CN102139935A - Ultraviolet-photochemical compound water purifying process and device capable of realizing synchronous cleaning - Google Patents

Ultraviolet-photochemical compound water purifying process and device capable of realizing synchronous cleaning Download PDF

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CN102139935A
CN102139935A CN2010101028650A CN201010102865A CN102139935A CN 102139935 A CN102139935 A CN 102139935A CN 2010101028650 A CN2010101028650 A CN 2010101028650A CN 201010102865 A CN201010102865 A CN 201010102865A CN 102139935 A CN102139935 A CN 102139935A
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强志民
史彦伟
李梦凯
曲久辉
刘锐平
刘娟
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Research Center for Eco Environmental Sciences of CAS
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Abstract

本发明是关于一种经济高效、运行简便的可同步清洗的紫外-光化学净水处理工艺和反应装置。该工艺包括利用主波长254nm、次波长185nm(10-15%)的紫外灯辐照空气产生臭氧,经射流器形成气水混合物,通过高强磁场强化臭氧自由基化,进入反应器,协同两段波长的紫外线发生光化学自由基链式反应,尾臭氧通过顶部导管利用气压进入集水箱,臭氧氧化和紫外/臭氧光氧化的多级处理达到灭活致病菌和去除微污染物的目的;同时气水混合物经反应器底部切线进入,冲击旋转叶片产生的螺旋上升气水流协同高位穿孔折流板的三维错流作用,冲刷套管表面,防止了生物和物化性附着结垢。该发明方法和反应装置具有很好的净水和同步清洗效果。

Figure 201010102865

The invention relates to an ultraviolet-photochemical water purification treatment process and a reaction device which are economical, efficient and easy to operate and can be cleaned synchronously. The process includes the use of ultraviolet lamps with a main wavelength of 254nm and a secondary wavelength of 185nm (10-15%) to irradiate the air to generate ozone, form a gas-water mixture through a jet, strengthen the free radicalization of ozone through a high-intensity magnetic field, enter the reactor, and coordinate two stages A photochemical free radical chain reaction occurs at the wavelength of ultraviolet rays, and the tail ozone enters the water collection tank through the top duct using air pressure. The multi-stage treatment of ozone oxidation and ultraviolet/ozone photooxidation achieves the purpose of inactivating pathogenic bacteria and removing micro-pollutants; The water mixture enters through the tangent line at the bottom of the reactor, and the spiral rising air and water flow generated by the impact on the rotating blade cooperates with the three-dimensional cross-flow effect of the high-level perforated baffle to scour the surface of the casing, preventing biological and physical and chemical adhesion scaling. The inventive method and reaction device have good water purification and synchronous cleaning effects.

Figure 201010102865

Description

一种可同步清洗的紫外-光化学复合净水工艺和装置A synchronous cleaning UV-photochemical composite water purification process and device

技术领域technical field

本发明涉及一种高效消毒和去除微污染物的工艺和装置,利用单级多波长的紫外线照射空气产生臭氧,并利用磁场强化臭氧自由基化以及臭氧与多段紫外线光化学联合作用的多级物理和光化学作用,达到高效消毒和去除微污染物的目的。利用切线流带动无电动力旋转叶片产生螺旋上升流,并协同多层穿孔折流板的三维错流作用,达到混合水体和同步冲刷清洗紫外套管的作用,强磁场磁化处理也可以改变钙类物质的结晶状态,降低结垢风险,属于饮用水处理技术领域。The invention relates to a process and device for highly efficient disinfection and removal of micro-pollutants. It uses single-stage multi-wavelength ultraviolet rays to irradiate air to generate ozone, and uses a magnetic field to strengthen ozone free radicalization and the multi-stage physical and chemical combination of ozone and multi-stage ultraviolet photochemistry. Photochemical action to achieve efficient disinfection and removal of micro-pollutants. Using tangential flow to drive the non-electric power rotating blades to generate spiral upward flow, and cooperate with the three-dimensional cross-flow effect of multi-layer perforated baffles to achieve the effect of mixing water and synchronously washing and cleaning the ultraviolet sleeve. The strong magnetic field magnetization treatment can also change the calcium The crystalline state of substances reduces the risk of scaling, and belongs to the technical field of drinking water treatment.

