powder carried by the waste flue gas pass through inertial collision in the primary dust collector 3 and sedimentation separation from flue gas;

6)经过一次除尘后的废烟气进入余热锅炉4,余热锅炉4利用废烟气携带的热量产生高温高压蒸汽用于发电或设备的驱动,实现炼焦余热的回收利用;经过余热锅炉4回收热量后的废烟气通过管道直接进入SCR脱硝装置5进行脱硝处理;6) The waste flue gas after the first dedusting enters the waste heat boiler 4, and the waste heat boiler 4 uses the heat carried by the waste flue gas to generate high-temperature and high-pressure steam for power generation or equipment drive, so as to realize the recovery and utilization of the coking waste heat; the heat is recovered through the waste heat boiler 4 The waste flue gas directly enters the SCR denitration device 5 through the pipeline for denitration treatment;

7)经SCR脱硝装置5脱硝处理后的废烟气进入热交换器二8进行降温处理;在热交换器二8内,废烟气通过间接换热的方式被来自余热锅炉4的除盐水冷却,废烟气携带的部分热量被除盐水回收后送入余热锅炉4,降温后的废烟气进入二次除尘器6;7) The waste flue gas after being denitrified by the SCR denitration device 5 enters the heat exchanger 2 8 for cooling treatment; in the heat exchanger 2 8, the waste flue gas is cooled by the demineralized water from the waste heat boiler 4 through indirect heat exchange , part of the heat carried by the waste flue gas is recovered by the desalinated water and sent to the waste heat boiler 4, and the cooled waste flue gas enters the secondary dust collector 6;

8)在二次除尘器6内,采用过滤除尘方式脱除废烟气中携带的固体颗粒物及粉尘,所捕集到的颗粒物和粉尘经二次除尘器6下部的粉尘收集装置7回收后外排处理;过滤除尘后的废烟气通过引风机9输送后送往烟囱12排放。8) In the secondary dust collector 6, the solid particles and dust carried in the waste flue gas are removed by filtering and dust removal. The captured particles and dust are recovered by the dust collection device 7 at the lower part of the secondary dust collector 6. Exhaust and treatment; the waste flue gas after filtering and dust removal is transported by the induced draft fan 9 and sent to the chimney 12 for discharge.

所述余热锅炉4的烟气出口温度控制在300℃~400℃之间。The flue gas outlet temperature of the waste heat boiler 4 is controlled between 300°C and 400°C.

所述一次除尘器3为惯性重力除尘器。The primary dust collector 3 is an inertial gravity dust collector.

所述二次除尘器6为袋式除尘器。The secondary dust collector 6 is a bag filter.

所述脱二氧化碳装置15采用物理化学溶剂吸收法、固体吸附法或膜气体分离法对二氧化碳进行分离回收。The carbon dioxide removal device 15 adopts a physical-chemical solvent absorption method, a solid adsorption method or a membrane gas separation method to separate and recover carbon dioxide.

如图1所示,是本发明所述一种混合煤气加热废气余热回收及净化工艺的具体结构形式,包括焦炉废烟气引入系统、热交换器一10、脱二氧化碳装置15、干熄炉1、干法脱硫装置2、一次除尘器3、余热锅炉4、SCR脱硝装置5、热交换器二8、二次除尘器6、引风机9及烟囱12;所述焦炉废烟气引入系统包括焦炉总烟道11及烟道翻板13,焦炉总烟道11上设焦炉废气引出口,烟道翻板13设置在焦炉废烟气引出口与烟囱12之间的焦炉总烟道11上;焦炉废气引出口通过焦炉废烟气管道连接热交换器一10的废烟气入口,热交换器一10的废烟气出口连接脱二氧化碳装置15的废烟气入口,脱二氧化碳装置15的废烟气出口连接干熄炉1下部的供气装置;干熄炉1上部的废烟气出口通过废烟气输送管道依次连接一次除尘器3、余热锅炉4、SCR脱硝装置5、热交换器二8、二次除尘器6、引风机9、烟囱12;沿废烟气流动方向,一次除尘器3上游的废烟气输送管道上设NaHCO3喷入口,通过NaHCO3喷入管道连接NaHCO3供给装置,NaHCO3喷入管道与NaHCO3供给装置共同组成干法脱硫装置2。As shown in Figure 1, it is a specific structure of the waste heat recovery and purification process of the mixed gas heating waste gas according to the present invention, including a coke oven waste flue gas introduction system, a heat exchanger 10, a decarbonation device 15, and a dry quenching furnace. 1. Dry desulfurization device 2, primary dust collector 3, waste heat boiler 4, SCR denitration device 5, heat exchanger 2 8, secondary dust collector 6, induced draft fan 9 and chimney 12; the coke oven waste flue gas introduction system Including the coke oven general flue 11 and the flue flap 13, the coke oven exhaust gas outlet is arranged on the coke oven general flue 11, and the flue flap 13 is arranged between the coke oven exhaust flue gas outlet and the chimney 12 of the coke oven On the general flue 11; the coke oven waste gas outlet is connected to the waste flue gas inlet of heat exchanger one 10 through the coke oven waste flue gas pipeline, and the waste flue gas outlet of heat exchanger one 10 is connected to the waste flue gas inlet of the decarbonation device 15. , the waste flue gas outlet of the decarbonation device 15 is connected to the gas supply device at the lower part of the CDQ 1; the waste flue gas outlet at the upper part of the CDQ 1 is connected to the primary dust collector 3, the waste heat boiler 4, and the SCR denitration sequentially through the waste flue gas conveying pipeline. Device 5, heat exchanger 2 8, secondary dust collector 6, induced draft fan 9, chimney 12; along the flow direction of waste flue gas, a NaHCO 3 injection port is set on the waste flue gas conveying pipeline upstream of the primary precipitator 3, through the NaHCO 3 The injection pipeline is connected to the NaHCO 3 supply device, and the NaHCO 3 injection pipeline and the NaHCO 3 supply device together form the dry desulfurization device 2 .

