CN115893638A - Multi-stage spiral symmetrical ozone oxidation device - Google Patents
Multi-stage spiral symmetrical ozone oxidation device Download PDFInfo
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Abstract
本发明公开了废水处理领域内的一种多级螺旋对称式臭氧氧化装置,包括:罐体,分为一级反应区和二级反应区,一级臭氧曝气头,设置在一级反应区的底部;一级进水管,从不锈钢罐体的两侧沿切线方向伸入罐体内;二级臭氧曝气头,设置在二级反应区的底部;二级进水管,从不锈钢罐体的两侧沿切线方向伸入罐体内;出水管,分两路,一路接出水口、另一路回流接二级进水管;排气管,一路接出气口、另一路回流接二级臭氧曝气头;筛板,设置有四块,其中两块设置在一级反应区,另两块设置在二级反应区内;催化填料,设置在一级反应区和二级反应区内的两块筛板之间,本发明解决现有技术中臭氧利用率低、气液传质效果差的问题,提升催化反应效率。
The invention discloses a multi-stage spiral symmetrical ozone oxidation device in the field of wastewater treatment, comprising: a tank body, which is divided into a primary reaction zone and a secondary reaction zone, and a primary ozone aeration head, which is arranged in the primary reaction zone the bottom of the bottom; the primary water inlet pipe extends into the tank from both sides of the stainless steel tank along the tangential direction; the secondary ozone aeration head is set at the bottom of the secondary reaction zone; the secondary water inlet pipe extends from the two sides of the stainless steel tank The side extends into the tank along the tangential direction; the outlet pipe is divided into two routes, one is connected to the water outlet, and the other is connected to the secondary water inlet pipe; the exhaust pipe is connected to the air outlet, and the other is connected to the secondary ozone aeration head; There are four sieve plates, two of which are set in the primary reaction zone and the other two are set in the secondary reaction zone; catalytic packing is set between the two sieve plates in the primary reaction zone and the secondary reaction zone In the meantime, the invention solves the problems of low ozone utilization rate and poor gas-liquid mass transfer effect in the prior art, and improves the catalytic reaction efficiency.
Description
技术领域technical field
-本发明涉及废水处理领域,特别涉及一种废水臭氧氧化处理装置。- The present invention relates to the field of wastewater treatment, in particular to a wastewater ozone oxidation treatment device.
背景技术Background technique
随着工业的迅速发展,工业废水的排放量日益增多,成分更加复杂,水中含有许多较难降解的有机物,如酚类化合物,多环芳烃类化合物,杂环类化合物,多氯联苯等化合物,造成天然水体污染的加剧,严重威胁人民的健康,并且制约社会经济和科技的发展。这些工业废水包括制药废水,煤化工废水,制浆废水,炼油废水等,具有生物毒性大,含有抑菌物质和较低可生化性等特点,造成传统的生物处理法的失活,因此急需开发新型的水处理技术。With the rapid development of industry, the discharge of industrial wastewater is increasing, and the composition is more complex. The water contains many organic compounds that are difficult to degrade, such as phenolic compounds, polycyclic aromatic hydrocarbons, heterocyclic compounds, polychlorinated biphenyls and other compounds. , causing aggravation of natural water pollution, seriously threatening people's health, and restricting the development of social economy and science and technology. These industrial wastewaters include pharmaceutical wastewater, coal chemical wastewater, pulping wastewater, oil refining wastewater, etc., which have the characteristics of high biological toxicity, bacteriostatic substances and low biodegradability, which cause the inactivation of traditional biological treatment methods, so they are in urgent need of development. New water treatment technology.
现有的废水深度处理技术主要有活性炭吸附、Fenton(芬顿)氧化、电催化氧化以及膜分离技术等,但都存在不同程度的应用瓶颈。活性炭吸附工艺运行费用较高,容易吸附饱和且不易解吸,并且在使用后很容易被鉴定成危废; Fenton氧化技术处理效果不稳定,且铁泥量大;电催化氧化技术一次性投资较大、极板消耗较快,且运行费用高;膜分离技术投资较大、运行成本高,并且产生的膜法浓水难处理,同样存在较大缺陷。The existing wastewater advanced treatment technologies mainly include activated carbon adsorption, Fenton oxidation, electrocatalytic oxidation, and membrane separation technology, but all of them have application bottlenecks to varying degrees. The operating cost of the activated carbon adsorption process is high, it is easy to absorb saturation and difficult to desorb, and it is easy to be identified as hazardous waste after use; the treatment effect of the Fenton oxidation technology is unstable, and the amount of iron sludge is large; the one-time investment of the electrocatalytic oxidation technology is relatively large 1. Plate consumption is fast, and the operating cost is high; membrane separation technology has a large investment, high operating cost, and the membrane concentrated water produced is difficult to treat, and there are also major defects.