背景技术Background technique

当前,利用紫外线杀菌的装置有单级紫外线和二级紫外臭氧联合作用(一级180-200nm紫外产臭氧和二级232-238nm紫外/臭氧联合),后者较前者在处理效果上有一定的提高作用,但臭氧浓度可能过高导致出水异味大,而且没有尾气再利用功能,二级处理能耗也会偏大;现有的紫外线自动清洗方式一般以机械清洗、加化学药剂清洗和两种结合的清洗方法为主,结构复杂,制造和安装不方便,而且能耗成本高,也会引入化学物质,清洗时需要中断水处理。因此,需要一种既能充分利用紫外、臭氧,又能强化臭氧自由基化的工艺,同时兼具同步自动清洗、不需要机械和化学药剂清洗的反应装置。At present, there are single-stage ultraviolet and two-stage ultraviolet-ozone joint effects in ultraviolet sterilization devices (first-stage 180-200nm ultraviolet ozone production and secondary 232-238nm ultraviolet/ozone combination), the latter has a certain degree of treatment effect compared with the former Improve the effect, but the ozone concentration may be too high to cause a strong odor in the effluent, and there is no tail gas reuse function, and the energy consumption of the secondary treatment will be too large; the existing automatic ultraviolet cleaning methods generally use mechanical cleaning, chemical cleaning and two The combined cleaning method is the main method, the structure is complicated, the manufacture and installation are inconvenient, and the energy consumption cost is high, and chemical substances will also be introduced, and the water treatment needs to be interrupted during cleaning. Therefore, there is a need for a process that can not only make full use of ultraviolet light and ozone, but also strengthen the free radicalization of ozone, and simultaneously have synchronous automatic cleaning, and a reaction device that does not require mechanical and chemical cleaning.

发明内容Contents of the invention

本发明提供了一种经济高效、运行简便的饮用水同步清洗和紫外光化学复合净水工艺和装置,该工艺综合单级多段波长紫外产臭氧、磁场强化臭氧自由基化、臭氧与多段紫外线联合光化学反应和尾臭氧自循环的多级作用,提高消毒效果,抑制病原菌光复活的同时氧化降解微污染物;综合在线切流、螺旋流、三维错流和磁场变晶作用来实现同步清洗和降低结垢风险的一体化强化处理。The invention provides an economical, efficient, and easy-to-operate drinking water synchronous cleaning and ultraviolet photochemical composite water purification process and device. The multi-stage effect of reaction and tail ozone self-circulation improves the disinfection effect, inhibits the photoreactivation of pathogenic bacteria and oxidizes and degrades micro-pollutants at the same time; integrates online cutting flow, spiral flow, three-dimensional cross-flow and magnetic field crystallization to realize synchronous cleaning and reduce the result. Integrated and enhanced treatment of scaling risks.

本发明的反应器的构造如附图1和2所示,包括第一级集水箱臭氧氧化装置(7)和第二级紫外-臭氧光化学氧化装置(18)。第一级反应装置内装有曝气砂板(8)和气水混合物循环导管(19),前面连接有流量计(6),与第二级反应装置之间配有提升泵(9)、阀门(10)、射流器(12)、磁化处理器(13)和下部进水口,通过管路相连接,阀门(10)和(11)调节控制一级循环和二级处理水量;第二级反应装置(18)内装有底部螺旋叶 片(14)、上部多套穿孔折流板(15)和石英套管(2),石英套管内装有一支主波长254nm、次波长185nm低压紫外灯管(3)、空气进气管和干燥器(1)、主臭氧导气管(4);在第二级反应装置的上部装有最终出水口和出水调节阀门(16),下部装有排污口和调节阀门(17)。The structure of the reactor of the present invention is shown in Figures 1 and 2, comprising a first-stage water collecting tank ozone oxidation device (7) and a second-stage ultraviolet-ozone photochemical oxidation device (18). The first-stage reaction device is equipped with an aeration sand plate (8) and a gas-water mixture circulation conduit (19), and a flow meter (6) is connected to the front, and a lift pump (9) and a valve ( 10), jet (12), magnetization processor (13) and the lower water inlet are connected through pipelines, and valves (10) and (11) adjust and control the primary circulation and secondary treatment water volume; the secondary reaction device (18) Bottom helical blades (14), upper multiple sets of perforated baffles (15) and quartz casing (2) are housed inside, and a main wavelength 254nm, secondary wavelength 185nm low pressure ultraviolet lamp tube (3 ), air intake pipe and drier (1), main ozone air duct (4); final water outlet and water outlet regulating valve (16) are installed on the top of the second-stage reaction device, and sewage outlet and regulating valve (16) are equipped on the bottom 17).

