CN1962035A - Spray cyclone bed type gas liquid solid tri-phase reactor - Google Patents
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Abstract
喷射旋流床式气液固三相反应器,使用若干台循环泵,将浆料池内的浆液从四角或四墙部位抽出,经循环泵的加速后形成多股高速射流从浆料池的周围切向喷入浆料池,驱动浆料池整体旋转,替代了机械桨叶搅拌器对浆料池的搅拌作用。整个流场大致上形成稳定的单一旋转流场,可以较为方便地控制固相颗粒的分选过程。而氧化空气直接在高速射流的喷口内投入,液相和气相有很大的速度差,高速的液相将气泡击碎,大大强化了气液之间的混合,可提高气液反应强度,另外,气相在浆池中形成螺旋运动的轨迹而不是自由上浮的状态,会延长气泡在浆池中的停留时间,从而提高氧化空气的利用率。
The jet swirl bed type gas-liquid-solid three-phase reactor uses several circulating pumps to extract the slurry in the slurry pool from the four corners or four walls, and after being accelerated by the circulating pump, multiple high-speed jets flow from the surrounding of the slurry pool. Tangential spraying into the slurry tank drives the overall rotation of the slurry tank, replacing the stirring effect of the mechanical paddle agitator on the slurry tank. The entire flow field roughly forms a stable single rotating flow field, which can control the sorting process of solid phase particles more conveniently. The oxidizing air is directly injected into the nozzle of the high-speed jet, and there is a large speed difference between the liquid phase and the gas phase. The high-speed liquid phase crushes the bubbles, which greatly strengthens the mixing between the gas and liquid, and can increase the gas-liquid reaction intensity. , The gas phase forms a spiral trajectory in the pulp tank instead of a free floating state, which will prolong the residence time of the bubbles in the pulp tank, thereby improving the utilization rate of oxidizing air.
Description
技术领域technical field
本发明属于三相反应器技术领域,具体涉及一种用于大型湿法烟气脱硫的浆液池的喷射旋流床式气液固三相反应器。The invention belongs to the technical field of three-phase reactors, and in particular relates to a jet swirl bed type gas-liquid-solid three-phase reactor used for a large-scale wet flue gas desulfurization slurry pool.
背景技术Background technique
湿法脱硫在吸收塔中完成SO2的吸收,而在浆液池中完成SO2的氧化与固化。浆液池是气固混合物吸收气体的重要部件,承担着气体与吸收液的分离,吸收液的中和,石膏氧化与结晶等重要任务,它的运行情况直接决定了吸收液的质量浓度、化学反应进行的状况以及排出物料的品质。Wet desulfurization completes the absorption of SO 2 in the absorption tower, and completes the oxidation and solidification of SO 2 in the slurry tank. The slurry tank is an important part of the gas-solid mixture to absorb gas. It undertakes important tasks such as the separation of gas and absorption liquid, the neutralization of absorption liquid, the oxidation and crystallization of gypsum, and its operation directly determines the mass concentration and chemical reaction of the absorption liquid. The status of the process and the quality of the discharged material.
