[go: up one dir, main page]

CN1303000C - Method and apparatus for treating waste water by microwave photocatalysis - Google Patents

Method and apparatus for treating waste water by microwave photocatalysis Download PDF

Info

Publication number
CN1303000C
CN1303000C CNB2004100659797A CN200410065979A CN1303000C CN 1303000 C CN1303000 C CN 1303000C CN B2004100659797 A CNB2004100659797 A CN B2004100659797A CN 200410065979 A CN200410065979 A CN 200410065979A CN 1303000 C CN1303000 C CN 1303000C
Authority
CN
China
Prior art keywords
waste water
microwave
reaction chamber
wastewater
electrodeless lamp
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Expired - Fee Related
Application number
CNB2004100659797A
Other languages
Chinese (zh)
Other versions
CN1654338A (en
Inventor
洪军
孙成
钟明
刘亚子
周芳
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Nanjing University
Original Assignee
Nanjing University
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Nanjing University filed Critical Nanjing University
Priority to CNB2004100659797A priority Critical patent/CN1303000C/en
Publication of CN1654338A publication Critical patent/CN1654338A/en
Application granted granted Critical
Publication of CN1303000C publication Critical patent/CN1303000C/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

Links

Images

Landscapes

  • Physical Water Treatments (AREA)

Abstract

本发明公开了一种微波光催化处理废水的方法与装置。要处理废水需格栅除杂、静置沉淀、pH调节,经上述初步处理后进入微波光催化处理废水的装置,进行微波光催化。装置包括微波反应炉、废水反应室和无电极灯,微波反应炉腔中安放废水反应室,废水反应室内壁的凸柱上架设环形固定器,无电极灯插入环形固定器的小孔中,石英搅拌器置于废水反应室中,石英搅拌器中轴经废水反应室上部和微波反应炉上部的开口与外部旋转电机相连。本发明可延长无电极灯使用寿命,提高光催化降解效率;该装置简单,占地面积少、能耗少;综合了微波作用与紫外—可见光、催化剂的光催化氧化技术,对有机物浓度小于100mg/L的废水,去除率达90%以上。

Figure 200410065979

The invention discloses a method and a device for microwave photocatalytic treatment of wastewater. To treat waste water, it is necessary to remove impurities by grille, settle and adjust pH. After the above preliminary treatment, it enters the device for microwave photocatalytic treatment of waste water for microwave photocatalysis. The device includes a microwave reaction furnace, a waste water reaction chamber and an electrodeless lamp. The waste water reaction chamber is placed in the microwave reaction furnace cavity, and a circular holder is erected on the convex column on the wall of the waste water reaction chamber. The electrodeless lamp is inserted into the small hole of the ring holder, and the quartz The stirrer is placed in the waste water reaction chamber, and the central shaft of the quartz stirrer is connected with the external rotating motor through openings in the upper part of the waste water reaction chamber and the upper part of the microwave reaction furnace. The invention can prolong the service life of the electrodeless lamp and improve the efficiency of photocatalytic degradation; the device is simple, occupies less floor area, and consumes less energy; it integrates microwave action, ultraviolet-visible light, and catalyst photocatalytic oxidation technology, and the concentration of organic matter is less than 100mg /L of wastewater, the removal rate is over 90%.

Figure 200410065979

Description

微波光催化处理废水的方法与装置Method and device for microwave photocatalytic treatment of wastewater

一、技术领域1. Technical field

本发明涉及废水处理的方法及装置,具体而言,是利用微波、微波激发无电极灯产生的紫外-可见光、负载纳米催化剂处理废水的一种方法和装置。The invention relates to a method and a device for wastewater treatment, in particular to a method and a device for treating wastewater by using microwaves, microwaves to excite ultraviolet-visible light generated by electrodeless lamps, and loading nanometer catalysts.

