CN100377763C - A method of using active coke to purify flue gas - Google Patents
A method of using active coke to purify flue gas Download PDFInfo
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- CN100377763C CN100377763C CNB2004100862724A CN200410086272A CN100377763C CN 100377763 C CN100377763 C CN 100377763C CN B2004100862724 A CNB2004100862724 A CN B2004100862724A CN 200410086272 A CN200410086272 A CN 200410086272A CN 100377763 C CN100377763 C CN 100377763C
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- 239000000571 coke Substances 0.000 title claims abstract description 90
- 239000003546 flue gas Substances 0.000 title claims abstract description 81
- UGFAIRIUMAVXCW-UHFFFAOYSA-N Carbon monoxide Chemical compound [O+]#[C-] UGFAIRIUMAVXCW-UHFFFAOYSA-N 0.000 title claims abstract description 79
- 238000000034 method Methods 0.000 title claims abstract description 40
- 238000006477 desulfuration reaction Methods 0.000 claims abstract description 22
- 230000023556 desulfurization Effects 0.000 claims abstract description 22
- MWUXSHHQAYIFBG-UHFFFAOYSA-N nitrogen oxide Inorganic materials O=[N] MWUXSHHQAYIFBG-UHFFFAOYSA-N 0.000 claims abstract description 12
- 238000002347 injection Methods 0.000 claims description 11
- 239000007924 injection Substances 0.000 claims description 11
- 238000006243 chemical reaction Methods 0.000 claims description 5
- 239000007921 spray Substances 0.000 claims description 5
- 239000003595 mist Substances 0.000 claims 1
- 238000000746 purification Methods 0.000 abstract description 22
- 229910052753 mercury Inorganic materials 0.000 abstract description 10
- 239000007789 gas Substances 0.000 abstract description 8
- QSHDDOUJBYECFT-UHFFFAOYSA-N mercury Chemical compound [Hg] QSHDDOUJBYECFT-UHFFFAOYSA-N 0.000 abstract description 7
- 229910001385 heavy metal Inorganic materials 0.000 abstract description 4
- 239000003344 environmental pollutant Substances 0.000 abstract description 3
- 231100000719 pollutant Toxicity 0.000 abstract description 3
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 abstract description 2
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 description 6
- 238000005516 engineering process Methods 0.000 description 6
- 238000010586 diagram Methods 0.000 description 5
- 230000008929 regeneration Effects 0.000 description 5
- 238000011069 regeneration method Methods 0.000 description 5
- 238000005507 spraying Methods 0.000 description 5
- 239000003638 chemical reducing agent Substances 0.000 description 4
- 239000003245 coal Substances 0.000 description 4
- 239000000843 powder Substances 0.000 description 3
- QAOWNCQODCNURD-UHFFFAOYSA-N Sulfuric acid Chemical compound OS(O)(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-N 0.000 description 2
- 230000018109 developmental process Effects 0.000 description 2
- 238000010438 heat treatment Methods 0.000 description 2
- 238000001179 sorption measurement Methods 0.000 description 2
- VYZAMTAEIAYCRO-UHFFFAOYSA-N Chromium Chemical compound [Cr] VYZAMTAEIAYCRO-UHFFFAOYSA-N 0.000 description 1
- 241001465754 Metazoa Species 0.000 description 1
- 229910002651 NO3 Inorganic materials 0.000 description 1
- NHNBFGGVMKEFGY-UHFFFAOYSA-N Nitrate Chemical compound [O-][N+]([O-])=O NHNBFGGVMKEFGY-UHFFFAOYSA-N 0.000 description 1
- NINIDFKCEFEMDL-UHFFFAOYSA-N Sulfur Chemical compound [S] NINIDFKCEFEMDL-UHFFFAOYSA-N 0.000 description 1
