CN108758658A - A kind of useless activated coke Incineration in CFB system - Google Patents
A kind of useless activated coke Incineration in CFB system Download PDFInfo
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- 239000000571 coke Substances 0.000 title claims abstract description 76
- UGFAIRIUMAVXCW-UHFFFAOYSA-N Carbon monoxide Chemical compound [O+]#[C-] UGFAIRIUMAVXCW-UHFFFAOYSA-N 0.000 claims abstract description 46
- 239000003546 flue gas Substances 0.000 claims abstract description 46
- 238000001179 sorption measurement Methods 0.000 claims abstract description 13
- 239000002826 coolant Substances 0.000 claims description 6
- 239000000463 material Substances 0.000 claims description 2
- 238000004064 recycling Methods 0.000 claims description 2
- 230000003134 recirculating effect Effects 0.000 claims 4
- 238000010521 absorption reaction Methods 0.000 claims 1
- 238000001816 cooling Methods 0.000 claims 1
- 238000000605 extraction Methods 0.000 claims 1
- 239000002737 fuel gas Substances 0.000 claims 1
- 239000002699 waste material Substances 0.000 abstract description 39
- 238000002485 combustion reaction Methods 0.000 abstract description 20
- 238000006477 desulfuration reaction Methods 0.000 abstract description 16
- 230000023556 desulfurization Effects 0.000 abstract description 16
- 239000000428 dust Substances 0.000 abstract description 16
- 238000011084 recovery Methods 0.000 abstract description 11
- 238000004519 manufacturing process Methods 0.000 abstract description 5
- 239000007789 gas Substances 0.000 abstract description 4
- 230000007613 environmental effect Effects 0.000 abstract description 2
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 26
- MWUXSHHQAYIFBG-UHFFFAOYSA-N nitrogen oxide Inorganic materials O=[N] MWUXSHHQAYIFBG-UHFFFAOYSA-N 0.000 description 21
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 description 12
- 238000000034 method Methods 0.000 description 12
- 238000010438 heat treatment Methods 0.000 description 9
- 239000006004 Quartz sand Substances 0.000 description 8
- VYPSYNLAJGMNEJ-UHFFFAOYSA-N Silicium dioxide Chemical compound O=[Si]=O VYPSYNLAJGMNEJ-UHFFFAOYSA-N 0.000 description 8
- 239000010865 sewage Substances 0.000 description 7
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 description 6
- 239000002894 chemical waste Substances 0.000 description 6
- 239000002245 particle Substances 0.000 description 6
- 238000011069 regeneration method Methods 0.000 description 6
- 239000000126 substance Substances 0.000 description 5
- 230000000694 effects Effects 0.000 description 4
- 238000005516 engineering process Methods 0.000 description 4
- 239000005416 organic matter Substances 0.000 description 4
- 239000003638 chemical reducing agent Substances 0.000 description 3
- 239000003344 environmental pollutant Substances 0.000 description 3
- 229910052757 nitrogen Inorganic materials 0.000 description 3
- 231100000719 pollutant Toxicity 0.000 description 3
- 230000008929 regeneration Effects 0.000 description 3
- VHUUQVKOLVNVRT-UHFFFAOYSA-N Ammonium hydroxide Chemical group [NH4+].[OH-] VHUUQVKOLVNVRT-UHFFFAOYSA-N 0.000 description 2
- 239000003463 adsorbent Substances 0.000 description 2
- 235000011114 ammonium hydroxide Nutrition 0.000 description 2
- 238000004458 analytical method Methods 0.000 description 2
- 239000003054 catalyst Substances 0.000 description 2
- 238000010531 catalytic reduction reaction Methods 0.000 description 2
- 238000005260 corrosion Methods 0.000 description 2
- 230000007797 corrosion Effects 0.000 description 2
- 230000004048 modification Effects 0.000 description 2
- 238000012986 modification Methods 0.000 description 2
- 230000003647 oxidation Effects 0.000 description 2
- 238000007254 oxidation reaction Methods 0.000 description 2
- 239000011148 porous material Substances 0.000 description 2
- 230000008569 process Effects 0.000 description 2
- 238000000746 purification Methods 0.000 description 2
- 239000002994 raw material Substances 0.000 description 2
- 238000000926 separation method Methods 0.000 description 2
- 239000002351 wastewater Substances 0.000 description 2
- KVGZZAHHUNAVKZ-UHFFFAOYSA-N 1,4-Dioxin Chemical compound O1C=COC=C1 KVGZZAHHUNAVKZ-UHFFFAOYSA-N 0.000 description 1
- XSQUKJJJFZCRTK-UHFFFAOYSA-N Urea Chemical compound NC(N)=O XSQUKJJJFZCRTK-UHFFFAOYSA-N 0.000 description 1
- 239000002253 acid Substances 0.000 description 1
- 230000009471 action Effects 0.000 description 1
- 238000010170 biological method Methods 0.000 description 1
- 239000004202 carbamide Substances 0.000 description 1
- 239000003575 carbonaceous material Substances 0.000 description 1
- 238000006243 chemical reaction Methods 0.000 description 1