二、背景技术2. Background technology

当前,进入环境、特别是水体中的污染物种类和数量越来越多,有毒有害、三致、难降解的有机污染物已严重的威胁人类的生存。目前,各种消除污染的化学、物理、生物的方法很多,这些方法针对不同类型的污染物以及污染控制要求分别显示出了各自的优势。然而,总体来看,传统的处理技术有些只能使污染物转移,产生严重的二次污染;有些适应性差,当污染物浓度过高或过低时往往无能为力;而各种新的污染处理与控制方法,虽为有机污染物的去除提供了一些独到的技术,如液液萃取法、大孔吸附树脂法、膜分离法、超声波法等,但目前我国造纸、印染、制药、石化等行业及垃圾堆放场仍然有大量的有毒有机废水排出,并且缺乏高效的、彻底的处理方法。At present, the types and quantities of pollutants entering the environment, especially water bodies, are increasing. Toxic, harmful, tertiary and refractory organic pollutants have seriously threatened the survival of human beings. At present, there are many chemical, physical, and biological methods for eliminating pollution. These methods have shown their own advantages for different types of pollutants and pollution control requirements. However, generally speaking, some traditional treatment technologies can only transfer pollutants and cause serious secondary pollution; some have poor adaptability, and are often powerless when the concentration of pollutants is too high or too low; Although the control method provides some unique technologies for the removal of organic pollutants, such as liquid-liquid extraction method, macroporous adsorption resin method, membrane separation method, ultrasonic method, etc., at present, my country's papermaking, printing and dyeing, pharmaceutical, petrochemical and other industries and There is still a large amount of toxic organic wastewater discharged from the garbage dump, and there is a lack of efficient and thorough treatment methods.

当前,微波技术受到人们的普遍重视。微波是频率300MHz~3006Hz的电磁波。微波作用于物质的方式十分特殊。首先,微波是对物质分子水平上的直接作用,由微波场引起物质分子的“变极效应”,使加热更加迅速(热效应);同时,大大增加了反应物分子间的碰撞几率,使反应活性增加(非热效应)。其次,微波作用具有选择性。微波加热时,极性物质很快升温,而非极性物质则不吸收或透过微波。微波已广泛应用于环境科学领域,如微波已成功用于环境样品的消解及饮用水的灭菌等,也有利用微波和外置紫外灯光降解有机污染物的技术,其中,紫外光是一种对有机物降解十分有效的能源,由于紫外线具有较高的能量,能够使大部分化学键发生断裂,或是与催化剂结合,产生活性物质,从而将有机污染物转变为二氧化碳和水,达到去污的目的。但是,这些方法的能耗大,设备复杂,同时,在降解目标污染物时,可能又带入新的污染。At present, microwave technology is generally paid attention to by people. Microwaves are electromagnetic waves with a frequency of 300MHz to 3006Hz. Microwaves act on matter in a very special way. First of all, microwave is a direct effect on the molecular level of the substance. The "polarization effect" of the substance molecule is caused by the microwave field, which makes the heating more rapid (thermal effect); at the same time, it greatly increases the collision probability between the reactant molecules and makes the reactivity increase (non-thermal effect). Second, microwave action is selective. When heated by microwaves, polar substances heat up quickly, while non-polar substances do not absorb or transmit microwaves. Microwaves have been widely used in the field of environmental science. For example, microwaves have been successfully used in the digestion of environmental samples and the sterilization of drinking water. There are also technologies that use microwaves and external ultraviolet light to degrade organic pollutants. Among them, ultraviolet light is a The degradation of organic matter is a very effective energy source. Due to the high energy of ultraviolet rays, it can break most of the chemical bonds, or combine with catalysts to produce active substances, thereby converting organic pollutants into carbon dioxide and water to achieve the purpose of decontamination. However, these methods consume a lot of energy, and the equipment is complicated. At the same time, when degrading the target pollutants, new pollution may be introduced.