- 238000003916 acid precipitation Methods 0.000 description 1
- 238000003915 air pollution Methods 0.000 description 1
- 229910052799 carbon Inorganic materials 0.000 description 1
- 229910052804 chromium Inorganic materials 0.000 description 1
- 239000011651 chromium Substances 0.000 description 1
- 229910052956 cinnabar Inorganic materials 0.000 description 1
- 239000000428 dust Substances 0.000 description 1
- 230000000694 effects Effects 0.000 description 1
- 238000003912 environmental pollution Methods 0.000 description 1
- 238000007254 oxidation reaction Methods 0.000 description 1
- 239000002245 particle Substances 0.000 description 1
- 230000036632 reaction speed Effects 0.000 description 1
- 229910052717 sulfur Inorganic materials 0.000 description 1
- 239000011593 sulfur Substances 0.000 description 1
- 238000011282 treatment Methods 0.000 description 1
- 239000002699 waste material Substances 0.000 description 1
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Abstract
本发明公开了一种应用活性焦净化烟气的方法。本发明所提供的应用活性焦净化烟气的方法,包括烟气在装有活性焦的由两段移动床反应器构成的脱硫脱硝反应器中进行净化,其流程是:烟气先进入底部装有来自第一段反应器的活性焦的第二段反应器,吸附脱除烟气中的SO2,然后与NH3或H2和CO混合气体混合后,进入顶部第一段加有活性焦的反应器,与顶部第一段反应器中的活性焦反应脱除其中的氮氧化物,其中,所述烟气还通过喷射活性焦的管道进行净化。本发明应用活性焦净化烟气的方法能同时脱除SO2、NOX和汞等重金属污染物,具有烟气净化率高、工程投资低、净化过程不消耗水等优点,具有广泛的推广应用前景。The invention discloses a method for purifying flue gas by using active coke. The method of using activated coke to purify flue gas provided by the present invention comprises that the flue gas is purified in a desulfurization and denitrification reactor composed of a two-stage moving bed reactor equipped with activated coke, and the process is as follows: the flue gas first enters the bottom The second stage reactor with active coke from the first stage reactor absorbs and removes SO 2 in the flue gas, and then mixes it with NH 3 or H 2 and CO mixed gas, and enters the top first stage with active coke The reactor reacts with the activated coke in the first stage reactor at the top to remove nitrogen oxides, wherein the flue gas is also purified through the pipeline for injecting activated coke. The method of using activated coke to purify flue gas in the present invention can remove heavy metal pollutants such as SO 2 , NO X and mercury at the same time, has the advantages of high flue gas purification rate, low engineering investment, no water consumption in the purification process, etc., and has wide popularization and application prospect.
Description
技术领域 technical field
本发明涉及烟气净化方法,特别是涉及一种应用活性焦净化烟气的方法。The invention relates to a flue gas purification method, in particular to a method for purifying flue gas using active coke.
背景技术 Background technique
发展洁净煤技术是可持续发展战略之 。我国大气污染主要是由燃煤引起的,所产生的NOx与SO2可以造成酸雨危害;而煤中汞、铅、铬等重金属在燃烧后可能引起的环境污染已经受到人们的广泛关注,以汞为例,汞在煤中通常以朱砂和游离汞的形式存在,其燃烧时多挥发到烟气中对人畜有害。The development of clean coal technology is one of the sustainable development strategies. Air pollution in China is mainly caused by coal burning, and the produced NO x and SO 2 can cause acid rain hazards; and the possible environmental pollution caused by heavy metals such as mercury, lead, and chromium in coal after burning has attracted widespread attention. Mercury is an example. Mercury usually exists in the form of cinnabar and free mercury in coal. When it is burned, it volatilizes into the flue gas and is harmful to humans and animals.