- 239000003245 coal Substances 0.000 description 1
- 230000003247 decreasing effect Effects 0.000 description 1
- 150000002013 dioxins Chemical class 0.000 description 1
- 230000009977 dual effect Effects 0.000 description 1
- 238000010828 elution Methods 0.000 description 1
- 238000003912 environmental pollution Methods 0.000 description 1
- 239000000446 fuel Substances 0.000 description 1
- 125000000524 functional group Chemical group 0.000 description 1
- 229910001385 heavy metal Inorganic materials 0.000 description 1
- 239000010842 industrial wastewater Substances 0.000 description 1
- 239000012528 membrane Substances 0.000 description 1
- 239000007787 solid Substances 0.000 description 1
- 238000009279 wet oxidation reaction Methods 0.000 description 1
Classifications
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- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23G—CREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
- F23G7/00—Incinerators or other apparatus for consuming industrial waste, e.g. chemicals
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- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23G—CREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
- F23G5/00—Incineration of waste; Incinerator constructions; Details, accessories or control therefor
- F23G5/44—Details; Accessories
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- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23J—REMOVAL OR TREATMENT OF COMBUSTION PRODUCTS OR COMBUSTION RESIDUES; FLUES
- F23J15/00—Arrangements of devices for treating smoke or fumes
- F23J15/02—Arrangements of devices for treating smoke or fumes of purifiers, e.g. for removing noxious material
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23J—REMOVAL OR TREATMENT OF COMBUSTION PRODUCTS OR COMBUSTION RESIDUES; FLUES
- F23J15/00—Arrangements of devices for treating smoke or fumes
- F23J15/06—Arrangements of devices for treating smoke or fumes of coolers
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23L—SUPPLYING 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
- F23L15/00—Heating of air supplied for combustion
- F23L15/04—Arrangements of recuperators
-
- Y—GENERAL 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
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02E—REDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
- Y02E20/00—Combustion technologies with mitigation potential
- Y02E20/34—Indirect CO2mitigation, i.e. by acting on non CO2directly related matters of the process, e.g. pre-heating or heat recovery
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- Engineering & Computer Science (AREA)
- Mechanical Engineering (AREA)
- General Engineering & Computer Science (AREA)
- Chemical & Material Sciences (AREA)
- Combustion & Propulsion (AREA)
- Environmental & Geological Engineering (AREA)
- Fluidized-Bed Combustion And Resonant Combustion (AREA)
- Treating Waste Gases (AREA)
Abstract
本发明公开了一种废活性焦循环流化床焚烧系统,包括依次布置的循环流化床焚烧装置、汽包、尾部烟气热量回收装置、第一换热器、脱硫除尘装置、活性焦吸附塔、引风机和第二换热器,所述循环流化床焚烧装置产生的烟气依次经过尾部烟气热量回收装置、第一换热器、脱硫除尘装置和活性焦吸附塔,再通过引风机抽引后经第二换热器和烟囱排放到大气中。本发明提供的废活性焦循环流化床焚烧系统利用废活性焦燃烧产生的热量进行热电生产,从而实现废物能源化利用,同时对废活性焦燃烧产生的尾气进行环保处理,达到无污染排放,解决了废活性焦的后续处理。
The invention discloses a waste activated coke circulating fluidized bed incineration system, which comprises a circulating fluidized bed incineration device, a steam drum, a tail flue gas heat recovery device, a first heat exchanger, a desulfurization and dust removal device, and an activated coke adsorption device arranged in sequence. Tower, induced draft fan and second heat exchanger, the flue gas produced by the circulating fluidized bed incineration device passes through the tail flue gas heat recovery device, the first heat exchanger, desulfurization and dust removal device and activated coke adsorption tower in sequence, and then passes through the induced After being drawn by the fan, it is discharged into the atmosphere through the second heat exchanger and the chimney. The waste activated coke circulating fluidized bed incineration system provided by the present invention uses the heat generated by the waste activated coke combustion to perform thermoelectric production, thereby realizing the utilization of waste energy, and at the same time performing environmental protection treatment on the tail gas generated by the waste activated coke combustion to achieve pollution-free emissions. The follow-up treatment of spent active coke is solved.
Description
技术领域technical field
本发明属于能源技术领域,尤其涉及一种废活性焦循环流化床焚烧系统。The invention belongs to the field of energy technology, in particular to a waste activated coke circulating fluidized bed incineration system.