臭氧催化氧化技术是一种高效的废水深度处理技术,与其它深度处理技术相比,臭氧催化氧化技术应用较为成熟,处理效果较好。臭氧以其氧化能力强(仅次于氟,·OH),反应速度快,不产生污泥和二次污染,能够提高水的可生化性等优点,在废水处理方面的应用越来越受重视。Ozone catalytic oxidation technology is an efficient wastewater advanced treatment technology. Compared with other advanced treatment technologies, ozone catalytic oxidation technology is more mature in application and has better treatment effect. Ozone has the advantages of strong oxidation ability (second only to fluorine, OH), fast reaction speed, no sludge and secondary pollution, and the ability to improve the biodegradability of water. The application of ozone in wastewater treatment has attracted more and more attention. .
臭氧催化氧化技术在广泛应用的同时,也存在着一定程度的缺陷和不足。比如,现有臭氧催化氧化装置普遍存在着臭氧利用率低以及气液传质效果差的现象。因此,有必要对现有臭氧催化氧化装置进行优化,从而提升催化反应效率,强化处理效果。While ozone catalytic oxidation technology is widely used, it also has some defects and deficiencies. For example, existing ozone catalytic oxidation devices generally have the phenomenon of low ozone utilization rate and poor gas-liquid mass transfer effect. Therefore, it is necessary to optimize the existing ozone catalytic oxidation device, so as to improve the catalytic reaction efficiency and strengthen the treatment effect.
发明内容Contents of the invention
针对现有技术中存在的不足,本发明提供了一种多级螺旋对称式臭氧氧化装置,解决现有技术中臭氧利用率低、气液传质效果差的问题,提升催化反应效率,增强废水处理效果。Aiming at the deficiencies in the prior art, the present invention provides a multi-stage spiral symmetric ozone oxidation device, which solves the problems of low ozone utilization rate and poor gas-liquid mass transfer effect in the prior art, improves the catalytic reaction efficiency, and enhances the efficiency of wastewater treatment. processing effect.
本发明的目的是这样实现的:一种多级螺旋对称式臭氧氧化装置,包括:The object of the present invention is achieved in that a kind of multi-stage spiral symmetrical ozonation device comprises:
不锈钢罐体,作为反应主体,内部分为一级反应区和二级反应区,一级反应区设置在二级反应区的下方,底部固定有承重支架;The stainless steel tank, as the main body of the reaction, is divided into a primary reaction area and a secondary reaction area. The primary reaction area is set below the secondary reaction area, and the bottom is fixed with a load-bearing bracket;
一级臭氧曝气头,设置在一级反应区的底部;The primary ozone aeration head is set at the bottom of the primary reaction zone;
一级进水管,设置有两根,从不锈钢罐体的两侧沿切线方向伸入罐体内;There are two first-level water inlet pipes, which extend into the tank from both sides of the stainless steel tank along the tangential direction;
二级臭氧曝气头,设置在二级反应区的底部;The secondary ozone aeration head is set at the bottom of the secondary reaction zone;
二级进水管,设置有两根,从不锈钢罐体的两侧沿切线方向伸入罐体内;There are two secondary water inlet pipes, which extend into the tank from both sides of the stainless steel tank along the tangential direction;
出水管,设置有两根,连接在罐体顶部,分两路,一路接出水口、另一路回流接二级进水管;There are two outlet pipes, which are connected to the top of the tank and divided into two routes, one is connected to the water outlet, and the other is connected to the secondary water inlet pipe for return flow;
排气管,分两路,一路接出气口、另一路回流接二级臭氧曝气头;The exhaust pipe is divided into two paths, one path is connected to the air outlet, and the other path is connected to the secondary ozone aeration head for return flow;
筛板,设置有四块,其中两块设置在一级反应区,另两块设置在二级反应区内;There are four sieve plates, two of which are set in the primary reaction zone, and the other two are set in the secondary reaction zone;
催化填料,设置在一级反应区和二级反应区内的两块筛板之间。The catalytic packing is arranged between the two sieve plates in the primary reaction zone and the secondary reaction zone.