本发明的反应器系统操作过程如下:Reactor system operating process of the present invention is as follows:

打开阀门10、11和16,开启电源,使紫外灯3和提升泵9开始工作。此时,在射流器的作用下,臭氧气水混合物经过磁处理器进入紫外反应器进行消毒和净水处理;多余的臭氧空气混合尾气由导管5进入集水箱扩散布气。通过调节阀门10和11可以调节控制水的处理量。Open the valves 10, 11 and 16, turn on the power supply, and make the ultraviolet lamp 3 and the lifting pump 9 start to work. At this time, under the action of the ejector, the ozone-water mixture enters the ultraviolet reactor through the magnetic processor for disinfection and water purification treatment; the excess ozone-air mixed tail gas enters the water collection tank through the conduit 5 for diffusion and distribution. By adjusting the valves 10 and 11, the water treatment volume can be adjusted and controlled.

本发明的技术原理为:Technical principle of the present invention is:

紫外/臭氧光化学反应可以产生氧化能力很强的羟基自由基·OH和氧自由基·O;自由基对的单重态向三重态的转化可以防止自由基单重态之间的重结合,外加磁场作用可以加快这种转化,从而加快了臭氧自身以及与UV反应产生羟基自由基·OH的速率,强化自由基氧化反应;套管表面螺旋流态的变化可以降低微生物、钙镁矿物质的附着和结垢风险,由射流器进入反应器的气水混合物沿底部切线进入,通过切线冲击螺旋叶片带动混合物螺旋上升,反应器高位区随着流态横向动能减弱可能变为平流,增设内外孔位交错的多层穿孔折流板(见附图1和2,折流板A型、B型间隔放置,相邻层的孔错位),可以在沿套管表面到反应器表面方向和垂直于这个方向的方向上产生流动,结合上升流动,产生的三维错流可以强化减弱的螺旋流对套管表面的冲刷作用,并且可以使内外水层加速混合,强化紫外线对单位水体的杀菌效果。The UV/ozone photochemical reaction can produce hydroxyl radicals OH and oxygen radicals O with strong oxidizing ability; the conversion of the singlet state of the free radical pair to the triplet state can prevent the recombination between the singlet states of the free radicals, plus The effect of the magnetic field can accelerate this conversion, thereby accelerating the rate of ozone itself and the reaction with UV to produce hydroxyl radicals OH, and strengthening the oxidation reaction of free radicals; the change of the helical flow state on the surface of the casing can reduce the adhesion of microorganisms and calcium and magnesium minerals and fouling risk, the gas-water mixture entering the reactor from the ejector enters along the tangent line at the bottom, and the mixture is driven to spiral upward through the tangential impact on the spiral blade. The high-level area of the reactor may become advection as the lateral kinetic energy of the flow state weakens. Staggered multi-layer perforated baffles (see accompanying drawings 1 and 2, baffles type A and type B are placed at intervals, and the holes of adjacent layers are misplaced), which can be along the direction from the surface of the casing to the surface of the reactor and perpendicular to this Combined with upward flow, the three-dimensional cross-flow generated can strengthen the scouring effect of the weakened spiral flow on the surface of the casing, and can accelerate the mixing of the inner and outer water layers, and strengthen the sterilizing effect of ultraviolet light on the unit water body.

本发明的优点如下:The advantages of the present invention are as follows:

1 采用单级多波长紫外光,同时实现产臭氧和净化水;产生的臭氧利用射流器与处理水混合进入反应器,未利用臭氧通过反应器余压自循环进入前置集水箱,实现单级产臭氧、双级臭氧化的目的;1 Adopt single-stage multi-wavelength ultraviolet light to realize ozone production and water purification at the same time; the generated ozone is mixed with the treated water into the reactor through the jet device, and the unused ozone enters the pre-water collection tank through the reactor residual pressure self-circulation, realizing single-stage The purpose of ozone production and double-stage ozonation;

2 利用高磁场强化臭氧水中自由基化和紫外/臭氧自由基化,强化自由基产生,多级自由基化强化消毒效果和氧化去除微污染物;2 Use high magnetic field to strengthen free radicalization in ozone water and ultraviolet/ozone free radicalization, strengthen free radical generation, multi-level free radicalization strengthen disinfection effect and oxidize and remove micro-pollutants;