浆液池主要的功能为:调制浆液:新鲜的石灰石粉(或石灰石浆)以及补给的新鲜水需要首先在浆池中充分混合,调配成为合适浓度和成分的脱硫浆液;氧化CaSO3:氧化空气直接输入浆液池,与吸收塔中回落下来的浆液(因与SO2反应,生成大量CaSO3)进行氧化反应,将CaSO3氧化为CaSO4,这一环节不但关系到能否充分实现固硫(把容易分解的CaSO3转化为稳定的CaSO4),也直接关系到浆液管道结垢的情况;调节浆液pH值及其它成分:浆液池中各种物料的平衡状况及添加剂的投入状况将决定在系统中循环的浆液的pH值及其它成分,浆液的pH值直接关系到吸收塔中对SO2的吸收能力,也影响CaSO3氧化反应的进行,pH值的调节,需要在浆液池中进行;液固分离:因为石膏必须结晶并成长到一定的粒径,才能作为合格的副产品排出,同时还要保证排出的石膏浆中其它杂质(主要是CaCO3和CaSO3)的含量处于限定的范围之内,此时,必须合理组织浆液池中的液固分离过程,保证石膏颗粒的分选质量;调节反应物停留时间:在湿法脱硫的浆液池设计中,有三个重要的停留时间需要得到保证,一是作为脱硫剂的石灰石颗粒在系统中的停留时间,因为石灰石是一种难溶物质,在弱酸性条件下,大约需要8~14小时才能消溶完毕,所以必须保证其在系统内有充足的停留时间才能保证石灰石充分参与脱硫反应;二是进入吸收塔的循环浆液的停留时间,因为从吸收塔中回落的浆液对吸收SO2而言是一种接近饱和的状态,必须在浆液池中停留足够的时间,使得SO3 2-充分转化为其它成分(如固相的CaCO3、CaSO4或SO4 2-),才能重新具备吸收SO2的能力而再次进入吸收塔;三是作为氧化剂的氧化空气在系统中的停留时间,氧气不是一种易溶于水的气体,而氧必须溶解于浆液才能参与CaSO3的氧化反应,所以必须保证氧化空气在浆池中有足够的停留时间,才能保证氧化反应的进行深度和氧化空气有较高的利用率。以上三种停留时间还必须相互匹配,以保证各种脱硫、固硫反应的充分完成;系统缓冲:脱硫系统的各个参数在运行期间是不断变化的,比如电站锅炉的负荷变化导致烟气量变化、燃烧的煤质变化导致烟气成分变化、石灰石粉的成分变化以及整个系统可能的其它情况导致的各种参数的变化,而在这些参数变化的情况下,整个系统应该是稳定而不是敏感的,保证烟气的脱硫率、排出石膏浆的品质及系统本身的稳定运行,此时,浆液的pH值、浆液主要成分、固相颗粒的粒径和分布情况等不应该发生明显的变化,就需要通过浆液池自身的物理缓冲及化学缓冲能力来保证。The main functions of the slurry tank are: preparation of slurry: fresh limestone powder (or limestone slurry) and fresh water for supply need to be fully mixed in the slurry tank first to prepare a desulfurization slurry with suitable concentration and composition; oxidation of CaSO 3 : oxidation of air directly Enter the slurry tank, and carry out oxidation reaction with the slurry falling back in the absorption tower (because of reacting with SO 2 to generate a large amount of CaSO 3 ), and oxidize CaSO 3 to CaSO 4 , this link is not only related to whether the sulfur fixation can be fully realized (put Easily decomposed CaSO 3 is converted into stable CaSO 4 ), which is also directly related to the scaling of the slurry pipeline; adjusting the pH value and other components of the slurry: the balance of various materials in the slurry tank and the input status of additives will determine the system The pH value and other components of the circulating slurry, the pH value of the slurry is directly related to the absorption capacity of SO 2 in the absorption tower, and also affects the progress of the CaSO 3 oxidation reaction. The adjustment of the pH value needs to be carried out in the slurry tank; Solid separation: Because gypsum must crystallize and grow to a certain particle size, it can be discharged as a qualified by-product, and at the same time, it is necessary to ensure that the content of other impurities (mainly CaCO 3 and CaSO 3 ) in the discharged gypsum slurry is within a limited range , at this time, the liquid-solid separation process in the slurry tank must be reasonably organized to ensure the sorting quality of gypsum particles; adjust the residence time of the reactants: in the design of the slurry tank for wet desulfurization, there are three important residence times that need to be guaranteed. One is the residence time of limestone particles used as a desulfurizer in the system. Because limestone is a kind of insoluble substance, it takes about 8 to 14 hours to dissolve completely under weakly acidic conditions, so it must be ensured that there is sufficient desulfurization in the system. The residence time can ensure that limestone fully participates in the desulfurization reaction; the second is the residence time of the circulating slurry entering the absorption tower, because the slurry falling back from the absorption tower is a state close to saturation for absorbing SO 2 and must stay in the slurry pool Enough time, so that SO 3 2- is fully converted into other components (such as solid-phase CaCO 3 , CaSO 4 or SO 4 2- ), can regain the ability to absorb SO 2 and enter the absorption tower again; the third is as an oxidant The residence time of oxidizing air in the system. Oxygen is not a gas that is easily soluble in water, and oxygen must be dissolved in the slurry to participate in the oxidation reaction of CaSO 3 . Ensure the depth of oxidation reaction and high utilization rate of oxidation air. The above three residence times must also be matched with each other to ensure the full completion of various desulfurization and sulfur fixation reactions; system buffer: various parameters of the desulfurization system are constantly changing during operation, such as changes in the load of power plant boilers lead to changes in flue gas volume , The change of the coal quality of the combustion leads to the change of the flue gas composition, the change of the composition of the limestone powder, and the change of various parameters caused by the possible other conditions of the whole system. In the case of these parameter changes, the whole system should be stable and not sensitive , to ensure the desulfurization rate of the flue gas, the quality of the discharged gypsum slurry and the stable operation of the system itself. At this time, the pH value of the slurry, the main components of the slurry, and the particle size and distribution of solid particles should not change significantly. It needs to be guaranteed by the physical buffer and chemical buffer capacity of the slurry pool itself.