本发明的工作原理为:Working principle of the present invention is:
废水由两根进水管送入罐体内,由于切线关系,进入管道内的废水会在罐体中形成旋流,随着不断地进水反应器内液面不断抬高,使整个反应区内的废水成螺旋状态流动上升;同时从一级臭氧曝气头通入臭氧,在筛板的作用下均匀上升,在一级反应区内实现臭氧、催化填料以及废水充分搅动混合,碰撞接触;随着液位的上升,废水进入二级反应区,同理再次进行反应,与一级反应区不同是,二级反应区内会有一部分臭氧和废水通过出水管、排气管回流再次循环反应。The waste water is sent into the tank by two water inlet pipes. Due to the tangential relationship, the waste water entering the pipes will form a swirling flow in the tank. Wastewater flows up in a spiral state; at the same time, ozone is introduced from the first-level ozone aeration head, and it rises evenly under the action of the sieve plate, and the ozone, catalytic filler and wastewater are fully stirred and mixed in the first-level reaction zone, and collide with each other; As the liquid level rises, the wastewater enters the secondary reaction zone, and reacts again in the same way. Unlike the primary reaction zone, part of the ozone and wastewater in the secondary reaction zone will flow back through the outlet pipe and exhaust pipe to recirculate and react again.
本发明通过两进水管切线方向进水,如此废水在罐体产生旋流,使得臭氧和催化填料在搅动过程中充分接触,可有效解决现有反应存在死角区的问题,进一步解决臭氧利用率低、气液传质效果差的问题;同时,如此结构省去了外力搅拌,简化了结构。The invention feeds water through two water inlet pipes in a tangential direction, so that the waste water generates a swirling flow in the tank body, so that the ozone and the catalytic filler are fully contacted during the agitation process, which can effectively solve the problem of dead zone in the existing reaction, and further solve the problem of low utilization rate of ozone , The problem of poor gas-liquid mass transfer effect; at the same time, such a structure saves external stirring and simplifies the structure.
本发明通过设计的隔板将催化填料限制的一定的区域内,解决了现有填料容易被冲走的问题,同时,还起到降低水体悬动速度,保证在一定的区域内水体与臭氧、催化填料的接触时长,实现充分反应,进一步解决臭氧利用率低、气液传质效果差的问题。The present invention limits the catalytic filler to a certain area through the designed partition, which solves the problem that the existing filler is easily washed away. At the same time, it also reduces the suspension speed of the water body and ensures that the water body and ozone, The contact time of the catalytic packing is long to achieve full reaction, further solving the problems of low ozone utilization rate and poor gas-liquid mass transfer effect.
本发明设计成的两级反应区域,其中一级反应区作为主反应区,可氧化降解污水中大部分的有机污染物;二级反应区作为循环反应区,罐体排出的剩余臭氧和处理后的水部分回送至二级反应区,延长了废水与臭氧、催化填料的接触时间,从而解决现有臭氧利用率低、气液传质效果差的问题;The two-stage reaction area designed by the present invention, wherein the first-stage reaction area is used as the main reaction area, can oxidize and degrade most of the organic pollutants in the sewage; Part of the water is sent back to the secondary reaction zone, which prolongs the contact time between wastewater, ozone and catalytic packing, thereby solving the existing problems of low ozone utilization rate and poor gas-liquid mass transfer effect;
与现有技术相比,本发明的有益效果在于:Compared with prior art, the beneficial effect of the present invention is:
本发明通过设计使废水斜对角平行进入罐内,可以在处理区内迅速形成旋转的流体,并搅动填料,使臭氧、废水、催化填料充分接触,相比于传统的侧向流进水方式,可以更加有效地减少装置内的死角,并提高臭氧、废水、催化填料的接触时间和接触面积,提高系统的催化氧化效率,无需其他搅拌设备,节约能源;The invention makes the waste water enter into the tank obliquely and parallel by design, and can quickly form a rotating fluid in the treatment area, and stir the packing, so that ozone, waste water, and catalytic packing are fully contacted, compared with the traditional side flow water inlet method , can more effectively reduce the dead angle in the device, and increase the contact time and contact area of ozone, wastewater, and catalytic fillers, improve the catalytic oxidation efficiency of the system, and save energy without other stirring equipment;
本发明设计二级循环处理系统,通过对排出水、气部分回流至循环反应区,进一步氧化污水中的有机污染物,并提高臭氧的利用效率。The invention designs a secondary circulation treatment system, and through returning the discharged water and gas to the circulation reaction zone, the organic pollutants in the sewage are further oxidized, and the utilization efficiency of ozone is improved.