3 利用进水气水混合物的动能带动旋转叶片,形成螺旋水流,协同高位区多层穿孔折流板的三维错流,实现同步冲刷的清洗目的,无化学污染物残留;3. Use the kinetic energy of the water-air-water mixture to drive the rotating blades to form a spiral water flow, and cooperate with the three-dimensional cross-flow of the multi-layer perforated baffles in the high-level area to achieve the cleaning purpose of synchronous flushing without residual chemical pollutants;

4 磁场强化自由基化和光催化氧化提高了消毒效果,并可有效防止病原菌的光复活 发生;4. The magnetic field strengthens free radicalization and photocatalytic oxidation to improve the disinfection effect and effectively prevent the photoreactivation of pathogenic bacteria;

5 系统构造简单,占地面积小,可实现连续和自动化运行,操作维护方便。5. The system is simple in structure, small in floor area, can realize continuous and automatic operation, and is easy to operate and maintain.

附图简要说明Brief description of the drawings

图1是本发明的工艺和反应装置运行示意图Fig. 1 is the operation schematic diagram of technique and reaction device of the present invention

图2是本发明反应装置高位区穿孔折流板示意图Fig. 2 is a schematic diagram of perforated baffles in the high position area of the reaction device of the present invention

(其中,1为石英套管壁,2为不锈钢筒壁,3为穿孔)(Wherein, 1 is the quartz casing wall, 2 is the stainless steel cylinder wall, and 3 is perforation)

具体实施方式Detailed ways

以下处理系统中,紫外灯管功率为41W,输出功率14W,输出波长主要为254nm,185nm波长紫外线输出率为10-15%。In the following processing system, the power of the ultraviolet lamp is 41W, the output power is 14W, the output wavelength is mainly 254nm, and the output rate of ultraviolet light with a wavelength of 185nm is 10-15%.

实施例1Example 1

地表水中常含有腐殖质等有机物,可吸收紫外能量降低紫外消毒效果。利用自来水配制含有大肠杆菌和腐植酸的待处理水,其中大肠杆菌总数为1.2×106CFU/L,腐植酸为2mg/L。空气流量为90L/h,臭氧产生量为0.66mg/L(混合气),处理水量为540L/h和900L/min时对大肠杆菌和腐植酸的处理效果见表1,可见处理水量增大近一倍,病原菌灭活率和腐植酸去除率变化较小。Surface water often contains organic matter such as humus, which can absorb ultraviolet energy and reduce the effect of ultraviolet disinfection. Use tap water to prepare water to be treated containing Escherichia coli and humic acid, wherein the total number of Escherichia coli is 1.2×10 6 CFU/L, and the humic acid is 2 mg/L. The air flow rate is 90L/h, the amount of ozone produced is 0.66mg/L (mixed gas), and the treatment effects on Escherichia coli and humic acid are shown in Table 1 when the treated water volume is 540L/h and 900L/min. It can be seen that the treated water volume increases by nearly doubled, the pathogenic bacteria inactivation rate and humic acid removal rate changed little.

表1 实施例1处理效果Table 1 embodiment 1 processing effect

Figure GSA00000009748200031
Figure GSA00000009748200031

实施例2Example 2

进气量的不同导致臭氧产率的不同,光氧化效率的不同导致杀菌效率的不同,致病菌初始浓度对其灭活率也有一定影响。利用自来水配制含有大肠杆菌和腐植酸的待处理水,其中大肠杆菌总数为1.5×106CFU/L,腐植酸为2mg/L。空气流量为120L/h,臭氧产生量为0.82mg/L(混合气),处理水量为540L/h和900L/min,对大肠杆菌和腐植酸的处理效果见表2。结果表明,增大进气量提高了腐植酸去除率;致病菌初始总数增大,但灭活率几乎不受影响。The difference in the amount of air intake leads to the difference in the ozone production rate, the difference in the photooxidation efficiency leads to the difference in the sterilization efficiency, and the initial concentration of pathogenic bacteria also has a certain influence on the inactivation rate. Use tap water to prepare water to be treated containing Escherichia coli and humic acid, wherein the total number of Escherichia coli is 1.5×10 6 CFU/L, and humic acid is 2 mg/L. The air flow rate is 120L/h, the ozone production is 0.82mg/L (mixed gas), and the treated water volume is 540L/h and 900L/min. The treatment effects on Escherichia coli and humic acid are shown in Table 2. The results showed that increasing the air intake increased the humic acid removal rate; the initial total number of pathogenic bacteria increased, but the inactivation rate was almost unaffected.

