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CN102276081A - Process for treating industrial organic waste water by serial catalytic oxidization - Google Patents

Process for treating industrial organic waste water by serial catalytic oxidization Download PDF

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CN102276081A
CN102276081A CN2011101385084A CN201110138508A CN102276081A CN 102276081 A CN102276081 A CN 102276081A CN 2011101385084 A CN2011101385084 A CN 2011101385084A CN 201110138508 A CN201110138508 A CN 201110138508A CN 102276081 A CN102276081 A CN 102276081A
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catalytic oxidation
wastewater
ozone
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夏东升
曾庆福
杨俊�
阮新潮
杨小俊
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Wuhan Textile University
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Abstract

The invention relates to a process for treating industrial organic waste water by serial catalytic oxidization and belongs to the technical field of environment protection. The process for treating industrial organic waste water by serial catalytic oxidization realizes the quick treatment of complex organic pollutants in pretreated industrial waste water by coordination between oxidizers in a mode of serially connecting and coordinating catalytic oxidization by ozone and catalytic oxidization by hydrogen peroxide. In the first catalytic oxidization process, a large amount of free radicals are formed by catalytic oxidization by ozone, so that organic matters in waste water are oxidized and decomposed; and the rest ozone and organic pollutants enter the second hydrogen peroxide catalytic decomposition process, so that the organic matters are decomposed, the degradation action and coordinated reaction of the hydrogen peroxide and ozone are activated and the organic pollutants are degraded quickly. The process for treating industrial organic waste water by serial catalytic oxidization not only improves the processing capacity of nondegradable organic pollutants, but also improves the utilization rate of oxidizers and effectively reduces operation cost.

Description

一种串联催化氧化处理工业有机废水工艺A series catalytic oxidation process for industrial organic wastewater treatment

技术领域 technical field

本发明涉及一种串联催化氧化处理工业有机废水工艺,属于环境保护技术领域。The invention relates to a series catalytic oxidation process for treating industrial organic wastewater, which belongs to the technical field of environmental protection.

背景技术 Background technique

工业园区的废水是较难处理的废水,其来源成分复杂,其中的有机污染物常为难生物降解有机物,处理难度大。这部分的COD常大于2000mg/L,带有苯环结构,性质稳定的有机污染物占有比例较大,因此增加了处理的难度。目前,工业园区废水采用单一氧化剂处理方法:H2O2的催化氧化法或者O3催化氧化法,将废水中的有机物氧化分解为小分子有机物或CO2和H2O,从而去除废水中的有机污染物。传统的化学氧化法仅靠氧化剂的氧化能力往往不能达到理想的氧化效果,所以使用一些辅助手段以提高氧化效率。出现了UV/O3、UV/H2O2、Fenton等催化氧化法,改进了化学氧化法的处理效率。同时也出现了其它处理办法如湿式催化氧化等方法,如1958年F.J.Zimmermann提出的湿式氧化技术(WAO)是以空气或纯氧作氧化剂,在高温(150t~350℃)、高压(0.5MPa~28MPa)条件下,将废水中的难降解有机物氧化分解为小分子有机物或CO2和H2O。由于在WAO技术中使用了较高的温度与压力,因此给设备的制造、运行操作都带来了相当大的困难。高温高压的运行条件一直是这种技术不能推广的主要原因。1894年Fenton发现二价铁和双氧水混合后会产生羟基自由基(-OH),-OH因其具有极高的氧化电位(2.8V),其氧化能力极强,与大多数有机污染物都可以发生快速的链式反应,无选择性地把有害物质氧化成CO2、H2O或矿物盐,无二次污染。Fenton试剂解决了催化氧化技术在常温常压下使用的问题,显著提高处理效率。20世纪80年代后,臭氧及双氧水的催化水处理技术在工业废水中的应用逐渐成为工业废水提高可生化性、有效降低污染浓度的主要方法。在使用的过程中,这种单纯应用单一催化剂催化氧化处理复杂的有机污染物的方法中也出现了氧化剂对不同有机污染物的处理活性不同的现象,处理种类受限等问题,工业有机废水,特别是工业园区的有机废水,其来源成分复杂,其中的有机污染物常为难生物降解有机物,处理难度大,是难降解有机废水。这部分的COD常大于2000mg/L,带有苯环结构,性质稳定的有机污染物占有比例较大,因此增加了处理的难度。所以将多种氧化方法联用进行处理的方法逐渐在工业实际应用中得到了应用,如在前期加入FeSO4,降解沉淀,然后再进行氧化剂氧化的工艺,但是对于考虑不同氧化剂之间的协同作用,提高氧化剂利用率,提高处理效果的工艺,还没有见到报道。Wastewater from industrial parks is difficult to treat, with complex sources and components. The organic pollutants in it are often refractory to biodegradable organic matter, which is difficult to treat. The COD in this part is usually greater than 2000mg/L, with a benzene ring structure, and a large proportion of stable organic pollutants, which increases the difficulty of treatment. At present, industrial park wastewater adopts a single oxidant treatment method: H 2 O 2 catalytic oxidation method or O 3 catalytic oxidation method, which oxidizes and decomposes organic matter in wastewater into small molecular organic matter or CO 2 and H 2 O, thereby removing Organic Pollutants. The traditional chemical oxidation method often cannot achieve the ideal oxidation effect only relying on the oxidation ability of the oxidant, so some auxiliary means are used to improve the oxidation efficiency. Catalytic oxidation methods such as UV/O 3 , UV/H 2 O 2 , and Fenton have appeared, which have improved the treatment efficiency of chemical oxidation methods. At the same time, other treatment methods such as wet catalytic oxidation have also appeared. For example, the wet oxidation technology (WAO) proposed by FJZimmermann in 1958 uses air or pure oxygen as the oxidant. ) conditions, the refractory organic matter in the wastewater is oxidized and decomposed into small molecule organic matter or CO 2 and H 2 O. Due to the high temperature and pressure used in WAO technology, it brings considerable difficulties to the manufacture and operation of the equipment. The operating conditions of high temperature and high pressure have always been the main reason why this technology cannot be promoted. In 1894, Fenton discovered that the mixture of ferrous iron and hydrogen peroxide would produce hydroxyl radicals (-OH). Because of its extremely high oxidation potential (2.8V), -OH has a strong oxidation ability and can be compatible with most organic pollutants. Rapid chain reaction occurs, non-selective oxidation of harmful substances into CO 2 , H 2 O or mineral salts, without secondary pollution. Fenton's reagent solves the problem of using catalytic oxidation technology at normal temperature and pressure, and significantly improves the treatment efficiency. After the 1980s, the application of ozone and hydrogen peroxide catalytic water treatment technology in industrial wastewater has gradually become the main method for improving the biodegradability of industrial wastewater and effectively reducing the concentration of pollution. In the process of use, this method of simply using a single catalyst to catalyze and oxidize complex organic pollutants also has the phenomenon that the oxidant has different treatment activities for different organic pollutants, and the treatment types are limited. Industrial organic wastewater, In particular, the organic wastewater in industrial parks has complex sources and components, and the organic pollutants in it are often refractory organic matter, which is difficult to treat and is refractory organic wastewater. The COD in this part is usually greater than 2000mg/L, with a benzene ring structure, and a large proportion of stable organic pollutants, which increases the difficulty of treatment. Therefore, the method of combining multiple oxidation methods for treatment has gradually been applied in industrial practical applications, such as adding FeSO4 in the early stage, degrading the precipitate, and then performing oxidation of the oxidant, but for considering the synergistic effect between different oxidants, Improve the utilization rate of oxidant, improve the technology of treatment effect, also do not see report.