目前,国外烟气净化大部分采用湿法技术,但湿法烟气净化技术在国内部分地区电厂推广应用受到限制。活性焦烟气净化技术是一种先进的干法烟气净化技术,已开发研究了活性焦固定床、移动床等方法。本发明发明人于2004年6月25日申请了名称为“一种烟气脱硫、脱硝方法”的发明专利,申请号为200410038037.X。该烟气脱硫、脱硝方法在由两段移动床反应器构成的脱硫脱硝反应器中进行,流程包括:烟气先进入底部装有来自第一段反应器的活性焦的第二段反应器,吸附脱除烟气中的SO2,然后与NH3或H2和CO混合气体混合后,进入顶部第一段加有活性焦的反应器,与顶部第一段反应器中的活性焦反应脱除其中的氮氧化物,生成气体排入大气。该方法在NH3或H2和CO混合还原剂作用下,具有较高的脱硝性能,解决了烟气脱硫、脱硝中所存在的反应速度慢、脱硝效率低等问题,主要用于烟气脱硫和脱硝;但是,该技术所用移动床装置一般比较庞大,设备投资高,另外,在脱硫、脱硝过程中所产生的破碎活性焦一般通过焚烧处理,利用率不高,使得运行成本偏高。At present, most foreign flue gas purification adopts wet technology, but the promotion and application of wet flue gas purification technology in power plants in some areas of China is limited. Activated coke flue gas purification technology is an advanced dry flue gas purification technology, and methods such as active coke fixed bed and moving bed have been developed and studied. The inventor of the present invention applied for an invention patent titled "a method for flue gas desulfurization and denitrification" on June 25, 2004, and the application number is 200410038037.X. The flue gas desulfurization and denitrification method is carried out in a desulfurization and denitrification reactor composed of two-stage moving bed reactors. The process includes: the flue gas first enters the second-stage reactor with activated coke from the first-stage reactor at the bottom, The SO 2 in the flue gas is adsorbed and removed, and then mixed with NH 3 or H 2 and CO mixed gas, then enters the reactor with activated coke in the first section of the top, and reacts with the active coke in the first section of the top reactor. In addition to nitrogen oxides, the resulting gas is discharged into the atmosphere. Under the action of NH3 or H2 and CO mixed reducing agent, this method has high denitrification performance, solves the problems of slow reaction speed and low denitrification efficiency in flue gas desulfurization and denitrification, and is mainly used for flue gas desulfurization and denitrification; however, the moving bed device used in this technology is generally relatively large, and the equipment investment is high. In addition, the broken activated coke produced in the process of desulfurization and denitrification is generally processed by incineration, and the utilization rate is not high, which makes the operating cost high.
发明内容 Contents of the invention
本发明的目的是提供一种应用活性焦高效连续的烟气净化方法。The object of the present invention is to provide an efficient and continuous flue gas purification method using active coke.
本发明所提供的应用活性焦净化烟气的方法,包括烟气在装有活性焦的由两段移动床反应器构成的脱硫脱硝反应器中进行净化,其流程是:烟气先进入底部装有来自第一段反应器的活性焦的第二段反应器,吸附脱除烟气中的SO2,然后与NH3或H2和CO混合气体混合后,进入顶部第一段加有活性焦的反应器,与顶部第一段反应器中的活性焦反应脱除其中的氮氧化物,其特征在于:所述烟气还通过喷射活性焦的管道进行净化。The method of using activated coke to purify flue gas provided by the present invention comprises that the flue gas is purified in a desulfurization and denitrification reactor composed of a two-stage moving bed reactor equipped with activated coke, and the process is as follows: the flue gas first enters the bottom The second stage reactor with active coke from the first stage reactor absorbs and removes SO 2 in the flue gas, and then mixes it with NH 3 or H 2 and CO mixed gas, and enters the top first stage with active coke The reactor reacts with the activated coke in the first stage reactor at the top to remove nitrogen oxides therein, and it is characterized in that: the flue gas is also purified through a pipeline for injecting activated coke.
本发明烟气净化方法具有多种组合方式,烟气可以先通过装有活性焦的由两段移动床反应器构成的脱硫脱硝反应器进行净化,然后再通过喷射活性焦的管道进行净化。也可以先通过喷射活性焦的管道进行净化,然后再通过装有活性焦的由两段移动床反应器构成的脱硫脱硝反应器进行净化。The flue gas purification method of the present invention has multiple combinations. The flue gas can be purified first through a desulfurization and denitrification reactor composed of two-stage moving bed reactors equipped with active coke, and then through a pipeline for injecting active coke. It can also be purified first through the pipeline for injecting active coke, and then through the desulfurization and denitrification reactor composed of two-stage moving bed reactors equipped with active coke.