湿法脱硫系统中,浆液池也是故障率较高的部件,在材料强度、安装减震、浆液的溢出和工程效率等诸多方面尚存在问题。传统的浆液池是采用机械搅拌的鼓泡床反应器,氧化空气由空气输入管从浆液池底部或搅拌器前方输入,采用垂直搅拌器一般一个浆池只布置一个搅拌器,流场结构相对简单,固相分选作用好,但是。对于300MW以上的锅炉机组,搅拌器的桨叶直径在10米乃至15米以上,不但其本身结构笨重,而且为浆液池上方的吸收塔布置带来一定的困难,此时必须采用吸收塔与浆液池不同心的偏心布置方式,或者必须采用双塔结构;采用侧壁机械搅拌方式,搅拌器的个数可以增加,但是整个浆液池内流场的情况十分复杂,难以兼顾固相分选的问题,而且浆池壁的受力状况不佳,同时转轴与浆池壁之间的密封有一定困难,时常有浆液泄漏的情况发生。In the wet desulfurization system, the slurry tank is also a component with a high failure rate, and there are still problems in many aspects such as material strength, installation shock absorption, slurry overflow, and engineering efficiency. The traditional slurry tank is a mechanically agitated bubbling bed reactor. Oxidation air is input from the bottom of the slurry tank or in front of the agitator through the air inlet pipe. A vertical agitator is used. Generally, only one agitator is arranged in a slurry tank, and the flow field structure is relatively simple. , solid-phase separation works well, however. For boiler units above 300MW, the diameter of the blades of the agitator is 10 meters or even more than 15 meters, which not only has a heavy structure, but also brings certain difficulties to the arrangement of the absorption tower above the slurry tank. At this time, the absorption tower and slurry must be used. The eccentric layout of the tank is not concentric, or the double tower structure must be adopted; the number of agitators can be increased by using the side wall mechanical stirring method, but the flow field in the entire slurry tank is very complicated, and it is difficult to take into account the problem of solid phase separation. Moreover, the stressed state of the slurry tank wall is not good, and the seal between the rotating shaft and the slurry tank wall is difficult, and the situation of slurry leakage often occurs.
这种反应器主要的缺点是:由于要照顾到固相的分选,机械搅拌的流速不可能很高大约50r/min,氧化空气的气泡基本上是一种自由上浮的状态,气液混合不够强烈,氧化反应速度相对较慢,而且一旦出现故障,氧化空气的利用率低于30%;脱硫塔属于大型反应装置,而机械搅拌器在大型化时,结构笨重、难于布置、故障率高、维修不便且必须停机维修。The main disadvantage of this kind of reactor is: due to the separation of solid phase, the flow rate of mechanical stirring cannot be as high as about 50r/min, the bubbles of oxidizing air are basically in a state of free floating, and the gas-liquid mixing is not enough Strong, the oxidation reaction speed is relatively slow, and once a failure occurs, the utilization rate of the oxidation air is lower than 30%; the desulfurization tower is a large-scale reaction device, and when the mechanical agitator is large-scale, the structure is bulky, difficult to arrange, and the failure rate is high. Maintenance is inconvenient and must be shut down for maintenance.