发明内容 Contents of the invention

针对上述存在问题,本发明的目的在于提供一种串联催化氧化处理工业有机废水工艺为了实现上述目的,本发明的技术解决方案如下:For above-mentioned existing problem, the object of the present invention is to provide a kind of tandem catalytic oxidation treatment industrial organic wastewater process. In order to realize above-mentioned object, the technical solution of the present invention is as follows:

一种串联催化氧化处理工业有机废水工艺,对经预处理过程后的有机废水采用的催化氧化处理方式为一级催化氧化与二级协同催化氧化。所述一级催化氧化指工业有机废水进入第一级催化氧化池体,池体中按质量比水∶一级催化剂=1000∶1放置催化剂,进水完成后加入臭氧,臭氧加入量为100~800g/T·h,反应时间为30分钟,池内废水进行第一级催化氧化内循环,循环过程持续40分钟,使废水与一级催化剂充分接触反应,第一级催化氧化反应结束。A serial catalytic oxidation treatment process for industrial organic wastewater, the catalytic oxidation treatment method adopted for the pretreated organic wastewater is a first-stage catalytic oxidation and a second-stage synergistic catalytic oxidation. The first-level catalytic oxidation means that industrial organic wastewater enters the first-level catalytic oxidation pool body, and the catalyst is placed in the pool body according to the mass ratio of water: first-level catalyst = 1000: 1. After the water intake is completed, ozone is added, and the amount of ozone added is 100 ~ 800g/T·h, the reaction time is 30 minutes, the wastewater in the pool undergoes the internal circulation of the first-stage catalytic oxidation, and the circulation process lasts for 40 minutes, so that the wastewater and the first-stage catalyst fully contact and react, and the first-stage catalytic oxidation reaction ends.

所述二级协同催化氧化是指经一级催化反应后的工业有机废水从第一级反应池排至第二级反应池,池体中按质量比水∶二级催化剂=1100∶1放置催化剂,并将一级催化氧化过程中未反应的臭氧收集至第二级反应池,曝气入第二级催化氧化池体,泵入浓度为20%双氧水100~700g/T·h,停留处理30分钟,期间进行内循环,循环过程持续30分钟,第二级催化氧化反应结束。The two-stage synergistic catalytic oxidation refers to that the industrial organic wastewater after the primary catalytic reaction is discharged from the first-stage reaction pool to the second-stage reaction pool, and the catalyst is placed in the pool body according to the mass ratio of water: secondary catalyst=1100:1 , and collect unreacted ozone in the first-stage catalytic oxidation process to the second-stage reaction tank, aerate into the second-stage catalytic oxidation tank body, pump in 20% hydrogen peroxide 100-700g/T h, and stay for 30 Minutes, during which the internal circulation is carried out, and the circulation process lasts for 30 minutes, and the second-stage catalytic oxidation reaction ends.

所述一级催化剂为以活性炭为载体,表面复合含锰金属离子,复合量为3g/kg。The first-stage catalyst uses activated carbon as a carrier, and the surface is compounded with manganese-containing metal ions, and the compounding amount is 3g/kg.

所述二级催化剂为以活性炭为载体,表面复合含铁金属离子,复合量为5g/kg。The secondary catalyst uses activated carbon as a carrier, and the surface is compounded with iron-containing metal ions, and the compounding amount is 5g/kg.

由于采用以上技术方案,本发明的的串联催化氧化处理工业有机废水工艺,采用催化臭氧化和催化双氧水化的串联与协同的方式,将多种氧化剂催化方法串联,实现了氧化剂间的协同和对复杂有机污染物的快速处理,所述串联催化氧化工艺是在常温、常压条件下,固定第一催化剂在第一个催化氧化过程中,为臭氧催化氧化过程:使用固定化催化剂催化分解臭氧,生成大量羟基自由基(.OH),利用.OH氧化还原电位和亲电性打断有机污染物分子结构中的生色基团,使水中的有机污染物快速降解,并且使废水中高分子氧化物的a位C-H键、β-C键、γ-C键、C-C断裂成为低分子化合物,从而对废水中的有机物进行氧化分解,快速降解有机物COD;余下的臭氧与剩余的有机污染物进入第二个催化分解过程,在此过程中,采用第二催化剂催化分解双氧水,产生OH自由基降解氧化剩余有机污物,并且,进入该过程中的臭氧与双氧水发生链式反应,产生更多的自由基,活化了双氧水与臭氧的降解作用,协同反应,达到快速降解有机污染物的目的。Due to the adoption of the above technical scheme, the serial catalytic oxidation treatment process of industrial organic wastewater of the present invention adopts the serial and synergistic mode of catalytic ozonation and catalytic hydrogen peroxide hydration, and connects various oxidant catalytic methods in series to realize the synergy between oxidants and the synergy between them. Rapid treatment of complex organic pollutants, the series catalytic oxidation process is to fix the first catalyst in the first catalytic oxidation process under normal temperature and normal pressure conditions, which is an ozone catalytic oxidation process: using an immobilized catalyst to catalyze the decomposition of ozone, Generate a large number of hydroxyl radicals (.OH), use the .OH redox potential and electrophilicity to break the chromophore in the molecular structure of organic pollutants, so that the organic pollutants in the water can be degraded rapidly, and the polymer oxides in the wastewater A position C-H bond, β-C bond, γ-C bond, C-C breaks into low molecular compounds, so as to oxidize and decompose the organic matter in the wastewater, and quickly degrade the organic matter COD; the remaining ozone and the remaining organic pollutants enter the second Catalytic decomposition process, in this process, the second catalyst is used to catalyze the decomposition of hydrogen peroxide to generate OH free radicals to degrade and oxidize the remaining organic pollutants, and the ozone entering the process undergoes a chain reaction with hydrogen peroxide to generate more free radicals, The degradation effect of hydrogen peroxide and ozone is activated, and the synergistic reaction is achieved to rapidly degrade organic pollutants.