作为本发明的进一步改进,所述催化填料采用铝硅复合材料制成,且催化填料为多面体空心球结构。首先,铝硅符合材料具有更好的催化效果,且机械强度高,不良环境耐性作用强,其次,多面体空心球结构由于其具备多个叶片,比表面积大,增强增大了催化剂与废水、臭氧的接触面积,进一步解决臭氧利用率低的问题,提升臭氧与废水的接触效率;另外,传统活性炭球形结构内部气体流速相对较低,采用中空的多面体空心球结构加快了臭氧流速,提升交换效率。As a further improvement of the present invention, the catalytic filler is made of aluminum-silicon composite material, and the catalytic filler is a polyhedral hollow sphere structure. First of all, aluminum-silicon composite materials have better catalytic effect, high mechanical strength, and strong resistance to adverse environments. Secondly, the polyhedral hollow sphere structure has multiple blades and a large specific surface area, which enhances the catalyst and wastewater, ozone. The contact area is large, which further solves the problem of low ozone utilization rate and improves the contact efficiency of ozone and wastewater; in addition, the gas flow rate inside the traditional spherical structure of activated carbon is relatively low, and the hollow polyhedral hollow sphere structure is used to speed up the ozone flow rate and improve the exchange efficiency.
作为本发明的进一步改进,所述催化填料的中心设有空心球囊,一级反应区中上部的筛板和二级反应区中上部的筛板均加工为球面结构。在实际应用过程中,由于催化填料采用铝硅复合材料,其密度略大于废水密度,在水体旋转过程中,由于传统的臭氧催化填料相对分布在罐体内靠近内壁的区域内,从而导致中心区域的废水不能与填料充分接触,并造成催化材料不能与臭氧气体充分进行催化反应等一系列问题。本发明通过在多面体空心球结构的中心设置空心球囊,增强了催化填料的浮力,使得催化填料可聚集在反应区顶部,与此同时,通过将反应区上部的筛板加工成弧形球面结构,在浮力增强的作用下,一部分催化填料会滑向筛板中央,使得催化填料的分布更加均匀,从而解决现有催化填料分布不均匀的问题,保证了反应区域的废水与填料的充分接触,使得反应更加充分。As a further improvement of the present invention, the center of the catalytic packing is provided with a hollow balloon, and the sieve plate in the middle and upper part of the primary reaction zone and the sieve plate in the middle and upper part of the secondary reaction zone are both processed into a spherical structure. In the actual application process, since the catalytic filler is made of aluminum-silicon composite material, its density is slightly greater than that of wastewater. During the rotation of the water body, the traditional ozone catalytic filler is relatively distributed in the area near the inner wall of the tank, resulting in the central area. The waste water cannot fully contact with the filler, which causes a series of problems such as the inability of the catalytic material to fully catalyze the reaction with the ozone gas. The present invention enhances the buoyancy of the catalytic packing by arranging a hollow balloon at the center of the polyhedral hollow sphere structure, so that the catalytic packing can gather at the top of the reaction zone, and at the same time, process the sieve plate at the upper part of the reaction zone into an arc-shaped spherical structure , under the effect of enhanced buoyancy, a part of the catalytic packing will slide to the center of the sieve plate, making the distribution of the catalytic packing more uniform, thereby solving the problem of uneven distribution of the existing catalytic packing and ensuring full contact between the wastewater in the reaction area and the packing. make the response more adequate.
作为本发明的进一步改进,所述第一筛板、第二筛板、第三筛板、第四筛板上加工有若干菱形通孔。菱形通孔冲压制成工艺简单,且机械强度较高。As a further improvement of the present invention, several diamond-shaped through holes are processed on the first sieve plate, the second sieve plate, the third sieve plate and the fourth sieve plate. The diamond-shaped through hole punching process is simple, and the mechanical strength is high.