为了提高烟气净化效率,所述管道喷射用活性焦来源于所述两段移动床反应器产生的活性焦,通常需要将其磨成粉末后使用。In order to improve the flue gas purification efficiency, the active coke used for pipeline injection is derived from the active coke produced by the two-stage moving bed reactor, which usually needs to be ground into powder before use.
烟气经过管道喷射活性焦进行净化后,经过除尘器将烟气与粉末活性焦分离,可以排空或用于进行下一步的脱硫、脱硝。After the flue gas is purified by spraying activated coke through the pipeline, the flue gas is separated from the powdered active coke through the dust collector, and can be emptied or used for the next step of desulfurization and denitrification.
在本发明中,所述移动床空速为800-2000h-1,管道喷射活性焦的喷射量为10-400mg活性焦/m3烟气。为了保证烟气净化的效果,烟气的温度在100-180℃为好。In the present invention, the space velocity of the moving bed is 800-2000h -1 , and the injection amount of activated coke injected into the pipeline is 10-400mg active coke/m 3 flue gas. In order to ensure the effect of flue gas purification, the temperature of the flue gas is preferably 100-180°C.
本发明所采用的活性焦优选使用申请号为02146004.3,发明名称为“一种制备活性炭的方法”的专利申请中制备的活性焦。脱硫、脱硝反应进行的两段移动床反应器可以选用本发明的发明人发明的专利号为00254473.3,名称为“一种烟气脱硫装置”中所公开的反应器。The active coke used in the present invention is preferably the active coke prepared in the patent application with the application number 02146004.3 and the title of the invention "a method for preparing activated carbon". The two-stage moving bed reactor for desulfurization and denitrification reactions can be selected from the reactor disclosed in the patent No. 00254473.3 named "a flue gas desulfurization device" invented by the inventor of the present invention.
本发明应用活性焦净化烟气的方法分为两段,其中采用活性焦移动床反应器脱硫、脱硝工艺示意图如图1A所示,采用管道喷射活性焦净化烟气的工艺示意图如图1B所示。在移动床中产生的破碎活性焦经过多次SO2吸附和加热再生处理,由于加热再生是活性焦表面的硫酸与活性焦表面的碳发生氧化反应,其吸附脱汞性能有显著提高,可以将其磨成粉末后,用于管道喷射净化烟气。在本发明中,由于管道喷射净化脱除烟气中部分SO2、NOX和汞等重金属污染物,减少了活性焦移动床烟气净化的压力,使活性焦移动床空速可以从常规工艺的200-600h-1提高到800-2000h-1,能使移动床反应器体积缩小,而管道喷射所用活性焦性能高,既可显著提高烟气净化效率,又能减少移动床活性焦的浪费,节约活性焦用量,使烟气净化成本显著降低。本发明应用活性焦净化烟气的方法能同时脱除SO2、NOX和汞等重金属污染物,具有烟气净化率高、工程投资低、净化过程不消耗水等优点,具有广泛的推广应用前景。The method of using activated coke to purify flue gas in the present invention is divided into two stages, wherein the schematic diagram of the desulfurization and denitrification process using activated coke moving bed reactor is shown in Figure 1A, and the process schematic diagram of using pipeline spraying activated coke to purify flue gas is shown in Figure 1B . The broken activated coke produced in the moving bed has undergone multiple SO2 adsorption and heating regeneration treatments. Since the heating regeneration is the oxidation reaction between the sulfuric acid on the surface of the active coke and the carbon on the surface of the active coke, its adsorption and demercuration performance has been significantly improved, which can After it is ground into powder, it is used for pipe spraying to purify flue gas. In the present invention, due to the removal of some heavy metal pollutants such as SO 2 , NO X and mercury in the flue gas by pipe injection purification, the pressure of the flue gas purification of the active coke moving bed is reduced, so that the space velocity of the active coke moving bed can be changed from the conventional process The 200-600h -1 can be increased to 800-2000h -1 , which can reduce the volume of the moving bed reactor, and the active coke used in the pipe injection has high performance, which can not only significantly improve the flue gas purification efficiency, but also reduce the waste of moving bed active coke , save the amount of active coke, and significantly reduce the cost of flue gas purification. The method of using activated coke to purify flue gas in the present invention can remove heavy metal pollutants such as SO 2 , NO X and mercury at the same time, has the advantages of high flue gas purification rate, low engineering investment, no water consumption in the purification process, etc., and has wide popularization and application prospect.