本发明的串联催化氧化处理工业有机废水工艺,不仅提高了处理难降解有机污染物的处理效率能力,而且提高了氧化剂的利用效率;可以有效降低运行成本,扩展工艺的应用领域。它改变了现有工业有机废水单一采用双氧水或者臭氧的催化氧化处理法,其处理废水种类受限、运行成本高、操作运行复杂的问题。本发明应用在同等运行条件下,可以大幅度提高工业有机废水处理效率,可以降低设备投资成本与运行成本,使之适用于更广泛的工业有机废水,如造纸废水、纺织印染废水或农药废水等种类的处理。The serial catalytic oxidation process of the present invention for treating industrial organic wastewater not only improves the treatment efficiency of refractory organic pollutants, but also improves the utilization efficiency of oxidants; it can effectively reduce operating costs and expand the application field of the process. It changes the problems of the existing industrial organic wastewater that only uses hydrogen peroxide or ozone catalytic oxidation treatment, which has limited types of wastewater, high operating costs, and complicated operation. Applied under the same operating conditions, the present invention can greatly improve the treatment efficiency of industrial organic wastewater, reduce equipment investment cost and operating cost, and make it applicable to a wider range of industrial organic wastewater, such as papermaking wastewater, textile printing and dyeing wastewater or pesticide wastewater, etc. Kind of processing.

附图说明 Description of drawings

附图是本发明的一种串联催化氧化处理工业有机废水工艺流程图。The accompanying drawing is a process flow diagram of a series catalytic oxidation treatment of industrial organic wastewater according to the present invention.

具体实施方式 Detailed ways

下面结合附图及具体实施例对本发明做进一步详细描述,见附图。The present invention will be further described in detail below in conjunction with the drawings and specific embodiments, see the drawings.

一种串联催化氧化处理工业有机废水工艺,其工艺流程为:工业有机废水→均和曝气→中和混凝沉淀→中间水池→一级催化氧化→二级协同催化氧化→出水A serial catalytic oxidation process for treating industrial organic wastewater, the process flow is: industrial organic wastewater → homogenization and aeration → neutralization coagulation sedimentation → intermediate pool → primary catalytic oxidation → secondary synergistic catalytic oxidation → effluent

所述有机废水预处理包括对废水的均和曝气流程和中和混凝沉淀流程,均和曝气流程采用均和曝气池,均和曝气池控制空气曝气强度1~7m3/m2.h,以使各类工业有机废水充分均和;中和混凝沉淀流程采用中和混凝沉淀池,在中和区采用切断阀投加熟石灰或盐酸调节pH值,控制pH值6~9,后绪投加0.5%助凝剂PAC,控制投加量1~10mg/L;通过预处理工艺去除废水中的大部分悬浮物和油分。The organic wastewater pretreatment includes a homogeneous aeration process and a neutralization coagulation sedimentation process for the wastewater. The homogeneous aeration process adopts a homogeneous aeration tank, and the homogeneous aeration tank controls the air aeration intensity to 1-7m 3 / m 2 .h to make all kinds of industrial organic wastewater fully homogeneous; the neutralization coagulation sedimentation process uses a neutralization coagulation sedimentation tank, and a cut-off valve is used in the neutralization zone to add slaked lime or hydrochloric acid to adjust the pH value and control the pH value to 6 ~9, add 0.5% coagulant aid PAC in the end, and control the dosage of 1~10mg/L; remove most of the suspended solids and oil in the wastewater through the pretreatment process.

对经预处理过程后的有机废水采用的催化氧化处理方式为一级催化氧化与二级协同催化氧化,所述一级催化氧化指工业有机废水经中间水池进入第一级催化氧化池体,池体中按质量比水∶一级催化剂=1000∶1放置一级催化剂,所述一级催化剂为以活性炭为载体,表面复合含锰金属离子,复合量为3g/kg,进水完成后加入臭氧,臭氧加入量为100~800g/T·h,反应时间为30分钟,池内废水在第一级催化氧化池进行内循环,循环过程持续40分钟,使废水与催化进充分接触反应,第一级催化氧化反应结束。The catalytic oxidation treatment method adopted for the organic wastewater after the pretreatment process is primary catalytic oxidation and secondary synergistic catalytic oxidation. Put the primary catalyst in the body according to the mass ratio of water: primary catalyst = 1000: 1. The primary catalyst is based on activated carbon as a carrier, and the surface is compounded with manganese metal ions. The composite amount is 3g/kg, and ozone is added after the water intake is completed. , the amount of ozone added is 100-800g/T h, and the reaction time is 30 minutes. The wastewater in the pool is internally circulated in the first-stage catalytic oxidation pool. The circulation process lasts for 40 minutes, so that the wastewater and the catalyst are fully contacted. The catalytic oxidation reaction ends.