所述热交换器一10上设有除盐水入口和除盐水出口,除盐水入口和除盐水出口分别通过除盐水管道连接余热锅炉4的省煤器。The first heat exchanger 10 is provided with a demineralized water inlet and a demineralized water outlet, and the demineralized water inlet and the demineralized water outlet are respectively connected to the economizer of the waste heat boiler 4 through a demineralized water pipeline.

所述热交换器二8上设有废烟气入口、废烟气出口、除盐水入口和除盐水出口,废烟气入口连接热交换器二8上游的废烟气输送管道,废烟气出口连接热交换器二8下游的废烟气输送管道;除盐水入口和除盐水出口分别通过除盐水管道连接余热锅炉4的省煤器。The second heat exchanger 8 is provided with a waste flue gas inlet, a waste flue gas outlet, a demineralized water inlet and a demineralized water outlet. Connect the waste flue gas conveying pipeline downstream of the second heat exchanger 8; the demineralized water inlet and the demineralized water outlet are respectively connected to the economizer of the waste heat boiler 4 through the demineralized water pipeline.

与本发明中所述干熄炉1相配套的焦炭装入装置、焦炭排出装置以及与所述一次除尘器3、二次除尘器6、干法脱硫装置2、SCR脱硝装置5、脱二氧化碳装置15等设备相配套的原料供给设施、粉料排出设施、脱硝催化剂再生设施等配置均为现有成熟技术,属本领域技术人员公知的技术,在此不再赘述。The coke loading device, the coke discharging device matched with the CDQ furnace 1 in the present invention, and the primary dust collector 3, the secondary dust collector 6, the dry desulfurization device 2, the SCR denitration device 5, the carbon dioxide removal device The raw material supply facilities, powder discharge facilities, denitration catalyst regeneration facilities and other configurations matched with equipment such as 15 are all existing mature technologies, which are well known to those skilled in the art, and will not be repeated here.

以上所述,仅为本发明较佳的具体实施方式,但本发明的保护范围并不局限于此,任何熟悉本技术领域的技术人员在本发明揭露的技术范围内,根据本发明的技术方案及其发明构思加以等同替换或改变,都应涵盖在本发明的保护范围之内。The above description is only a preferred embodiment of the present invention, but the protection scope of the present invention is not limited to this. The equivalent replacement or change of the inventive concept thereof shall be included within the protection scope of the present invention.

Claims (6)