发明内容Contents of the invention
本发明的目的在于克服上述现有技术的缺点,提供了一种无需机械搅拌部件,可以防止结垢、磨损及其它机械部件故障的喷射旋流床式气液固三相反应器。The object of the present invention is to overcome the above-mentioned shortcoming of prior art, provide a kind of jet swirl bed type gas-liquid-solid three-phase reactor that does not need mechanical stirring parts, can prevent fouling, wear and other mechanical parts failure.
为达到上述目的,本发明采用的技术方案是:包括浆料池,在浆料池的四壁上各布置有一台或一台以上的浆液循环泵,该浆液循环泵的入口与出口分别通过管路与浆液池的引出口及送入口相连通,送入口的管路还与氧化空气管路相连通,且引出口和送入口与浆料池的四角或四墙切向角为5°~40°。In order to achieve the above-mentioned purpose, the technical solution adopted by the present invention is to include a slurry tank, one or more slurry circulation pumps are respectively arranged on the four walls of the slurry tank, and the inlet and outlet of the slurry circulation pump are respectively passed through pipes. The road is connected with the outlet and the inlet of the slurry tank, and the pipeline of the inlet is also connected with the oxidation air pipeline, and the tangential angle between the outlet and the inlet and the four corners or four walls of the slurry tank is 5°~40° °.
由于本发明使用若干台循环泵,将浆料池内的浆液从四角或四墙部位抽出,经循环泵的加速后形成多股高速射流从浆料池的周围切向喷入浆料池,驱动浆料池整体旋转,替代了机械桨叶搅拌器对浆料池的搅拌作用。整个流场大致上形成稳定的单一旋转流场,可以较为方便地控制固相颗粒的分选过程。而氧化空气直接在高速射流的喷口内投入,液相和气相有很大的速度差,高速的液相将气泡击碎,大大强化了气液之间的混合,可提高气液反应强度,另外,气相在浆池中形成螺旋运动的轨迹而不是自由上浮的状态,会延长气泡在浆池中的停留时间,从而提高氧化空气的利用率,且本发明只需使用若干循环泵和连接管道,布置方便灵活,省去了笨重的机械搅拌桨叶,十分有利于反应器的大型化。Because the present invention uses several circulation pumps, the slurry in the slurry pool is extracted from the four corners or four walls, and after the acceleration of the circulation pump, multiple high-speed jets are formed and sprayed into the slurry pool tangentially from the periphery of the slurry pool to drive the slurry. The overall rotation of the material tank replaces the stirring effect of the mechanical paddle agitator on the slurry tank. The entire flow field roughly forms a stable single rotating flow field, which can control the sorting process of solid phase particles more conveniently. The oxidizing air is directly injected into the nozzle of the high-speed jet, and there is a large speed difference between the liquid phase and the gas phase. The high-speed liquid phase crushes the bubbles, which greatly strengthens the mixing between the gas and liquid, and can increase the gas-liquid reaction intensity. , the gas phase forms a trajectory of spiral motion in the slurry tank instead of a free floating state, which will prolong the residence time of the air bubbles in the pulp tank, thereby improving the utilization rate of oxidation air, and the present invention only needs to use several circulation pumps and connecting pipes, The layout is convenient and flexible, eliminating the need for heavy mechanical stirring blades, which is very conducive to the enlargement of the reactor.
附图说明Description of drawings
图1是本发明的整体结构示意图。Fig. 1 is a schematic diagram of the overall structure of the present invention.
具体实施方式Detailed ways
下面结合附图对本发明作进一步详细说明。The present invention will be described in further detail below in conjunction with the accompanying drawings.