所述二级协同催化氧化是指经一级催化反应后的工业有机废水从第一级反应池排至第二级催化氧化池,池体中按质量比水∶二级催化剂=1100∶1放置二级催化剂,所述二级催化剂为以活性炭为载体,表面复合含铁金属离子,复合量为5g/kg,并将一级催化氧化过程中未反应的臭氧收集至第二级反应池,曝气入第二级催化氧化池体,泵入浓度为20%双氧水100~700g/T·h,停留处理30分钟,期间进行内循环,循环过程持续30分钟,第二级催化氧化反应结束。The two-stage synergistic catalytic oxidation means that the industrial organic wastewater after the primary catalytic reaction is discharged from the first-stage reaction pool to the second-stage catalytic oxidation pool, and the pool body is placed according to the mass ratio of water: secondary catalyst = 1100:1 A secondary catalyst, the secondary catalyst is based on activated carbon as a carrier, and the surface is compounded with iron-containing metal ions, the composite amount is 5g/kg, and the unreacted ozone in the primary catalytic oxidation process is collected into the secondary reaction tank, exposed to Gas enters the second-stage catalytic oxidation tank body, pumps 20% hydrogen peroxide at a concentration of 100-700g/T·h, and stays for 30 minutes for treatment, during which internal circulation is carried out. The circulation process lasts for 30 minutes, and the second-stage catalytic oxidation reaction ends.

所述串联催化氧化工艺是在常温、常压条件下,固定催化剂在第一个催化氧化过程中,为臭氧催化氧化过程:使用固定化催化剂催化分解臭氧,生成大量羟基自由基(.OH),利用.OH氧化还原电位和亲电性打断有机污染物分子结构中的生色基团,使水中的有机污染物快速降解,并且使废水中高分子氧化物的a位C-H键、β-C键、γ-C键、C-C断裂成为低分子化合物,从而对废水中的有机物进行氧化分解,快速降解有机物COD;余下的臭氧与剩余的有机污染物进入第二个催化分解过程,在此过程中,采用别外一种催化剂催化分解双氧水,产生OH自由基降解氧化剩余有机污物,并且,进入该过程中的臭氧与双氧水发生链式反应,产生更多的自由基,活化了双氧水与臭氧的降解作用,协同反应,达到快速降解有机污染物的目的。The series catalytic oxidation process is under the condition of normal temperature and normal pressure, the fixed catalyst is in the first catalytic oxidation process, which is the ozone catalytic oxidation process: the fixed catalyst is used to catalyze the decomposition of ozone to generate a large number of hydroxyl radicals (.OH), Use .OH oxidation-reduction potential and electrophilicity to break the chromogenic group in the molecular structure of organic pollutants, so that the organic pollutants in the water can be degraded rapidly, and the a-position C-H bond, β-C bond, The γ-C bond and C-C are broken to form low molecular compounds, so as to oxidize and decompose the organic matter in the wastewater, and quickly degrade the organic matter COD; the remaining ozone and the remaining organic pollutants enter the second catalytic decomposition process. In this process, adopt Another catalyst catalyzes the decomposition of hydrogen peroxide to generate OH free radicals to degrade and oxidize the remaining organic pollutants, and the ozone entering the process undergoes a chain reaction with hydrogen peroxide, generating more free radicals and activating the degradation of hydrogen peroxide and ozone , synergistic reaction, to achieve the purpose of rapid degradation of organic pollutants.

所述串联催化氧化工艺采用两级处理工艺,由进水-反应、循环-排水流程组成,连续运行;工业有机废水进入第一级催化氧化池体,进水完成后加入臭氧,加入量根据入水COD的浓度,加入100~800g/T·h,进气30分钟,池内废水第一级催化氧化内循环,循环过程持续40分钟,使废水与填料充分接触反应,第一级催化氧化反应结束;废水从第一级反应池排至第二级循环池,并将未反应的臭氧收集,曝气入第二级催化氧化池体,泵入浓度为20%双氧水100~700g/T·h,停留处理30分钟后,池内废水开始第二级催化氧化内循环,循环过程持续20分钟,第二级催化氧化反应结束,切断电源;经过两级催化氧化反应,完成一个废根据权利要求1所述的串联催化氧化处理工业有机废水工艺,其特征在于,所述均和曝气池优选控制曝气强度1~7m3/m2.H。The series catalytic oxidation process adopts a two-stage treatment process, which is composed of water intake-reaction, circulation-drainage process, and runs continuously; industrial organic wastewater enters the first-stage catalytic oxidation tank body, and ozone is added after the water intake is completed. COD concentration, add 100-800g/T h, air intake for 30 minutes, the first-stage catalytic oxidation of wastewater in the pool is internally circulated, and the circulation process lasts for 40 minutes, so that the wastewater and the filler are fully contacted and reacted, and the first-stage catalytic oxidation reaction is completed; Wastewater is discharged from the first-stage reaction pool to the second-stage circulation pool, and the unreacted ozone is collected, aerated into the second-stage catalytic oxidation pool body, and the concentration of 20% hydrogen peroxide is pumped in 100-700g/T·h, and it stays After 30 minutes of treatment, the wastewater in the pool starts the second-stage catalytic oxidation internal circulation, and the circulation process lasts for 20 minutes. After the second-stage catalytic oxidation reaction ends, the power supply is cut off; The process for treating industrial organic wastewater by serial catalytic oxidation is characterized in that the homogenization and aeration tank preferably controls the aeration intensity to 1-7m 3 /m 2 .H.

具体实施例:Specific examples:

实施例一:按上述工艺流程:Embodiment one: by above-mentioned technological process:

所述有机废水为制药废水,指标为:处理量1T,浓度为COD:2000mg/L;其有机废水预处理包括对废水的均和曝气流程和中和混凝沉淀流程,均和曝气流程采用均和曝气池,均和曝气池控制空气曝气强度7m3/m2.h,充分均和;中和混凝沉淀流程采用中和混凝沉淀池,在中和区采用切断阀投加熟石灰或盐酸或盐酸调节pH值,控制pH值6~9,后续投加0.5%助凝剂PAC,控制投加量8mg/L;通过预处理工艺去除废水中的大部分悬浮物和油分。The organic wastewater is pharmaceutical wastewater, the index is: the treatment capacity is 1T, and the concentration is COD: 2000mg/L; the pretreatment of the organic wastewater includes the homogenization and aeration process of the wastewater and the neutralization coagulation sedimentation process, and the homogenization and aeration process The homogenization and aeration tank is used, and the air aeration intensity of the homogenization aeration tank is 7m 3 /m 2 .h, which is fully homogenized; the neutralization coagulation sedimentation process adopts a neutralization coagulation sedimentation tank, and a shut-off valve is used in the neutralization area Add slaked lime or hydrochloric acid or hydrochloric acid to adjust the pH value, control the pH value from 6 to 9, then add 0.5% coagulant aid PAC, and control the dosage of 8mg/L; remove most of the suspended solids and oil in the wastewater through the pretreatment process .