背景技术Background technique
传统的水处理技术如化学法、生物法、氧化法、活性碳吸附法、膜法等,由于其工艺本身存在的弱点,在进行污水深处理时,投资大、处理费用比较高,同时处理周期也较长,因此,企业和社会无法承受。活性焦是以高挥发分煤为主要原料研制出的一种具有吸附剂和催化剂双重性能的粒状物质,一种多孔的含碳物质,是没有得到充分干馏或活化的活性炭类吸附剂。活性焦具有活性炭的特点,但同时它又克服了活性炭价格高、机械强度低、易粉碎的缺点。Traditional water treatment technologies such as chemical methods, biological methods, oxidation methods, activated carbon adsorption methods, membrane methods, etc., due to the weaknesses of the technology itself, require large investment and relatively high treatment costs for deep sewage treatment, and the treatment cycle Also longer, therefore, businesses and society can not afford. Activated coke is a granular substance with dual properties of adsorbent and catalyst developed from high-volatile coal as the main raw material. It is a porous carbonaceous substance and is an activated carbon adsorbent that has not been fully carbonized or activated. Activated coke has the characteristics of activated carbon, but at the same time it overcomes the disadvantages of high price, low mechanical strength and easy crushing of activated carbon.
活性焦具有强大的孔结构及特殊的官能团,对污水中的悬浮物、无机物及有机物等有害成分具有很强的吸附能力,并且活性焦较活性炭廉价,国内已有一批污水处理企业采用活性焦来用于城市污水、工业废水、污染河水等水源的净化处理,由活性焦处理过的废水,可以用于中水回用,能够有效的缓解废水的排放及对环境的污染。Activated coke has a strong pore structure and special functional groups, and has a strong adsorption capacity for harmful components such as suspended solids, inorganic and organic substances in sewage, and activated coke is cheaper than activated carbon. A number of domestic sewage treatment enterprises have adopted activated coke It is used for the purification of urban sewage, industrial wastewater, polluted river water and other water sources. The wastewater treated by activated coke can be used for reuse of reclaimed water, which can effectively alleviate the discharge of wastewater and the pollution of the environment.
虽然活性焦在污水净化处理方面比传统污水处理工艺有着绝对的优势,但是废活性焦(处理过污水后失去活性的活性焦)的后续处理是个难题。虽然可以借鉴活性炭的再生处理工艺(如药剂洗脱的化学再生法、生物再生法、湿式氧化法、电解氧化法或加热再生法)对废活性焦进行活性再生,但是由于废活性焦含水量高,吸附的有机物量大,进行再生活性处理不仅成本高、次数有限,而且所吸附的有机物很容易从废活性焦孔结构中析出,造成二次污染,如果随意堆放又势必造成环境污染,因此,解决废活性焦的利用问题乃当务之急。Although activated coke has absolute advantages over traditional sewage treatment processes in sewage purification treatment, the follow-up treatment of waste activated coke (activated coke that loses its activity after sewage treatment) is a difficult problem. Although the regeneration treatment process of activated carbon can be used for reference (such as chemical regeneration method of chemical elution, biological regeneration method, wet oxidation method, electrolytic oxidation method or heating regeneration method) for active regeneration of waste activated coke, but due to the high water content of waste activated coke , the amount of adsorbed organic matter is large, and the regeneration activity treatment is not only costly and the number of times is limited, but also the adsorbed organic matter is easily precipitated from the pore structure of the spent activated coke, causing secondary pollution. If it is randomly stacked, it will inevitably cause environmental pollution. Therefore, It is urgent to solve the utilization problem of waste activated coke.
发明内容Contents of the invention
本发明的目的在于提供一种废活性焦循环流化床焚烧系统,利用富含水分、有机物的废活性焦燃烧释放的热量生产高温高压蒸汽,从而进行电力生产或供热,最终实现废物能源化利用,同时对废活性焦燃烧产生的尾气进行环保处理,达到无污染排放,解决了废活性焦的后续处理。The purpose of the present invention is to provide a circulating fluidized bed incineration system for waste activated coke, which uses the heat released by the combustion of waste activated coke rich in water and organic matter to produce high-temperature and high-pressure steam, thereby carrying out power production or heat supply, and finally realizing waste energy. At the same time, the tail gas produced by the combustion of waste activated coke is treated in an environmentally friendly manner to achieve pollution-free emissions and solve the follow-up treatment of waste activated coke.
本发明采用如下技术方案:The present invention adopts following technical scheme:
一种废活性焦循环流化床焚烧系统,包括依次布置的循环流化床焚烧装置、汽包、尾部烟气热量回收装置、第一换热器、脱硫除尘装置、活性焦吸附塔、引风机和第二换热器。A circulating fluidized bed incineration system for waste activated coke, including a circulating fluidized bed incineration device, a steam drum, a tail flue gas heat recovery device, a first heat exchanger, a desulfurization and dust removal device, an activated coke adsorption tower, and an induced draft fan arranged in sequence and a second heat exchanger.
所述循环流化床焚烧装置包括循环流化床焚烧炉、与循环流化床焚烧炉底部连接的给料机和点火器、与循环流化床焚烧炉顶部连接的分离器、设置在分离器与循环流化床焚烧炉间的返料器。The circulating fluidized bed incinerator includes a circulating fluidized bed incinerator, a feeder and an igniter connected to the bottom of the circulating fluidized bed incinerator, a separator connected to the top of the circulating fluidized bed incinerator, and a The feeder between the circulating fluidized bed incinerator.
所述点火器中设有一次风管。A primary air duct is arranged in the igniter.