表2 实施例2处理效果Table 2 embodiment 2 processing effect

实施例3Example 3

由于地表水中存在颗粒物,水的浊度常常会影响紫外线的穿透率和消毒效果。利用自来水配置含有大肠杆菌的待处理水,其中大肠杆菌总数为9.3×105CFU/L,用高岭土调节水的浊度,分别为3NTU和5NTU。空气流量为120L/h,臭氧产生量为0.82mg/L(混合气),处理水量为540L/h,对大肠杆菌的灭活效果见表3。结果表明,常见的地表水浊度在此反应系统中几乎不影响杀菌效率。Due to the presence of particulate matter in surface water, water turbidity often affects UV penetration and disinfection effectiveness. Use tap water to prepare water to be treated containing Escherichia coli, wherein the total number of Escherichia coli is 9.3×10 5 CFU/L, and use kaolin to adjust the turbidity of the water to 3NTU and 5NTU respectively. The air flow rate is 120L/h, the amount of ozone produced is 0.82mg/L (gas mixture), and the treated water volume is 540L/h. The inactivation effect on Escherichia coli is shown in Table 3. The results showed that common surface water turbidity had little influence on the bactericidal efficiency in this reaction system.

表3 实施例3处理效果Table 3 embodiment 3 processing effect

Figure GSA00000009748200042
Figure GSA00000009748200042

实施例4Example 4

由于受到农药的点源和面源污染,地表水中有时会有农药残留,对人体健康造成威胁。利用自来水配制含有莠去津和乐果的待处理水。空气流量为120L/h,臭氧产生量为0.82mg/L(混合气),处理水量为300L/h,对莠去津和乐果的去除效果见表4。结果表明,农药微污染能够在此反应系统中得到高效去除。Due to the point source and non-point source pollution of pesticides, there are sometimes pesticide residues in surface water, which poses a threat to human health. Use tap water to prepare water for treatment containing atrazine and dimethoate. The air flow rate is 120L/h, the amount of ozone produced is 0.82mg/L (gas mixture), and the treated water volume is 300L/h. The removal effects of atrazine and dimethoate are shown in Table 4. The results show that pesticide micro-pollution can be efficiently removed in this reaction system.

表4 实例4处理效果Table 4 Example 4 treatment effect

Figure GSA00000009748200043
Figure GSA00000009748200043

Claims (7)