对经预处理过程后的有机废水经中间水池进入第一级催化氧化池体,池体中放置1000g负载量为3g/kg复合含锰金属离子的活性炭催化剂。进水完成后加入臭氧,臭氧加入量为700g/T·h,反应时间为30分钟,池内废水第一级催化氧化内循环,循环过程持续40分钟,使废水与催化进充分接触反应,第一级催化氧化反应结束。The organic wastewater after the pretreatment process enters the first-stage catalytic oxidation tank body through the intermediate pool, and 1000g of activated carbon catalyst with a loading capacity of 3g/kg composite manganese metal ions is placed in the pool body. After the water inflow is completed, ozone is added. The amount of ozone added is 700g/T h, and the reaction time is 30 minutes. The first-stage catalytic oxidation of the wastewater in the pool is internally circulated. The circulation process lasts for 40 minutes, so that the wastewater and the catalyst can fully contact and react. The stage catalytic oxidation reaction ends.

经一级催化反应后的工业有机废水从第一级反应池排至第二级反应池,池体中放置910g负载量为5g/kg复合含铁金属离子的活性炭催化剂。并将未反应的臭氧收集,曝气入第二级催化氧化池体,泵入浓度为20%的双氧水800g/T·h,停留处理30分钟,期间进行内循环,循环过程持续30分钟,第二级催化氧化反应结束。水处理流程结束;出水指标为:处理量1T,浓度为COD:800mg/L。The industrial organic wastewater after the first-stage catalytic reaction is discharged from the first-stage reaction pool to the second-stage reaction pool, and 910 g of activated carbon catalysts with a loading capacity of 5 g/kg of composite iron-containing metal ions are placed in the pool body. The unreacted ozone is collected, aerated into the second-stage catalytic oxidation tank body, and 800g/T h of hydrogen peroxide with a concentration of 20% is pumped in, and the treatment is stopped for 30 minutes, during which internal circulation is carried out, and the circulation process lasts for 30 minutes. The secondary catalytic oxidation reaction ends. The water treatment process is over; the effluent index is: the treatment capacity is 1T, and the concentration is COD: 800mg/L.

实施例二:按上述工艺流程:Embodiment two: by above-mentioned technological process:

所述有机废水为制药废水,指标为:处理量1T,浓度为COD:2000mg/L,其有机废水预处理包括对废水的均和曝气流程和中和混凝沉淀流程,均和曝气流程采用均和曝气池,均和曝气池控制空气曝气强度6m3/m2.h,充分均和;中和混凝沉淀流程采用中和混凝沉淀池,在中和区采用切断阀投加熟石灰或盐酸调节pH值,控制pH值6~9,后续投加0.5%助凝剂PAC,控制投加量5mg/L;通过预处理工艺去除废水中的大部分悬浮物和油分。The organic wastewater is pharmaceutical wastewater, the index is: the treatment capacity is 1T, and the concentration is COD: 2000mg/L. The pretreatment of the organic wastewater includes the homogenization and aeration process of the wastewater and the neutralization coagulation sedimentation process, and the homogenization and aeration process The uniform aeration tank is adopted, and the air aeration intensity of the uniform aeration tank is 6m 3 /m 2 .h, which is fully uniform; the neutralization coagulation sedimentation process adopts a neutralization coagulation sedimentation tank, and a shut-off valve is used in the neutralization area Add slaked lime or hydrochloric acid to adjust the pH value, control the pH value to 6-9, then add 0.5% coagulant PAC, and control the dosage to 5mg/L; remove most of the suspended solids and oil in the wastewater through the pretreatment process.

对经预处理过程后的有机废水经中间水池进入第一级催化氧化池体,池体中放置1000g负载量为3g/kg复合含锰金属离子的活性炭催化剂。进水完成后加入臭氧,臭氧加入量为400g/T·h,反应时间为30分钟,池内废水第一级催化氧化内循环,循环过程持续40分钟,使废水与催化进充分接触反应,第一级催化氧化反应结束;The organic wastewater after the pretreatment process enters the first-stage catalytic oxidation tank body through the intermediate pool, and 1000g of activated carbon catalyst with a loading capacity of 3g/kg composite manganese metal ions is placed in the pool body. After the water inflow is completed, ozone is added. The amount of ozone added is 400g/T h, and the reaction time is 30 minutes. The first-stage catalytic oxidation of the wastewater in the pool is internally circulated. The circulation process lasts for 40 minutes, so that the wastewater and the catalyst can fully contact and react. The stage catalytic oxidation reaction ends;

经一级催化反应后的工业有机废水从第一级反应池排至第二级反应池,池体中放置910g负载量为5g/kg复合含铁金属离子的活性炭催化剂。并将未反应的臭氧收集,曝气入第二级催化氧化池体,泵入浓度为20%的双氧水500g/T·h,停留处理30分钟,期间进行内循环,循环过程持续30分钟,第二级催化氧化反应结束。水处理流程结束;出水指标为:处理量1T,浓度为COD:1000mg/LThe industrial organic wastewater after the first-stage catalytic reaction is discharged from the first-stage reaction pool to the second-stage reaction pool, and 910 g of activated carbon catalysts with a loading capacity of 5 g/kg of composite iron-containing metal ions are placed in the pool body. And unreacted ozone is collected, aerated into the second-stage catalytic oxidation tank body, pumped into the concentration of 20% hydrogen peroxide 500g/T h, stay for 30 minutes, during which internal circulation is carried out, and the circulation process lasts for 30 minutes. The secondary catalytic oxidation reaction ends. The water treatment process is over; the effluent index is: the treatment capacity is 1T, and the concentration is COD: 1000mg/L