参见图1,本发明包括浆料池1,在浆料池1的四壁上各布置有一台浆液循环泵2,系统运行时浆液由引出口3引出被浆液循环泵2送到送入口4重新进入浆料池1,浆料池1的引出口3和送入口4与浆料池1的四角或四墙的切角为5°~40°,按照此角度设置后可在浆料池1内形成水流的两层水平旋转,从而实现气-液两相的湍动混合,该情形类似于火室燃烧炉中的四角切圆燃烧,从而达到搅拌的预期效果。Referring to Fig. 1, the present invention includes a
若浆料池的直径比较大时,本发明在浆料池1的四角或四壁上布置有多台浆液循环泵2,且此多台浆液循环泵2在同一水平面上。If the diameter of the slurry tank is relatively large, the present invention arranges multiple slurry circulation pumps 2 on the four corners or walls of the
如果浆料池1比较高时,本发明在浆料池1的四壁上沿浆料池1的高度方向上布置有多台的浆液循环泵2。If the
本发明在浆料池1周围有多股高速气液混合射流切向喷入浆料池1,这些射流的动量足以驱动浆料池1整体旋转,且气液两相混合强烈,也满足浆料池1传质的需要;浆料池1内的气液固三相流整体上为旋流,可以保持较强的液固混合强度,并形成合理的固相分层,实现对固相颗粒的合理分选;无机械搅拌器,但可通过调节射流速度,动态调节固相的浓度和粒度分布,使之达到颗粒分选的要求。参加反应的气体从射流喷口即送入口4内给入,气液相速度差大,气体被强制粉碎为小气泡,比表面积大、停留时间长,气液反应强烈。也可以根据需要在浆料池1底部或送入口4外给入气体,易于实现对现有设备的改装。In the present invention, there are multiple high-speed gas-liquid mixed jets sprayed tangentially into the
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Cited By (7)
| Publication number | Priority date | Publication date | Assignee | Title |
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| CN102019158A (en) * | 2010-11-01 | 2011-04-20 | 沈阳化工大学 | Tubular gas-liquid reactor capable of realizing synchronization of rotational flow and injection |
| CN103316576A (en) * | 2013-05-14 | 2013-09-25 | 宜兴市化工成套设备有限公司 | Desulfurizing and demisting combined tower |
| WO2015195051A1 (en) * | 2014-06-20 | 2015-12-23 | National University Of Singapore | Triphasic flow millireactors |
| CN106732259A (en) * | 2016-12-13 | 2017-05-31 | 衡阳华砷科技有限公司 | A kind of stirring means of reaction vessel |
| CN107020007A (en) * | 2017-06-05 | 2017-08-08 | 成都绿水科技有限公司 | A kind of economic benefits and social benefits reaction of high order type desulfurization slurry oxidization processing system and technique |
| CN108130265A (en) * | 2017-07-07 | 2018-06-08 | 北京昊海天际科技有限公司 | A kind of method for stirring fermentation materials in dry fermentation tank |
| CN112827344A (en) * | 2021-02-07 | 2021-05-25 | 华南理工大学 | A kind of jet extraction desulfurization tower slurry oxidation device and method |
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2006
- 2006-10-30 CN CN 200610104818 patent/CN1962035A/en active Pending
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| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN102019158A (en) * | 2010-11-01 | 2011-04-20 | 沈阳化工大学 | Tubular gas-liquid reactor capable of realizing synchronization of rotational flow and injection |
| CN102019158B (en) * | 2010-11-01 | 2013-06-19 | 沈阳化工大学 | Tubular gas-liquid reactor capable of realizing synchronization of rotational flow and injection |
| CN103316576A (en) * | 2013-05-14 | 2013-09-25 | 宜兴市化工成套设备有限公司 | Desulfurizing and demisting combined tower |
| WO2015195051A1 (en) * | 2014-06-20 | 2015-12-23 | National University Of Singapore | Triphasic flow millireactors |
| US9850184B2 (en) | 2014-06-20 | 2017-12-26 | National University Of Singapore | Triphasic flow millireactors |
| CN106732259A (en) * | 2016-12-13 | 2017-05-31 | 衡阳华砷科技有限公司 | A kind of stirring means of reaction vessel |
| CN107020007A (en) * | 2017-06-05 | 2017-08-08 | 成都绿水科技有限公司 | A kind of economic benefits and social benefits reaction of high order type desulfurization slurry oxidization processing system and technique |
| CN108130265A (en) * | 2017-07-07 | 2018-06-08 | 北京昊海天际科技有限公司 | A kind of method for stirring fermentation materials in dry fermentation tank |
| CN112827344A (en) * | 2021-02-07 | 2021-05-25 | 华南理工大学 | A kind of jet extraction desulfurization tower slurry oxidation device and method |
| CN112827344B (en) * | 2021-02-07 | 2025-02-11 | 华南理工大学 | A slurry oxidation device and method for jet exhaust desulfurization tower |
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