1.本发明是关于一种经济高效、运行简便的可同步清洗的紫外-光化学净水处理工艺和反应装置。该工艺包括利用主波长254nm、次波长185nm(10-15%)的紫外灯辐照空气产生臭氧,经射流器形成气水混合物,通过高强磁场强化臭氧自由基化进入反应器,协同两段波长的紫外线发生光化学自由基链式反应,尾臭氧通过顶部导管利用气压进入集水箱,臭氧氧化和紫外/臭氧光氧化多级处理达到灭活致病菌和去除微污染物的目的;同时气水混合物经反应器底部切线进入,冲击旋转叶片产生的螺旋上升气水流协同高位穿孔折流板的三维错流作用,冲刷套管表面,防止了生物和物化性附着结垢。该发明方法和装置具有很好的净水和同步清洗效果。1. The present invention relates to a UV-photochemical water purification process and reaction device that is economical, efficient, and easy to operate and can be cleaned synchronously. The process includes the use of ultraviolet lamps with a main wavelength of 254nm and a secondary wavelength of 185nm (10-15%) to irradiate air to generate ozone, form a gas-water mixture through a jet device, and enter the reactor through a high-intensity magnetic field to strengthen ozone free radicals, and cooperate with two wavelengths The ultraviolet rays undergo a photochemical free radical chain reaction, and the tail ozone enters the water collection tank through the top conduit using air pressure, and the multi-stage treatment of ozone oxidation and ultraviolet/ozone photooxidation achieves the purpose of inactivating pathogenic bacteria and removing micro-pollutants; at the same time, the gas-water mixture Entering through the tangent line at the bottom of the reactor, the spiral rising gas-water flow generated by impacting the rotating blade cooperates with the three-dimensional cross-flow effect of the high-level perforated baffle to scour the surface of the casing, preventing biological and physical and chemical adhesion scaling. The inventive method and device have good water purification and synchronous cleaning effects. 2.按照权利要求1所述的方法,其中,磁化处理器为高磁场处理器,其磁场强度高于5000GS,用于改变钙盐的结晶结构和强化臭氧自由基化。2. according to the described method of claim 1, wherein, magnetization processor is high magnetic field processor, and its magnetic field strength is higher than 5000GS, is used for changing the crystalline structure of calcium salt and strengthening ozone free radicalization. 3.按照权利要求1所述的方法,其中,紫外灯为主波长为254nm、次波长185nm(10-15%)的高臭氧低压紫外灯。3. according to the described method of claim 1, wherein, ultraviolet lamp main wavelength is the high ozone low pressure ultraviolet lamp of 254nm, secondary wavelength 185nm (10-15%). 4.一种可同步清洗的紫外-光化学净水装置,其特征在于,它包括第一级集水箱臭氧氧化装置(7)和第二级紫外-臭氧光化学氧化装置(18),第一级反应装置内装有曝气砂板(8)和气水混合物循环导管(19);第一级反应装装置前连接有流量计(6),与第二级反应装置之间配有提升泵(9)、阀门(10)、射流器(12)、磁化处理器(13)和下部进水口,通过管路相连接,阀门(10)和(11)调节控制一级循环和二级处理水量;第二级反应装置(18)内装有底部螺旋叶片(14)、上部多套穿孔折流板(15)和石英套管(2),石英套管内装有一支主波长254nm、次波长185nm低压紫外灯管(3)、空气进气管和干燥器(1)、主臭氧导气管(4);在第二级反应装置的上部装有最终出水口和出水调节阀门(16),下部装有排污口和调节阀门(17)。4. A UV-photochemical water purification device that can be cleaned synchronously is characterized in that it includes a first-stage water collecting tank ozone oxidation device (7) and a second-stage UV-ozone photochemical oxidation device (18), and the first-stage reaction The device is equipped with an aeration sand plate (8) and a gas-water mixture circulation conduit (19); a flow meter (6) is connected in front of the first-stage reaction device, and a lift pump (9), The valve (10), jet (12), magnetization processor (13) and the lower water inlet are connected by pipelines, and the valves (10) and (11) adjust and control the first-stage circulation and the second-stage treatment water volume; the second-stage The reaction device (18) is equipped with a bottom helical blade (14), multiple sets of perforated baffles (15) and a quartz casing (2), and a low-voltage ultraviolet lamp with a main wavelength of 254nm and a secondary wavelength of 185nm is installed in the quartz casing ( 3), air inlet pipe and dryer (1), main ozone air duct (4); the final water outlet and water outlet regulating valve (16) are installed on the upper part of the second-stage reaction device, and the sewage outlet and regulating valve are installed on the lower part (17). 5.根据权利要求4所述的反应器,其特征在于,第二级反应器中的底部螺旋叶片(14)为无电动力旋转、利用底部进水和气流的切线冲击旋转搅动水流螺旋上升。5. The reactor according to claim 4, characterized in that, the bottom helical blade (14) in the second-stage reactor rotates without electric power, and utilizes the tangential impact rotation of the bottom water and airflow to stir the water flow to spiral up. 6.根据权利要求4所述的反应器,其特征在于,第二级反应器上部增设的多层穿孔折流板(15)分别为近套管内环穿孔和远套管外环穿孔,并且孔与孔错位布置,实现三维错流,达到内外混合和冲刷套管的目的。6. The reactor according to claim 4, characterized in that, the multi-layer perforated baffles (15) added on the top of the second-stage reactor are respectively perforated near the inner ring of the casing and the outer ring of the far casing, and the holes Displaced arrangement with the holes to achieve three-dimensional cross-flow, to achieve the purpose of mixing inside and outside and flushing the casing. 7.根据权利要求4所述的反应器,其特征在于:在第二级反应装置的顶空部分还安装有尾臭氧导气管(5),用于引导未反应的臭氧进入一级反应装置内参与自循环反应。7. The reactor according to claim 4, characterized in that: the headspace part of the second-stage reaction device is also equipped with a tail ozone air duct (5), which is used to guide unreacted ozone into the first-stage reaction device Participate in self-circulation reactions.
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