实施例三:按上述工艺流程:Embodiment three: by above-mentioned technological process:

所述有机废水为制药废水,指标为:处理量1T,浓度为COD:2000mg/L,其有机废水预处理包括对废水的均和曝气流程和中和混凝沉淀流程,均和曝气流程采用均和曝气池,均和曝气池控制空气曝气强度1m3/m2.h,充分均和;中和混凝沉淀流程采用中和混凝沉淀池,在中和区采用切断阀投加熟石灰或盐酸调节pH值,控制pH值6~9,后续投加0.5%助凝剂PAC,控制投加量1mg/L;通过预处理工艺去除废水中的大部分悬浮物和油分。The organic wastewater is pharmaceutical wastewater, the index is: the treatment capacity is 1T, and the concentration is COD: 2000mg/L. The pretreatment of the organic wastewater includes the homogenization and aeration process of the wastewater and the neutralization coagulation sedimentation process, and the homogenization and aeration process The uniform aeration tank is adopted, and the air aeration intensity of the uniform aeration tank is controlled to 1m 3 /m 2 .h, which is fully uniform; the neutralization coagulation sedimentation process adopts a neutralization coagulation sedimentation tank, and a shut-off valve is used in the neutralization area Add slaked lime or hydrochloric acid to adjust the pH value, control the pH value to 6-9, then add 0.5% coagulant aid PAC, control the dosage of 1mg/L; remove most of the suspended solids and oil in the wastewater through the pretreatment process.

对经预处理过程后的有机废水经中间水池进入第一级催化氧化池体,池体中放置1000g负载量为3g/kg复合含锰金属离子的活性炭催化剂。进水完成后加入臭氧,臭氧加入量为100g/T·h,反应时间为30分钟,池内废水第一级催化氧化内循环,循环过程持续40分钟,使废水与催化进充分接触反应,第一级催化氧化反应结束;The organic wastewater after the pretreatment process enters the first-stage catalytic oxidation tank body through the intermediate pool, and 1000g of activated carbon catalyst with a loading capacity of 3g/kg composite manganese metal ions is placed in the pool body. After the water inflow is completed, add ozone, the amount of ozone added is 100g/T h, and the reaction time is 30 minutes. The first-stage catalytic oxidation of wastewater in the pool is internally circulated. The cycle lasts for 40 minutes, so that the wastewater and the catalyst can fully contact and react. The stage catalytic oxidation reaction ends;

经一级催化反应后的工业有机废水从第一级反应池排至第二级反应池,池体中放置910g负载量为5g/kg复合含铁金属离子的活性炭催化剂。并将未反应的臭氧收集,曝气入第二级催化氧化池体,泵入浓度为20%的双氧水100g/T·h,停留处理30分钟,期间进行内循环,循环过程持续30分钟,第二级催化氧化反应结束。水处理流程结束;出水指标为:处理量1T,浓度为COD:1800mg/LThe industrial organic wastewater after the first-stage catalytic reaction is discharged from the first-stage reaction pool to the second-stage reaction pool, and 910 g of activated carbon catalysts with a loading capacity of 5 g/kg of composite iron-containing metal ions are placed in the pool body. And the unreacted ozone is collected, aerated into the second-stage catalytic oxidation tank body, pumped with a concentration of 20% hydrogen peroxide 100g/T h, and stayed for 30 minutes, during which internal circulation was carried out, and the circulation process lasted for 30 minutes. The secondary catalytic oxidation reaction ends. The water treatment process is over; the effluent index is: the treatment capacity is 1T, and the concentration is COD: 1800mg/L

实施例四:按上述工艺流程:Embodiment four: by above-mentioned technological process:

所述有机废水为印染废水,指标为:处理量1T,浓度为COD:2000mg/L,其有机废水预处理包括对废水的均和曝气流程和中和混凝沉淀流程,均和曝气流程采用均和曝气池,均和曝气池控制空气曝气强度4m3/m2.h,充分均和;中和混凝沉淀流程采用中和混凝沉淀池,在中和区采用切断阀投加熟石灰或盐酸调节pH值,控制pH值6~9,后续投加0.5%助凝剂PAC,控制投加量8mg/L;通过预处理工艺去除废水中的大部分悬浮物和油分。The organic wastewater is printing and dyeing wastewater, the index is: the treatment capacity is 1T, and the concentration is COD: 2000mg/L. The homogenizing aeration tank is adopted, and the air aeration intensity of the homogenizing aeration tank is 4m 3 /m 2 .h, which is fully homogenized; the neutralization coagulation sedimentation process adopts a neutralization coagulation sedimentation tank, and a shut-off valve is used in the neutralization area Add slaked lime or hydrochloric acid to adjust the pH value, control the pH value to 6-9, then add 0.5% coagulant aid PAC, and control the dosage to 8mg/L; remove most of the suspended solids and oil in the wastewater through the pretreatment process.

对经预处理过程后的有机废水经中间水池进入第一级催化氧化池体,池体中放置1000g负载量为3g/kg复合含锰金属离子的活性炭催化剂。进水完成后加入臭氧,臭氧加入量为800g/T·h,反应时间为30分钟,池内废水第一级催化氧化内循环,循环过程持续40分钟,使废水与催化进充分接触反应,第一级催化氧化反应结束;The organic wastewater after the pretreatment process enters the first-stage catalytic oxidation tank body through the intermediate pool, and 1000g of activated carbon catalyst with a loading capacity of 3g/kg composite manganese metal ions is placed in the pool body. After the water inflow is completed, ozone is added. The amount of ozone added is 800g/T h, and the reaction time is 30 minutes. The first-stage catalytic oxidation of wastewater in the pool is internally circulated. The circulation process lasts for 40 minutes, so that the wastewater and the catalyst can fully contact and react. The stage catalytic oxidation reaction ends;