1. A waste gas waste heat recovery and purification process of a mixed gas heating system is characterized in that coke oven waste flue gas generated in the heating process of a coke oven is sent into a dry quenching furnace after heat exchange, temperature reduction and carbon dioxide removal treatment, and high-temperature coke is cooled; the waste flue gas discharged from the dry quenching furnace enters a primary dust remover, a desulfurizer is sprayed into the primary dust remover, and SO in the waste flue gas is removed2Removing; the desulfurized waste flue gas enters a waste heat boiler to recover heat carried by the waste flue gas, and the outlet temperature of the waste flue gas is controlled by the waste heat boiler to ensure that the waste flue gas is discharged after heat exchangeDirectly feeding the waste flue gas into an SCR denitration device for denitration; and the waste flue gas after denitration is sent to a chimney for discharging after heat exchange, temperature reduction and secondary dust removal.
2. The waste gas waste heat recovery and purification process of the mixed gas heating system according to claim 1, which comprises the following steps:
1) the coke oven waste flue gas generated in the heating process of the coke oven is led out from the coke oven main flue through the coke oven waste flue gas leading-in system and enters the heat exchanger I;
2) in the heat exchanger I, coke oven waste flue gas with the temperature of 200-300 ℃ is cooled to below 70 ℃ by desalted water from a waste heat boiler in an indirect heat exchange mode, part of heat carried by the coke oven waste flue gas is recycled by the desalted water and then is sent to the waste heat boiler, and the coke oven waste flue gas after heat exchange enters a carbon dioxide removal device;
3) in the carbon dioxide removing device, carbon dioxide gas in the waste flue gas is separated and recovered, and the residual waste flue gas enters the dry quenching furnace from a gas supply device at the lower part of the dry quenching furnace;
4) in a dry quenching furnace, coke oven waste flue gas is in reverse contact with high-temperature coke, the waste flue gas absorbing coke heat is discharged from the upper section of the dry quenching furnace and then enters a primary dust remover, and cooled coke is discharged through a coke discharging system at the lower part of the dry quenching furnace;
5) the dry desulfurization device adopts NaHCO3As a desulfurizing agent, by NaHCO3The conveying pipeline sprays NaHCO into the primary dust remover3In a primary precipitator, NaHCO3With SO in waste flue gas2Fully contact to react to generate NaHSO3、Na2SO3Realizing SO in the waste flue gas2Removing; produced NaHSO3、Na2SO3And separating coke powder carried by the waste flue gas from the flue gas through inertial collision and sedimentation in the primary dust remover;
6) the waste flue gas after primary dust removal enters a waste heat boiler, and the waste heat boiler generates high-temperature and high-pressure steam for power generation or equipment driving by using heat carried by the waste flue gas, so that the recycling of coking waste heat is realized; waste flue gas after heat recovery by the waste heat boiler directly enters an SCR denitration device through a pipeline for denitration treatment;
7) the waste flue gas subjected to denitration treatment by the SCR denitration device enters a heat exchanger II for cooling treatment; in the second heat exchanger, the waste flue gas is cooled by the desalted water from the waste heat boiler in an indirect heat exchange mode, part of heat carried by the waste flue gas is recycled by the desalted water and then is sent to the waste heat boiler, and the cooled waste flue gas enters a secondary dust remover;
8) in the secondary dust remover, solid particles and dust carried in the waste flue gas are removed by adopting a filtering and dust removing mode, and the collected particles and dust are recycled by a dust collecting device at the lower part of the secondary dust remover and then are discharged for treatment; and conveying the filtered and dedusted waste flue gas to a chimney through a draught fan for discharging.
3. The waste gas waste heat recovery and purification process of the mixed gas heating system according to claim 1 or 2, wherein the temperature of the flue gas outlet of the waste heat boiler is controlled between 300 ℃ and 400 ℃.
4. The waste gas heat recovery and purification process of the mixed gas heating system according to claim 1 or 2, wherein the primary dust remover is an inertial gravity dust remover.
5. The waste gas heat recovery and purification process of the mixed gas heating system according to claim 1 or 2, wherein the secondary dust remover is a bag type dust remover.
6. The waste gas heat recovery and purification process of the mixed gas heating system according to claim 1 or 2, wherein the carbon dioxide removal device adopts a physical and chemical solvent absorption method, a solid adsorption method or a membrane gas separation method to separate and recover carbon dioxide.
CN201911215152.2A 2019-12-02 2019-12-02 Waste gas waste heat recovery and purification process of mixed gas heating system Withdrawn CN110813007A (en)

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Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN113797728A (en) * 2021-09-30 2021-12-17 灌南县同益金属有限公司 Treatment method for smoke generated in valuable secondary material treatment process
CN113941236A (en) * 2021-11-30 2022-01-18 华泰永创(北京)科技股份有限公司 Dry quenching flue gas treatment system and method thereof
CN118549223A (en) * 2024-07-26 2024-08-27 北京华科仪科技股份有限公司 Cooling device for dry quenching boiler sampling and working method thereof
CN119488788A (en) * 2024-12-16 2025-02-21 攀枝花市众立诚实业有限公司 A flue gas purification treatment system and method for high sulfur and phosphorus tail gas boiler

Cited By (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN113797728A (en) * 2021-09-30 2021-12-17 灌南县同益金属有限公司 Treatment method for smoke generated in valuable secondary material treatment process
CN113797728B (en) * 2021-09-30 2024-05-10 灌南县同益金属有限公司 Treatment method for generating smoke in valuable secondary material treatment process
CN113941236A (en) * 2021-11-30 2022-01-18 华泰永创(北京)科技股份有限公司 Dry quenching flue gas treatment system and method thereof
CN113941236B (en) * 2021-11-30 2023-12-29 华泰永创(北京)科技股份有限公司 Dry quenching flue gas treatment system and method thereof
CN118549223A (en) * 2024-07-26 2024-08-27 北京华科仪科技股份有限公司 Cooling device for dry quenching boiler sampling and working method thereof
CN119488788A (en) * 2024-12-16 2025-02-21 攀枝花市众立诚实业有限公司 A flue gas purification treatment system and method for high sulfur and phosphorus tail gas boiler

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