附图说明 Description of drawings
图1A为采用活性焦移动床反应器脱硫、脱硝工艺示意图;Figure 1A is a schematic diagram of the desulfurization and denitrification process using an active coke moving bed reactor;
图1B为采用管道喷射活性焦净化烟气的工艺示意图;Fig. 1B is a schematic diagram of a process for purifying flue gas by injecting activated coke into a pipeline;
图2为管道喷射净化器的结构示意图。Fig. 2 is a structural schematic diagram of a pipeline jet purifier.
具体实施方式 Detailed ways
实施例1、烟气净化脱硫、脱硝、脱汞Embodiment 1, flue gas purification desulfurization, denitrification, demercury
1、烟气采用活性焦移动床反应器进行净化1. The flue gas is purified by active coke moving bed reactor
利用南京电力自动化设备总厂生产的两段移动床反应器脱除烟气中的硫和硝。烟气中SO2浓度为5000mg/m3,NOX浓度为500mg/m3,Hg含量为20ug/m3,温度为120℃,移动床反应器空速为1000h-1。脱SOx/脱NOX反应器的第一段加有150公斤活性焦;加入的NH3和CO混合还原剂浓度为500 mg/m3(NH3/CO摩尔比为20),温度为10-100℃,进气流量为500m3/h。经过第二段脱硫反应的活性焦回收送入再生塔,在200-600u℃下加热3-30h再生,再生过程产生的CO气体送入脱SOx/脱NOX反应器,再生好的活性焦补加其总量的0.5-10%新活性焦后送入脱SOx/脱NOX反应器的第一段,开始下一个循环。Sulfur and nitrate in flue gas were removed by using two-stage moving bed reactor produced by Nanjing Electric Power Automation Equipment General Factory. The SO 2 concentration in the flue gas is 5000mg/m 3 , the NO X concentration is 500mg/m 3 , the Hg content is 20ug/m 3 , the temperature is 120°C, and the space velocity of the moving bed reactor is 1000h -1 . 150 kg of active coke is added to the first section of the SO x / NO x reactor; the concentration of NH 3 and CO mixed reducing agent added is 500 mg/m 3 (NH 3 /CO molar ratio is 20), and the temperature is 10 -100°C, the intake air flow rate is 500m 3 /h. The activated coke after the second desulfurization reaction is recycled and sent to the regeneration tower, heated at 200-600u°C for 3-30h for regeneration, and the CO gas generated during the regeneration process is sent to the deSOx / deNOx reactor to regenerate the activated coke After adding 0.5-10% of the total amount of new active coke, it is sent to the first section of the de-SO x / de-NO x reactor to start the next cycle.
2、烟气采用管道喷射活性焦进行净化2. The flue gas is purified by pipe spraying active coke
将上步在移动床中生成的破碎活性焦磨成粒度为100-320目的粉末,用于管道喷射净化器。Grind the crushed active coke generated in the moving bed in the previous step into a powder with a particle size of 100-320 mesh, which is used in the pipeline jet purifier.