经一级催化反应后的工业有机废水从第一级反应池排至第二级反应池,池体中放置910g负载量为5g/kg复合含铁金属离子的活性炭催化剂。并将未反应的臭氧收集,曝气入第二级催化氧化池体,泵入浓度为20%的双氧水800g/T·h,停留处理30分钟,期间进行内循环,循环过程持续30分钟,第二级催化氧化反应结束。水处理流程结束;出水指标为:处理量1T,浓度为COD:800mg/LThe industrial organic wastewater after the first-stage catalytic reaction is discharged from the first-stage reaction pool to the second-stage reaction pool, and 910 g of activated carbon catalysts with a loading capacity of 5 g/kg of composite iron-containing metal ions are placed in the pool body. The unreacted ozone is collected, aerated into the second-stage catalytic oxidation tank body, and 800g/T h of hydrogen peroxide with a concentration of 20% is pumped in for 30 minutes, during which internal circulation is carried out, and the circulation process lasts for 30 minutes. The secondary catalytic oxidation reaction ends. The water treatment process is over; the effluent index is: the treatment capacity is 1T, and the concentration is COD: 800mg/L

实施例五:按上述工艺流程:Embodiment five: by above-mentioned technological process:

所述有机废水为造纸废水,指标为:处理量1T,浓度为COD:2000mg/L,其有机废水预处理包括对废水的均和曝气流程和中和混凝沉淀流程,均和曝气流程采用均和曝气池,均和曝气池控制空气曝气强度7m3/m2.h,充分均和;中和混凝沉淀流程采用中和混凝沉淀池,在中和区采用切断阀投加熟石灰或盐酸调节pH值,控制pH值6~9,后续投加0.5%助凝剂PAC,控制投加量2mg/L;通过预处理工艺去除废水中的大部分悬浮物和油分。The organic wastewater is papermaking wastewater, the index is: the treatment capacity is 1T, the concentration is COD: 2000mg/L, and the pretreatment of the organic wastewater includes the homogenization and aeration process of the wastewater and the neutralization coagulation sedimentation process, and the homogenization and aeration process The homogenization and aeration tank is used, and the air aeration intensity of the homogenization aeration tank is 7m 3 /m 2 .h, which is fully homogenized; the neutralization coagulation sedimentation process adopts a neutralization coagulation sedimentation tank, and a shut-off valve is used in the neutralization area Add slaked lime or hydrochloric acid to adjust the pH value, control the pH value to 6-9, then add 0.5% coagulant PAC, and control the dosage to 2mg/L; remove most of the suspended solids and oil in the wastewater through the pretreatment process.

对经预处理过程后的有机废水经中间水池进入第一级催化氧化池体,池体中放置1000g负载量为3g/kg复合含锰金属离子的活性炭催化剂。进水完成后加入臭氧,臭氧加入量为800g/T·h,反应时间为30分钟,池内废水第一级催化氧化内循环,循环过程持续40分钟,使废水与催化进充分接触反应,第一级催化氧化反应结束;The organic wastewater after the pretreatment process enters the first-stage catalytic oxidation tank body through the intermediate pool, and 1000g of activated carbon catalyst with a loading capacity of 3g/kg composite manganese metal ions is placed in the pool body. After the water inflow is completed, ozone is added. The amount of ozone added is 800g/T h, and the reaction time is 30 minutes. The first-stage catalytic oxidation of wastewater in the pool is internally circulated. The circulation process lasts for 40 minutes, so that the wastewater and the catalyst can fully contact and react. The stage catalytic oxidation reaction ends;

经一级催化反应后的工业有机废水从第一级反应池排至第二级反应池,池体中放置910g负载量为5g/kg复合含铁金属离子的活性炭催化剂。并将未反应的臭氧收集,曝气入第二级催化氧化池体,泵入浓度为20%的双氧水600g/T·h,停留处理30分钟,期间进行内循环,循环过程持续30分钟,第二级催化氧化反应结束。水处理流程结束;出水指标为:处理量1T,浓度为COD:800mg/LThe industrial organic wastewater after the first-stage catalytic reaction is discharged from the first-stage reaction pool to the second-stage reaction pool, and 910 g of activated carbon catalysts with a loading capacity of 5 g/kg of composite iron-containing metal ions are placed in the pool body. And the unreacted ozone is collected, aerated into the second-stage catalytic oxidation tank body, pumped into the concentration of 20% hydrogen peroxide 600g/T h, stay for 30 minutes, during which the internal circulation is carried out, and the circulation process lasts for 30 minutes. The secondary catalytic oxidation reaction ends. The water treatment process is over; the effluent index is: the treatment capacity is 1T, and the concentration is COD: 800mg/L

Claims (3)