所述分离器为旋风分离器。The separator is a cyclone separator.
废活性焦通过给料机进入循环流化床焚烧炉,经点火器给循环流化床焚烧炉加热,并通过一次风管送入一次风,废活性焦燃烧后破碎产生灰颗粒,灰颗粒经分离器分离后通过返料器返回至循环流化床焚烧炉或进入尾部烟气热量回收装置。The waste activated coke enters the circulating fluidized bed incinerator through the feeder, heats the circulating fluidized bed incinerator through the igniter, and sends it into the primary air through the primary air pipe. After the waste activated coke is burned, it is broken to produce ash particles, which are passed through After being separated by the separator, it returns to the circulating fluidized bed incinerator through the feeder or enters the tail flue gas heat recovery device.
所述的循环流化床焚烧炉的高度为25~50米,主要是为了废活性焦在焚烧炉内析出的可燃挥发分有充分的停留时间,停留时间为4-6秒,使燃烧更充分。The height of the circulating fluidized bed incinerator is 25 to 50 meters, mainly because the combustible volatile matter precipitated from the waste activated coke in the incinerator has sufficient residence time, and the residence time is 4-6 seconds, so that the combustion is more complete .
所述的循环流化床焚烧炉的相对墙体上布置若干根二次风管,主要用于调节燃烧状况;通过向循环流化床焚烧炉内注入一定量二次风,可以有效地抑制氮氧化物的生成;二次风管输入的二次风占循环流化床焚烧炉内总风量的40-60%,所述百分比为体积比。Several secondary air pipes are arranged on the opposite wall of the circulating fluidized bed incinerator, mainly for adjusting the combustion state; by injecting a certain amount of secondary air into the circulating fluidized bed incinerator, nitrogen can be effectively suppressed. The generation of oxides; the secondary air input by the secondary air pipe accounts for 40-60% of the total air volume in the circulating fluidized bed incinerator, and the percentage is volume ratio.
优选的,二次风管输入的二次风占循环流化床焚烧炉内总风量的50%,以实现废活性焦的充分燃烧,抑制氮氧化物的生成。Preferably, the secondary air input by the secondary air pipe accounts for 50% of the total air volume in the circulating fluidized bed incinerator, so as to realize the full combustion of spent activated coke and suppress the generation of nitrogen oxides.
所述的循环流化床的内壁面布置水冷壁,主要是吸收废活性焦燃烧释放的热量。The inner wall of the circulating fluidized bed is arranged with a water-cooled wall, which mainly absorbs the heat released by the combustion of waste activated coke.
所述的循环流化床焚烧炉中的燃烧温度为850~950℃。The combustion temperature in the circulating fluidized bed incinerator is 850-950°C.
所述的尾部烟气热量回收装置从上至下依次布置高温过热器、低温过热器、省煤器和空气预热器。The tail flue gas heat recovery device is arranged in sequence from top to bottom with a high-temperature superheater, a low-temperature superheater, an economizer and an air preheater.
所述的汽包分为上半部和下半部,上半部与省煤器的出口、水冷壁的出口和低温过热器连接,下半部与水冷壁的入口连接。汽包主要用于汽水分离,从汽包分离出的蒸汽依次通过低温过热器、高温过热器与电力或供热设备连接,用于电力生产或供热。The steam drum is divided into an upper part and a lower part, the upper part is connected with the outlet of the economizer, the outlet of the water wall and the low-temperature superheater, and the lower part is connected with the inlet of the water wall. The steam drum is mainly used for the separation of steam and water. The steam separated from the steam drum is connected to electric power or heating equipment through the low-temperature superheater and high-temperature superheater in turn, and is used for power production or heat supply.
所述省煤器的入口与给水装置连接,出口与汽包的上半部连接。The inlet of the economizer is connected with the water supply device, and the outlet is connected with the upper half of the steam drum.
所述空气预热器的入口与送风机连接,空气预热器的出口与一次风管和二次风管连接。The inlet of the air preheater is connected with the blower, and the outlet of the air preheater is connected with the primary air pipe and the secondary air pipe.
所述废活性焦循环流化床焚烧系统还包括布置在循环流化床焚烧炉的出口与分离器之间的脱硝装置,主要作用是脱除废活性焦燃烧中产生的氮氧化物。The waste activated coke circulating fluidized bed incineration system also includes a denitrification device arranged between the outlet of the circulating fluidized bed incinerator and the separator, and its main function is to remove nitrogen oxides generated during the combustion of waste activated coke.
所述的脱硝装置为选择性非催化还原(SNCR)脱硝装置,在无催化剂的作用下,在适合脱硝反应的“温度窗口”内喷入还原剂将烟气中的氮氧化物还原为无害的氮气和水。The denitrification device is a selective non-catalytic reduction (SNCR) denitrification device. Under the action of no catalyst, a reducing agent is injected into the "temperature window" suitable for the denitrification reaction to reduce the nitrogen oxides in the flue gas to harmless of nitrogen and water.