该管道喷射净化器的结构如图2所示,活性焦储存仓11,定量给料器12、气体压缩机13以及活性焦输送管道14组成活性焦输送系统,管道22上有一排活性焦输入孔21用于向管道22中喷入活性焦,烟气在管道22内流动。储存于活性焦储存仓11的活性焦进入定量给料器12,用气体压缩机13向其中压入空气,通过定量给料器12控制活性焦的喷射量,喷出活性焦经活性焦输送管道14从活性焦输入孔21送入管道22内,净化管道22中的烟气。The structure of the pipeline jet purifier is shown in Figure 2, the active
将经过移动床反应器的烟气通入到管道喷射净化器中,以150mg活性焦粉末/m3烟气的喷射量向管道中喷射活性焦。The flue gas passing through the moving bed reactor is passed into the pipe jet cleaner, and the active coke is sprayed into the pipe at an injection rate of 150mg active coke powder/ m3 flue gas.
整个过程烟气SO2脱除率为95%,NOX脱除率为79%,Hg脱除率为85%。The removal rate of flue gas SO 2 is 95%, NO X removal rate is 79%, and Hg removal rate is 85%.
实施例2、烟气净化脱硫、脱硝、脱汞Embodiment 2, flue gas purification desulfurization, denitrification, demercury
1、烟气采用管道喷射活性焦进行净化1. The flue gas is purified by pipe spraying active coke
烟气SO2含量为3000mg/m3,NOX浓度为300mg/m3,Hg含量为10ug/m3,烟气温度为120℃,将该烟气通入到如实施例1的管道喷射净化器中,以380mg活性焦粉末/m3烟气的喷射量向管道中喷射活性焦。其中,最初所用活性焦粉末可以采用新活性焦,以后的过程可以采用在移动床中生成的破碎活性焦。The flue gas SO 2 content is 3000mg/m 3 , the NO X concentration is 300mg/m 3 , the Hg content is 10ug/m 3 , and the flue gas temperature is 120°C, the flue gas is passed into the pipeline as in Example 1 for jet purification In the device, inject active coke into the pipeline at an injection rate of 380mg active coke powder/m 3 flue gas. Among them, the initial active coke powder used can be new active coke, and the subsequent process can use broken active coke generated in the moving bed.
2、烟气采用活性焦移动床反应器进行净化2. The flue gas is purified by active coke moving bed reactor
将上步所得烟气通入到如实施例1的移动床反应器中,其中,移动床空速为800h-1,加入的NH3和CO混合还原剂的浓度为300PPm(NH3/CO摩尔比为5),其余过程按照实施例1进行。Pass the flue gas obtained in the previous step into the moving bed reactor as in Example 1, wherein the space velocity of the moving bed is 800h -1 , and the concentration of the added NH 3 and CO mixed reducing agent is 300PPm (NH 3 /CO molar Ratio is 5), and all the other processes are carried out according to embodiment 1.
整个过程烟气SO2脱除率为98%,NOX脱除率为83%,Hg脱除率为90%。The removal rate of flue gas SO2 is 98%, NOx removal rate is 83%, and Hg removal rate is 90%.
实施例3、烟气净化脱硫、脱硝、脱汞Embodiment 3, flue gas purification desulfurization, denitrification, demercury
烟气SO2含量为7500 mg/m3,NOX浓度为600 mg/m3,Hg含量为25ug/m3,烟气温度为180℃,按照实施例1的步骤1和步骤2连续进行烟气净化,其中,移动床空速为900h-1,加入的H2和CO混合还原剂的浓度为600mg/m3(H2/CO摩尔比为0.5),活性焦管道喷射量为50mg/m3。整个过程SO2脱除率为90%,NOX脱除率为75%,Hg脱除率为80%。The flue gas SO 2 content is 7500 mg/m 3 , the NO X concentration is 600 mg/m 3 , the Hg content is 25ug/m 3 , the flue gas temperature is 180°C, and the flue gas is continuously carried out according to step 1 and step 2 of Example 1. Gas purification, where the space velocity of the moving bed is 900h -1 , the concentration of the added H 2 and CO mixed reducing agent is 600mg/m 3 (the molar ratio of H 2 /CO is 0.5), and the injection amount of activated coke pipeline is 50mg/m 3 . The removal rate of SO2 is 90%, NOx removal rate is 75%, and Hg removal rate is 80% in the whole process.
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