作为本发明的进一步改进,所述一级进水管、二级进水管、一级臭氧曝气头、二级臭氧曝气头的入口均设有加压装置。通过设计加压装置可增强流速,保证反应效果。As a further improvement of the present invention, the inlets of the primary water inlet pipe, the secondary water inlet pipe, the primary ozone aeration head, and the secondary ozone aeration head are all provided with pressurizing devices. By designing the pressurization device, the flow rate can be enhanced to ensure the reaction effect.
作为本发明的进一步改进,所述排气管的入口处设有二相分离器。二相分离器的设计可有助于臭氧的排出、循环。As a further improvement of the present invention, a two-phase separator is provided at the inlet of the exhaust pipe. The design of the two-phase separator can help the discharge and circulation of ozone.
附图说明Description of drawings
为了更清楚地说明本发明实施例或现有技术中的技术方案,下面将对实施例或现有技术描述中所需要使用的附图作简单地介绍,显而易见地,下面描述中的附图仅仅是本发明的实施例,对于本领域普通技术人员来讲,在不付出创造性劳动的前提下,还可以根据提供的附图获得其他的附图。In order to more clearly illustrate the technical solutions in the embodiments of the present invention or the prior art, the following will briefly introduce the drawings that need to be used in the description of the embodiments or the prior art. Obviously, the accompanying drawings in the following description are only It is an embodiment of the present invention, and those skilled in the art can also obtain other drawings according to the provided drawings without creative work.
图1为本发明结构示意图。Fig. 1 is a schematic diagram of the structure of the present invention.
图2为沿图1中A-A向剖视图。Fig. 2 is a sectional view along the line A-A in Fig. 1 .
图3为沿图1中B-B向剖视图。Fig. 3 is a sectional view along the direction B-B in Fig. 1 .
图4为本发明中催化填料结构示意图。Fig. 4 is a schematic diagram of the structure of the catalytic packing in the present invention.
其中,1罐体,1a一级反应区,1b二级反应区,2承重支架,3一级臭氧曝气头,4一级进水管,5二级臭氧曝气头,6二级进水管,7出水管,8排气管,9筛板,10催化填料,11球囊,12二相分离器。Among them, 1 tank, 1a primary reaction zone, 1b secondary reaction zone, 2 load-bearing brackets, 3 primary ozone aeration head, 4 primary water inlet pipe, 5 secondary ozone aeration head, 6 secondary water inlet pipe, 7 outlet pipe, 8 exhaust pipe, 9 sieve plate, 10 catalytic packing, 11 balloon, 12 two-phase separator.
具体实施方式Detailed ways
下面将结合本发明实施例中的附图,对本发明实施例中的技术方案进行清楚、完整地描述,显然,所描述的实施例仅仅是本发明一部分实施例,而不是全部的实施例。基于本发明中的实施例,本领域普通技术人员在没有做出创造性劳动前提下所获得的所有其他实施例,都属于本发明保护的范围。The following will clearly and completely describe the technical solutions in the embodiments of the present invention with reference to the accompanying drawings in the embodiments of the present invention. Obviously, the described embodiments are only some, not all, embodiments of the present invention. Based on the embodiments of the present invention, all other embodiments obtained by persons of ordinary skill in the art without making creative efforts belong to the protection scope of the present invention.