所述的选择性非催化还原(SNCR)脱硝装置中的还原剂选自氨水或尿素。The reducing agent in the selective non-catalytic reduction (SNCR) denitrification device is selected from ammonia water or urea.
所述的第一换热器与第二换热器相连通,第一换热器与烟气换热后,将烟气降到一定温度,便于脱硫除尘装置正常工作,另外第一换热器中的冷却介质吸收烟气的热量后传递至第二换热器中作为加热介质,用于加热烟囱入口的烟气,以提高排放烟气温度,避免烟气阻塞、低温腐蚀等问题;第二换热器中的加热介质与烟气换热后传递至第一换热器中作为冷却介质。The first heat exchanger is connected with the second heat exchanger, and after exchanging heat with the flue gas, the first heat exchanger lowers the flue gas to a certain temperature to facilitate the normal operation of the desulfurization and dust removal device. In addition, the first heat exchanger The cooling medium in the cooling medium absorbs the heat of the flue gas and transfers it to the second heat exchanger as a heating medium, which is used to heat the flue gas at the chimney inlet to increase the temperature of the exhausted flue gas and avoid problems such as flue gas blockage and low-temperature corrosion; the second The heating medium in the heat exchanger exchanges heat with the flue gas and is transferred to the first heat exchanger as a cooling medium.
上述废活性焦循环流化床焚烧系统的使用方法,包括以下步骤:The method for using the above waste activated coke circulating fluidized bed incineration system comprises the following steps:
(1)在循环流化床焚烧炉内加入石英砂;(1) Add quartz sand in the circulating fluidized bed incinerator;
(2)开启点火器加热石英砂至650~750℃并通入一次风;(2) Turn on the igniter to heat the quartz sand to 650-750°C and feed the primary air;
(3)废活性焦经给料机输送到循环流化床焚烧炉内燃烧,,燃烧时通过二次风管通入二次风;废活性焦在循环流化床内焚烧释放的热量部分被水冷壁回收利用;(3) The waste activated coke is transported to the circulating fluidized bed incinerator through the feeder for combustion, and the secondary air is introduced through the secondary air pipe during combustion; the heat released by the waste activated coke incineration in the circulating fluidized bed is partially consumed Water wall recycling;
(4)从循环流化床焚烧炉出来的烟气经过尾部烟气热量回收装置进行热量回收利用;(4) The flue gas from the circulating fluidized bed incinerator passes through the tail flue gas heat recovery device for heat recovery;
(5)烟气再依次进入第一换热器降温、进入脱硫除尘装置进行脱硫除尘、再进入活性焦吸附塔除去有机物;(5) The flue gas enters the first heat exchanger to cool down in turn, enters the desulfurization and dust removal device for desulfurization and dust removal, and then enters the active coke adsorption tower to remove organic matter;
(6)烟气再通过引风机和第二换热器加热后进入烟囱。(6) The flue gas enters the chimney after being heated by the induced draft fan and the second heat exchanger.
所述步骤(1)中的石英砂主要作为热载体与废活性焦进行传热,粒径为0-5mm,在循环流化床炉内的高度为300-700mm;以便达到与废活性焦充分传热的效果。The quartz sand in the step (1) is mainly used as a heat carrier for heat transfer with the waste activated coke, the particle size is 0-5mm, and the height in the circulating fluidized bed furnace is 300-700mm; The effect of heat transfer.
所述步骤(2)中开启点火器加热石英砂至650~750℃,主要是因为废活性焦半焦着火点比较高,基本在650℃以上。In the step (2), the igniter is turned on to heat the quartz sand to 650-750°C, mainly because the ignition point of the waste activated coke semi-coke is relatively high, basically above 650°C.
本发明提供的废活性焦循环流化床焚烧系统,以废活性焦为原料,通过合理的配风比例和环保装置的布置,可实现废活性焦的高效燃烧及无污染排放,通过汽包和尾部回收装置回收的高温高压蒸汽可用于供热或电力生产,从而不仅实现了废活性焦能源化及清洁化利用,而且增加了企业的收入。The waste activated coke circulating fluidized bed incineration system provided by the present invention uses waste activated coke as a raw material, and through a reasonable air distribution ratio and the arrangement of environmental protection devices, can realize efficient combustion and pollution-free emission of waste activated coke. The high-temperature and high-pressure steam recovered by the tail recovery device can be used for heating or power production, which not only realizes the energy and clean utilization of waste activated coke, but also increases the income of the enterprise.
附图说明Description of drawings
图1为本发明提供的废活性焦循环流化床焚烧系统的结构示意图;Fig. 1 is the structural representation of the waste activated coke circulating fluidized bed incineration system provided by the present invention;
其中,1、循环流化床焚烧炉;2、水冷壁;3、二次风管;4、给料机;5、点火器;6、返料器;7、旋风分离器;8、脱硝装置(SNCR);9、高温过热器;10、低温过热器;11、省煤器;12、空气预热器;13、第一换热器;14、脱硫除尘装置;15、活性焦吸附塔;16、引风机;17、烟囱;18、第二换热器;19、汽包。Among them, 1. Circulating fluidized bed incinerator; 2. Water wall; 3. Secondary air duct; 4. Feeder; 5. Igniter; (SNCR); 9. High temperature superheater; 10. Low temperature superheater; 11. Economizer; 12. Air preheater; 13. First heat exchanger; 14. Desulfurization and dust removal device; 15. Activated coke adsorption tower; 16. Induced fan; 17. Chimney; 18. Second heat exchanger; 19. Steam drum.