1.一种串联催化氧化处理工业有机废水工艺,它包括对工业有机废水进行预处理和催化氧化处理,其特征在于:对经预处理过程后的有机废水采用的催化氧化处理的方式为一级催化氧化与二级协同催化氧化,所述一级催化氧化指工业有机废水进入第一级催化氧化池体,池体中按质量比水∶一级催化剂=1000∶1放置催化剂,进水完成后加入臭氧,臭氧加入量为100~800g/T·h,反应时间为30分钟,池内废水进行第一级催化氧化内循环,循环过程持续40分钟,使废水与一级催化剂充分接触反应,第一级催化氧化反应结束,所述二级协同催化氧化是指经一级催化反应后的工业有机废水从第一级反应池排至第二级反应池,池体中按质量比水∶二级催化剂=1100∶1放置二级催化剂,并将一级催化氧化过程中未反应的臭氧收集第二级反应池,曝气入第二级催化氧化池体,泵入浓度为20%双氧水100~700g/T·h,停留处理30分钟,期间进行内循环,循环过程持续30分钟,第二级催化氧化反应结束。1. A tandem catalytic oxidation treatment of industrial organic wastewater process, which includes carrying out pretreatment and catalytic oxidation treatment of industrial organic wastewater, characterized in that: the catalytic oxidation treatment method adopted for the organic wastewater after the pretreatment process is one-level Catalytic oxidation and secondary synergistic catalytic oxidation, the first-level catalytic oxidation refers to industrial organic wastewater entering the first-level catalytic oxidation pool body, and the catalyst is placed in the pool body according to the mass ratio of water: first-level catalyst = 1000: 1, after the water intake is completed Add ozone, the amount of ozone added is 100-800g/T h, and the reaction time is 30 minutes. The wastewater in the pool undergoes the first-stage catalytic oxidation internal circulation. The first-level catalytic oxidation reaction ends, and the second-level synergistic catalytic oxidation refers to that the industrial organic wastewater after the first-level catalytic reaction is discharged from the first-level reaction pool to the second-level reaction pool, and in the pool body, water: secondary catalyst =1100:1 place the secondary catalyst, collect the unreacted ozone in the primary catalytic oxidation process from the secondary reaction tank, aerate it into the secondary catalytic oxidation tank body, pump in 20% hydrogen peroxide at a concentration of 100-700g/ T h, stay for 30 minutes, during which internal circulation is carried out, the circulation process lasts for 30 minutes, and the second-stage catalytic oxidation reaction ends. 2.根据权利要求1所述的串联催化氧化处理工业有机废水工艺,其特征在于:所述一级催化剂为以活性炭为载体,表面复合含锰金属离子,复合量为3g/kg。2. The tandem catalytic oxidation process for treating industrial organic wastewater according to claim 1, characterized in that: the first-stage catalyst uses activated carbon as a carrier, and the surface is compounded with manganese-containing metal ions, and the compounding amount is 3g/kg. 3.根据权利要求1所述的串联催化氧化处理工业有机废水工艺,其特征在于:所述二级催化剂为以活性炭为载体,表面复合含铁金属离子,复合量为5g/kg。3. The tandem catalytic oxidation process for industrial organic wastewater treatment according to claim 1, characterized in that: the secondary catalyst is activated carbon as a carrier, and the surface is compounded with iron-containing metal ions, and the compounding amount is 5g/kg.
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Cited By (12)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102583814A (en) * 2012-01-18 2012-07-18 马放 Method for processing heavy alkylbenzene sulfonate waste water
CN104193118A (en) * 2014-09-25 2014-12-10 无锡昊瑜节能环保设备有限公司 Printing and dyeing wastewater recycling device and wastewater purification method
CN105439311A (en) * 2014-08-12 2016-03-30 北京朗新明环保科技有限公司 Coal chemical industrial wastewater deep treatment apparatus and method
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CN107364943A (en) * 2017-09-10 2017-11-21 杭州东日节能技术有限公司 Catalytic wet oxidation administers the device and its technique of hydrochloric organic wastewater
CN108275848A (en) * 2018-03-27 2018-07-13 中节能工程技术研究院有限公司 A kind of wastewater treatment integrating device and method
CN108585336A (en) * 2018-05-23 2018-09-28 上海邵雍环境科技有限公司 The processing method of glyphosate mother solution wet oxidation sequential catalyst wet oxidation
CN110342724A (en) * 2019-08-14 2019-10-18 安徽科博瑞环境科技有限公司 A kind of high-concentration industrial organic waste water zero-discharge treatment system and its technique
CN112607845A (en) * 2021-01-26 2021-04-06 山西远航环境科技股份有限公司 Method for treating organic wastewater by using ozone composite activated carbon nano titanium dioxide
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Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH0364393A (en) * 1989-08-02 1991-03-19 Nkk Corp Remote driving of coke guide car
JPH09164393A (en) * 1995-12-18 1997-06-24 Meidensha Corp Treatment of hardly-decomposable matter contained in return water
JP2000176468A (en) * 1998-12-11 2000-06-27 Ataka Construction & Engineering Co Ltd Sewage treatment and device therefor
EP1234802A1 (en) * 1999-10-28 2002-08-28 Kazuto Hashizume Improved method and apparatus for water treatment
CN101327985A (en) * 2008-07-31 2008-12-24 哈尔滨工业大学 A method for catalytic ozonation to remove organic pollutants in water
CN101781036A (en) * 2009-12-23 2010-07-21 新奥科技发展有限公司 Equipment and method for treating nondegradable wastewater by utilizing catalytic oxidation of ozone

Patent Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH0364393A (en) * 1989-08-02 1991-03-19 Nkk Corp Remote driving of coke guide car
JPH09164393A (en) * 1995-12-18 1997-06-24 Meidensha Corp Treatment of hardly-decomposable matter contained in return water
JP2000176468A (en) * 1998-12-11 2000-06-27 Ataka Construction & Engineering Co Ltd Sewage treatment and device therefor
EP1234802A1 (en) * 1999-10-28 2002-08-28 Kazuto Hashizume Improved method and apparatus for water treatment
CN101327985A (en) * 2008-07-31 2008-12-24 哈尔滨工业大学 A method for catalytic ozonation to remove organic pollutants in water
CN101781036A (en) * 2009-12-23 2010-07-21 新奥科技发展有限公司 Equipment and method for treating nondegradable wastewater by utilizing catalytic oxidation of ozone

Cited By (14)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102583814B (en) * 2012-01-18 2013-10-02 马放 Method for processing heavy alkylbenzene sulfonate waste water
CN102583814A (en) * 2012-01-18 2012-07-18 马放 Method for processing heavy alkylbenzene sulfonate waste water
CN105439311A (en) * 2014-08-12 2016-03-30 北京朗新明环保科技有限公司 Coal chemical industrial wastewater deep treatment apparatus and method
CN104193118A (en) * 2014-09-25 2014-12-10 无锡昊瑜节能环保设备有限公司 Printing and dyeing wastewater recycling device and wastewater purification method
CN106492785A (en) * 2016-08-31 2017-03-15 浙江奇彩环境科技股份有限公司 A kind of catalyst and its method of wastewater treatment for dye wastewater treatment
CN107265725B (en) * 2017-08-18 2020-11-27 上海海洋大学 A kind of ozone treatment method of pig farm sewage used for microalgae cultivation
CN107265725A (en) * 2017-08-18 2017-10-20 上海海洋大学 A kind of ozone treatment method of wastewater from pig farm for both culturing microalgae
CN107364943A (en) * 2017-09-10 2017-11-21 杭州东日节能技术有限公司 Catalytic wet oxidation administers the device and its technique of hydrochloric organic wastewater
CN108275848A (en) * 2018-03-27 2018-07-13 中节能工程技术研究院有限公司 A kind of wastewater treatment integrating device and method
CN108585336A (en) * 2018-05-23 2018-09-28 上海邵雍环境科技有限公司 The processing method of glyphosate mother solution wet oxidation sequential catalyst wet oxidation
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