实施例1Example 1
如图1-4所示的一种多级螺旋对称式臭氧氧化装置,包括:A kind of multi-stage spiral symmetrical ozonation device as shown in Figure 1-4, comprises:
不锈钢罐体1,作为反应主体,内部分为一级反应区1a和二级反应区1b,一级反应区1a设置在二级反应区1b的下方,底部固定有承重支架2,通过承重支架2固定在地面;The stainless steel tank 1, as the main body of the reaction, is internally divided into a primary reaction zone 1a and a secondary reaction zone 1b, the primary reaction zone 1a is set below the secondary reaction zone 1b, and a load-
一级反应区1a由两块隔板围成,下一块隔板的下方设置有一级臭氧曝气头3,一级曝气头接外部臭氧气源,同时配合气泵增压,下一块隔板的上方设置有一级进水管4,一级进水管4设置有两根,从不锈钢罐体1的两侧沿切线方向伸入罐体1内,一级进水管4的入口设有水泵、并接废水源;The first-stage reaction zone 1a is surrounded by two partitions, and the bottom of the next partition is provided with a first-stage
二级反应区1b也由两块隔板围成,下一块隔板的下方设置有二级臭氧曝气头5,二级曝气头旁接在排气管8上,同时配合气泵增压,下一块隔板的上方设置有二级进水管6,二级进水管6设置有两根,从不锈钢罐体1的两侧沿切线方向伸入罐体1内,二级进水管6旁接在出水管7上;The secondary reaction zone 1b is also surrounded by two partitions. A secondary ozone aeration head 5 is arranged under the next partition, and the secondary aeration head is connected to the
排气管8从罐体1顶部伸入,排气管8的入口处设有二相分离器12,分两路,一路接出气口、另一路回流接二级臭氧曝气头5;The
催化填料10,设置在一级反应区1a和二级反应区1b内的两块筛板9之间,催化填料10采用铝硅复合材料制成,且催化填料10为多面体空心球结构,催化填料10的中心设有空心球囊11,一级反应区1a中上部的筛板9和二级反应区1b中上部的筛板9均加工为球面结构。The
本实施例中,罐体1采用316L不锈钢材质,厚度为3-5mm,增强抗氧化和腐蚀能力,底部焊接承重支架2保持装置平稳。In this embodiment, the tank body 1 is made of 316L stainless steel with a thickness of 3-5mm, which enhances the anti-oxidation and corrosion resistance, and the load-
臭氧通过臭氧发生器以0.8-1.2MPa压力进入装置内,并通过筛板9进入一级反应区1a;筛板9为菱形孔,孔眼大小为8-12mm;废水通过水泵增压,随管道斜对角平行进入处理区。Ozone enters the device through the ozone generator at a pressure of 0.8-1.2MPa, and enters the primary reaction zone 1a through the
工作时,通过水泵增压进入管道内的废水会在装置中形成旋流,随着不断地进水反应器内液面不断抬高,使整个反应区内的废水成螺旋状态流动上升,可以使反应区内的臭氧、催化填料10以及废水充分搅动混合,碰撞接触。When working, the waste water that enters the pipeline through the pressurization of the water pump will form a swirling flow in the device. With the continuous increase of the liquid level in the reactor, the waste water in the entire reaction zone will flow upward in a spiral state, which can make The ozone,
臭氧催化剂填料采用铝硅复合材料,复合材料载体进一步加强了载体强度,磨损消耗低,机械强度高,催化剂载体高强度实现了催化组分不流失,不更换,长期运行稳定高效,形状为空心多面空心球形,直径为25mm,具有气速高,叶片多,阻力小,比表面积大等优点。The ozone catalyst filler is made of aluminum-silicon composite material. The composite material carrier further enhances the carrier strength, low wear consumption, high mechanical strength, and the high strength of the catalyst carrier realizes that the catalytic components are not lost or replaced, and the long-term operation is stable and efficient. The shape is hollow and multi-faceted Hollow spherical shape with a diameter of 25mm has the advantages of high gas velocity, many blades, small resistance, and large specific surface area.
在一级反应区1a内,臭氧和催化填料10在水流搅动过程中充分接触,并迅速与污水中的有机污染物发生氧化反应,使水中有机污染物的浓度降低,从而达到废水深度处理的效果。可以有效的解决装置内的死角区,并减小水头损失;同时,直接用提升泵从底部增压注水,可以无需机械外力搅拌,简化装置。In the primary reaction zone 1a, the ozone and the catalytic packing 10 fully contact during the agitation process of the water flow, and quickly oxidize the organic pollutants in the sewage, reducing the concentration of organic pollutants in the water, thereby achieving the effect of advanced wastewater treatment . It can effectively solve the dead angle area in the device and reduce the loss of water head; at the same time, the lift pump is directly used to pressurize and inject water from the bottom, which can simplify the device without mechanical external force stirring.