具体实施方式Detailed ways
下面结合具体实施例对本发明作进一步阐释。The present invention will be further explained below in conjunction with specific examples.
如图1所示,一种废活性焦循环流化床焚烧系统,包括依次布置的循环流化床焚烧装置、汽包19、脱硝装置8、尾部烟气热量回收装置、第一换热器13、脱硫除尘装置14、活性焦吸附塔15、第二换热器18和引风机16,循环流化床焚烧装置产生的烟气依次经过脱硝装置8、尾部烟气热量回收装置、第一换热器13、脱硫除尘装置14和活性焦吸附塔15,再通过引风机16抽引后经第二换热器18和烟囱17排放到大气中。As shown in Figure 1, a waste activated coke circulating fluidized bed incineration system includes a circulating fluidized bed incineration device, a steam drum 19, a denitrification device 8, a tail flue gas heat recovery device, and a first heat exchanger 13 arranged in sequence , desulfurization and dust removal device 14, activated coke adsorption tower 15, second heat exchanger 18 and induced draft fan 16, the flue gas produced by the circulating fluidized bed incineration device passes through the denitrification device 8, the tail flue gas heat recovery device, the first heat exchange device 13, desulfurization and dust removal device 14, and activated coke adsorption tower 15, and then is drawn by induced draft fan 16 and then discharged into the atmosphere through second heat exchanger 18 and chimney 17.
循环流化床焚烧装置,包括循环流化床焚烧炉1、与循环流化床焚烧炉1底部连接的给料机4和点火器5、与循环流化床焚烧炉1顶部连接的旋风分离器7和设置在旋风分离器7和循环流化床焚烧炉1之间的返料器6;旋风分离器7的出口通过返料器6与循环流化床焚烧炉1底部连接;循环流化床焚烧炉1的内壁面布置水冷壁2,循环流化床焚烧炉1的相对墙体上布置二次风管3;尾部烟气热量回收装置,从上至下依次布置高温过热器9、低温过热器10、省煤器11和空气预热器12;脱硝装置(SNCR)8,布置在循环流化床焚烧炉1的出口与旋风分离器7之间;汽包19的下半部与水冷壁2的入口连接,所述的汽包19的上半部分别与水冷壁2的出口、省煤器11的出口连接和低温过热器10连接,水通过省煤器11的出口进入汽包19的上半部,再进入到水冷壁2进行水循环;省煤器11的入口与给水装置连接;空气预热器12的入口与送风机连接,空气预热器12的出口与一次风管和二次风管3连接,提供加热后的一次风和二次风。A circulating fluidized bed incinerator, including a circulating fluidized bed incinerator 1, a feeder 4 and an igniter 5 connected to the bottom of the circulating fluidized bed incinerator 1, and a cyclone separator connected to the top of the circulating fluidized bed incinerator 1 7 and the feeder 6 arranged between the cyclone separator 7 and the circulating fluidized bed incinerator 1; the outlet of the cyclone separator 7 is connected with the bottom of the circulating fluidized bed incinerator 1 through the feeder 6; the circulating fluidized bed The water-cooled wall 2 is arranged on the inner wall of the incinerator 1, and the secondary air pipe 3 is arranged on the opposite wall of the circulating fluidized bed incinerator 1; the tail flue gas heat recovery device is arranged in sequence from top to bottom with a high-temperature superheater 9 and a low-temperature superheater device 10, economizer 11 and air preheater 12; denitrification device (SNCR) 8, arranged between the outlet of circulating fluidized bed incinerator 1 and cyclone separator 7; the lower half of steam drum 19 and the water wall 2, the upper half of the steam drum 19 is connected to the outlet of the water wall 2, the outlet of the economizer 11, and the low-temperature superheater 10, and the water enters the steam drum 19 through the outlet of the economizer 11. The upper part, then enters the water wall 2 for water circulation; the inlet of the economizer 11 is connected to the water supply device; the inlet of the air preheater 12 is connected to the blower, and the outlet of the air preheater 12 is connected to the primary air pipe and the secondary air Pipe 3 is connected to provide heated primary air and secondary air.
在循环流化床焚烧炉1内加入一定量的石英砂,废活性焦通过给料机4进入循环流化床焚烧炉1,开启点火器5加热石英砂,并经一次风管送入一次风;在废活性焦燃烧过程中通过二次风管3向循环流化床焚烧炉1注入二次风,调节燃烧状况,有效地抑制氮氧化物的生成;水冷壁2吸收废活性焦燃烧释放的热量;废活性焦燃烧破碎产生烟气,烟气中氮氧化物与脱硝装置8喷射的还原剂反应生成氮气;烟气中的灰颗粒中的较粗部分经旋风分离器7分离后通过返料器6重新回到循环流化床焚烧炉1内,而烟气中的较细灰颗粒则在脱硫除尘装置14内被脱除。Add a certain amount of quartz sand into the circulating fluidized bed incinerator 1, waste activated coke enters the circulating fluidized bed incinerator 1 through the feeder 4, turns on the igniter 5 to heat the quartz sand, and sends it into the primary air through the primary air duct. ; During the waste activated coke combustion process, the secondary air is injected into the circulating fluidized bed incinerator 1 through the secondary air pipe 3 to adjust the combustion conditions and effectively suppress the generation of nitrogen oxides; the water wall 2 absorbs the waste activated coke combustion released heat; the waste activated coke is burned and broken to produce flue gas, and the nitrogen oxides in the flue gas react with the reducing agent injected by the denitrification device 8 to generate nitrogen; the thicker part of the ash particles in the flue gas is separated by the cyclone separator 7 and passed through the return material The device 6 returns to the circulating fluidized bed incinerator 1, and the finer ash particles in the flue gas are removed in the desulfurization and dust removal device 14.
同时,化工废活性焦燃烧释放的热量依次被高温过热器9、低温过热器10、省煤器11、空气预热器12及第一换热器13回收利用;接着,化工废活性焦燃烧产生的烟气SO2、重金属Hg等污染物在脱硫除尘装置14内被脱除,烟气中未分解有机气体在活性焦吸附塔15内被吸附,从而来自循环流化床焚烧炉1的烟气经脱硝装置(SNCR)8、脱硫除尘装置14及活性焦吸附塔15处理后变为洁净烟气,通过引风机16抽引,经第二换热器18加热后,经烟囱17排放到大气中。At the same time, the heat released by the combustion of chemical waste activated coke is sequentially recycled by the high-temperature superheater 9, low-temperature superheater 10, economizer 11, air preheater 12, and first heat exchanger 13; The pollutants such as SO 2 and heavy metal Hg in the flue gas are removed in the desulfurization and dust removal device 14, and the undecomposed organic gases in the flue gas are adsorbed in the activated coke adsorption tower 15, so that the flue gas from the circulating fluidized bed incinerator 1 After being treated by the denitrification device (SNCR) 8, the desulfurization and dust removal device 14 and the activated coke adsorption tower 15, it becomes clean flue gas, which is drawn by the induced draft fan 16, heated by the second heat exchanger 18, and discharged into the atmosphere through the chimney 17 .
第一换热器13与第二换热器18相连通,第一换热器13的出口与第二换热器18的入口相连通,第一换热器13与烟气换热后,将烟气降到一定温度,便于脱硫除尘装置14正常工作,另外第一换热器13中的冷却介质吸收烟气的热量后传递至第二换热器18作为加热介质,用于加热烟囱17入口的烟气,以提高排放烟气温度,避免烟气阻塞、低温腐蚀等问题;第二换热器18中的加热介质与烟气换热后传递至第一换热器13中作为冷却介质。The first heat exchanger 13 communicates with the second heat exchanger 18, and the outlet of the first heat exchanger 13 communicates with the inlet of the second heat exchanger 18. After the first heat exchanger 13 exchanges heat with the flue gas, the The flue gas drops to a certain temperature, which facilitates the normal operation of the desulfurization and dust removal device 14. In addition, the cooling medium in the first heat exchanger 13 absorbs the heat of the flue gas and transfers it to the second heat exchanger 18 as a heating medium for heating the inlet of the chimney 17. flue gas to increase the exhaust gas temperature and avoid problems such as flue gas blockage and low-temperature corrosion; the heating medium in the second heat exchanger 18 exchanges heat with the flue gas and transfers it to the first heat exchanger 13 as a cooling medium.
汽包19分为上半部和下半部,上半部与省煤器11的出口、水冷壁2的出口和低温过热器10连接,下半部与水冷壁2的入口连接。汽包19用于汽水分离,分离出来的蒸汽依次通过低温过热器10、高温过热器9与电力设备连接,用于电力生产;分离出来的水再次进入到水冷壁2进行水循环,吸收部分废活性焦在循环流化床内焚烧释放的热量。The steam drum 19 is divided into an upper part and a lower part, the upper part is connected with the outlet of the economizer 11, the outlet of the water wall 2 and the low-temperature superheater 10, and the lower part is connected with the inlet of the water wall 2. The steam drum 19 is used for the separation of steam and water, and the separated steam is connected to the power equipment through the low-temperature superheater 10 and the high-temperature superheater 9 in sequence, and is used for power production; the separated water enters the water wall 2 again for water circulation to absorb part of waste activity The heat released by coke incineration in a circulating fluidized bed.
应用例1Application example 1
表1为典型化工废活性焦特性分析数据,用本发明提供的废活性焦循环流化床焚烧系统进行焚烧处理。Table 1 shows the characteristic analysis data of typical chemical waste activated coke, which is incinerated with the waste activated coke circulating fluidized bed incineration system provided by the present invention.