通过筛板9分隔催化填料10,并防止催化填料10被水流冲走。装置内部分为一级反应区1a和二级反应区1b,并通过挡流板和筛板9降低水体旋动速度,在装置顶部设计二相分离器12,处理后的污水通过溢流堰排至出水管7道,一部分进行后续生化处理,一部分则继续通过水泵增压进入二级反应区1b;未利用的臭氧尾气通过二相分离器12汇集,一部分尾气通过臭氧破坏器后无污染排放,另一部分增压后进入二级反应区1b进行曝气,提高臭氧的利用效率。二级反应区1b采用螺旋对称布水方式,使臭氧、催化填料10和废水充分接触,提高了系统的处理效率。The
臭氧氧化装置分一级反应区1a,可氧化降解污水中大部分的有机污染物;二级反应区1b,装置排出的剩余臭氧和处理后的水部分加压回送至二级反应区1b,进一步提高了废水中有机污染物的处理效率,并增加了臭氧的利用效率。一级反应区1a和二级反应区1b均采用螺旋对称布水方式,可以有效促进臭氧、废水和催化填料10直接的接触时间,提高臭氧的氧化效率。The ozone oxidation device is divided into the primary reaction zone 1a, which can oxidize and degrade most of the organic pollutants in the sewage; the secondary reaction zone 1b, the remaining ozone discharged from the device and the treated water part are returned to the secondary reaction zone 1b under pressure, and further The treatment efficiency of organic pollutants in wastewater is improved, and the utilization efficiency of ozone is increased. Both the primary reaction zone 1a and the secondary reaction zone 1b adopt a spiral symmetrical water distribution method, which can effectively promote the direct contact time of ozone, waste water and catalytic packing 10, and improve the oxidation efficiency of ozone.
反应后的气体和废水通过进入二级反应区1b内继续进行氧化,旋流水体经挡流板和筛板9流速变慢后通过二相分离器12进行气液分离。废水通过溢流堰,一部分至出水回流管道加压后进入二级反应区1b,一部分则通过废水出水管7排放,剩余臭氧经臭氧收集管道汇集后,一部分通过循环进入二级反应区1b进入再曝气,一部分臭氧则通过排气管8排出,经臭氧破坏器处理后安全排放。After the reaction, the gas and waste water enter the secondary reaction zone 1b to continue to be oxidized, and the swirling water passes through the baffle plate and the
实施例2:Example 2:
本实施例提供上述多级螺旋对称式臭氧氧化装置在污水处理中应用的实际实验例:This embodiment provides an actual experimental example of the application of the above-mentioned multi-stage spiral symmetrical ozonation device in sewage treatment:
山东临邑某炼油厂的污水处理工艺:在沉淀池后设计臭氧深度处理装置,废水经臭氧氧化后,出水送至二级生化池进行生物处理。经处理后达标排放。改炼油厂污水经原工艺处理后,出水COD浓度在100mg/L左右,现要求出水达到50mg/L以下方可排放,因此需要进行深度处理。经过臭氧深度处理后,其进出水效果,60天内进水COD浓度为92-120mg/L,平均浓度为105.6mg/L,出水COD浓度为28-46mg/L,平均浓度为36.67mg/L。经过臭氧氧化处理后,污水处理工艺的最终出水COD浓度低于50mg/L的排放标准。Sewage treatment process of an oil refinery in Linyi, Shandong: After the sedimentation tank, an ozone advanced treatment device is designed. After the wastewater is oxidized by ozone, the effluent is sent to the secondary biochemical tank for biological treatment. Discharge up to standard after treatment. After the refinery sewage is treated by the original process, the COD concentration of the effluent is about 100mg/L. Now it is required that the effluent can be discharged below 50mg/L, so advanced treatment is required. After advanced ozone treatment, the influent and effluent effect, within 60 days, the influent COD concentration is 92-120mg/L, with an average concentration of 105.6mg/L, and the effluent COD concentration is 28-46mg/L, with an average concentration of 36.67mg/L. After ozone oxidation treatment, the COD concentration of the final effluent of the sewage treatment process is lower than the discharge standard of 50mg/L.
以上实施例的说明只是用于帮助理解本发明的方法及其核心思想。应当指出,对于本技术领域的普通技术人员来说,在不脱离本发明原理的前提下,还可以对本发明进行若干改进和修饰,这些改进和修饰也落入本发明权利要求的保护范围内。The descriptions of the above embodiments are only used to help understand the method and core idea of the present invention. It should be pointed out that for those skilled in the art, without departing from the principle of the present invention, some improvements and modifications can be made to the present invention, and these improvements and modifications also fall within the protection scope of the claims of the present invention.
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