表1典型化工废活性焦特性分析数据Table 1 Characteristic analysis data of typical chemical waste activated coke
循环流化床焚烧炉1内加入40cm厚的石英砂,送入180Nm3/h一次风,开启点火器5将石英砂加热到650℃左右。化工废活性焦燃料经给料机4给入循环流化床焚烧炉1并燃烧,燃烧时经二次风管3通入180Nm3/h二次风,循环流化床焚烧炉1出口温度保持在900℃左右。Add 40cm thick quartz sand into the circulating fluidized bed incinerator 1, send in 180Nm 3 /h primary air, turn on the igniter 5 to heat the quartz sand to about 650°C. The chemical waste activated coke fuel is fed into the circulating fluidized bed incinerator 1 through the feeder 4 and burned. During combustion, 180Nm 3 /h secondary air is introduced through the secondary air pipe 3, and the outlet temperature of the circulating fluidized bed incinerator 1 is maintained. At around 900°C.
化工废活性焦燃烧产生的烟气中灰颗粒浓度为11g/Nm3,经旋风分离器7分离后为220mg/Nm3;同时化工废活性焦燃烧产生大量污染物,烟气中污染物组分氮氧化物(NOx)、SO2及二噁英的浓度分别为140mg/Nm3、326mg/Nm3和0.062ng/Nm3;从循环流化床焚烧炉1出来的烟气经脱硝装置(SNCR)8喷射氨水处理后氮氧化物(NOx)浓度降为40mg/Nm3。The concentration of ash particles in the flue gas produced by the combustion of chemical waste activated coke is 11g/Nm 3 , which is 220mg/Nm 3 after being separated by the cyclone separator 7; at the same time, the combustion of chemical waste activated coke produces a large amount of pollutants, and the pollutant components in the flue gas The concentrations of nitrogen oxides (NO x ), SO 2 and dioxins are 140mg/Nm 3 , 326mg/Nm 3 and 0.062ng/Nm 3 respectively; the flue gas from the circulating fluidized bed incinerator 1 passes through the denitration device ( The concentration of nitrogen oxides (NO x ) decreased to 40 mg/Nm 3 after SNCR) 8 was sprayed with ammonia water.
来自循环流化床焚烧炉1的烟气(温度约为900℃)经过高温过热器9、低温过热器10冷却后温度降为450℃左右,其次经过省煤器11、空气预热器12吸收热量后温度降至150℃左右,最后经换热器13换热后温度约为120℃左右,该温度低于酸露点温度,有助于提高脱硫除尘装置14的除尘效率和脱硫效率。The flue gas from the circulating fluidized bed incinerator 1 (temperature is about 900°C) is cooled by the high temperature superheater 9 and the low temperature superheater 10, and then the temperature drops to about 450°C, and then it is absorbed by the economizer 11 and the air preheater 12 After heating, the temperature drops to about 150°C, and finally the temperature after heat exchange by the heat exchanger 13 is about 120°C, which is lower than the acid dew point temperature, which helps to improve the dust removal efficiency and desulfurization efficiency of the desulfurization and dust removal device 14 .
烟气再经过脱硫除尘装置14脱除后,灰颗粒浓度仅为4mg/Nm3,SO2浓度降为20mg/Nm3,最后经活性焦吸附塔15吸附后二噁英的浓度约为0.0097ng/Nm3左右。After the flue gas is removed by the desulfurization and dust removal device 14, the concentration of ash particles is only 4 mg/Nm 3 , the concentration of SO 2 is reduced to 20 mg/Nm 3 , and the concentration of dioxin after being adsorbed by the activated coke adsorption tower 15 is about 0.0097 ng /Nm 3 or so.
处理后的烟气为洁净烟气,通过引风机16抽引、第二换热器18加热烟气到150℃后经烟囱17排放到大气中。The treated flue gas is clean flue gas, drawn by the induced draft fan 16, heated by the second heat exchanger 18 to 150°C, and then discharged into the atmosphere through the chimney 17.
上述应用例仅用于解释说明本发明的发明构思,而非对本发明权利保护的限定,凡是依据本发明的技术和方法实质对以上实施例所做的任何简单修改、等同变化与修饰,均仍属于本发明的技术和方法方案的范围内。The above application examples are only used to explain the inventive concept of the present invention, rather than to limit the protection of the rights of the present invention. Any simple modifications, equivalent changes and modifications made to the above embodiments according to the essence of the technology and methods of the present invention are still valid. Belong to the technical and method scheme scope of the present invention.
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| CN110953589A (en) * | 2019-12-05 | 2020-04-03 | 大连绿诺集团有限公司 | Bubbling type internal circulating fluidized bed incinerator capable of self-sustaining incineration of low-calorific-value sludge |
| CN111530216A (en) * | 2020-06-12 | 2020-08-14 | 中冶赛迪技术研究中心有限公司 | A flue gas quenching and dust removal device and control method for inhibiting dioxin regeneration |
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Application publication date: 20181106 |