近年来,有学者利用微波激发无电极灯产生紫外光来处理废水,如“微波-无极紫外光催化氧化水处理方法”(公开号CN 1482072A),无极紫外灯应用于染料废水的降解(孟祥周等.无极紫外光降解活性艳蓝KN-R染料溶液的研究.武汉科技学院学报,2003,16(5):32~36),40mg/L活性艳蓝KN-R处理110min后,脱色率为73%,TOC去除34%。这种方法的优点在于,可产生紫外光的无电极灯并不需要额外的电源提供能量,而且,微波与紫外光协同作用的装置简单、易行。但是,这种无电极灯受微波激发时闪烁不定,发光效率不高,光强较小,降解所需时间较长;而且,无电极灯受激发后的温度可达到700~1400K,如不进行及时有效的降温,所激发的谱线将因自吸而变宽,并且缩短无电极灯的寿命。In recent years, some scholars have used microwaves to excite electrodeless lamps to generate ultraviolet light to treat wastewater, such as "Microwave-Infinite Ultraviolet Photocatalytic Oxidation Water Treatment Method" (public number CN 1482072A), and electrodeless ultraviolet lamps are used in the degradation of dye wastewater (Meng Xiangzhou et al. .Research on the degradation of reactive brilliant blue KN-R dye solution by infinite ultraviolet light. Journal of Wuhan Institute of Science and Technology, 2003, 16 (5): 32~36), after 40mg/L reactive brilliant blue KN-R was treated for 110min, the decolorization rate was 73 %, TOC removal 34%. The advantage of this method is that the electrodeless lamp that can generate ultraviolet light does not need an additional power source to provide energy, and the device for the synergistic effect of microwave and ultraviolet light is simple and easy to implement. However, when this electrodeless lamp is excited by microwaves, it flickers indefinitely, the luminous efficiency is not high, the light intensity is small, and it takes a long time to degrade; moreover, the temperature of the electrodeless lamp after being excited can reach 700-1400K. Timely and effective cooling, the excited spectral line will be broadened due to self-absorption, and the life of the electrodeless lamp will be shortened.

三、发明内容3. Contents of the invention

1、发明目的1. Purpose of the invention

本发明提供一种微波光催化处理废水的方法与装置,利用微波、微波激发无电极灯产生紫外-可见光、负载纳米催化剂光催化氧化废水中的有机污染物,为难降解有毒有机废水净化提供有效的方法和装置。The invention provides a method and device for microwave photocatalytic treatment of waste water, which uses microwaves and microwaves to excite electrodeless lamps to generate ultraviolet-visible light, and supports nano-catalysts to photocatalyze and oxidize organic pollutants in waste water, providing an effective solution for the purification of refractory toxic organic waste water. Methods and Apparatus.

2、技术方案2. Technical solution

本发明提出了微波光催化处理废水的方法和装置。微波光催化处理废水的方法,包括格栅除杂、静置沉淀、pH调节,废水经上述初步处理后进入微波光催化处理废水的装置,进行微波光催化。The invention provides a method and a device for microwave photocatalytic treatment of wastewater. The method for microwave photocatalytic treatment of wastewater includes grid removal, static precipitation, and pH adjustment. After the above preliminary treatment, the wastewater enters a microwave photocatalytic wastewater treatment device for microwave photocatalysis.

废水的pH值要控制在2~10之间,超出范围的,需用酸碱进行pH调节。酸碱调节溶液pH范围为2~10。废水的微波光催化处理在微波光催化处理废水的装置中进行,水流方向采取下进上出或上进下出的方式;废水在微波光催化反应器中的停留时间为20~40分钟,废水溶液的温度保持在100℃以下,压力为常压:微波光催化的纳米催化剂为半导体材料TiO2、ZnO、CdS,或是半导体材料掺杂Cu、Fe、Ag、Cd、Zn、Mn、Co、Ni等氧化物的复合催化剂,掺杂金属氧化物的质量百分比为0.1%~5.0%,纳米催化剂的制备采用溶胶-凝胶法、化学气相沉积法和溶液静置法等。The pH value of the wastewater should be controlled between 2 and 10. If it exceeds the range, it needs to be adjusted with acid and alkali. The pH range of the acid-base adjustment solution is 2-10. The microwave photocatalytic treatment of wastewater is carried out in the device for microwave photocatalytic treatment of wastewater. The temperature is kept below 100°C, and the pressure is normal pressure: the nano-catalysts for microwave photocatalysis are semiconductor materials TiO 2 , ZnO, CdS, or semiconductor materials doped with Cu, Fe, Ag, Cd, Zn, Mn, Co, Ni The composite catalyst of equal oxides is doped with metal oxides in a mass percentage of 0.1% to 5.0%. The nano-catalyst is prepared by sol-gel method, chemical vapor deposition method and solution standing method.

微波光催化处理废水的方法,其工作原理为:微波激发无电极灯产生紫外-可见光,经照射纳米催化剂膜表面后生成高电位的·OH或·OOH,并氧化有机污染物;或者激发产生的紫外-可见光直接对有机物进行光降解,实现废水的净化。The method of microwave photocatalytic treatment of wastewater, its working principle is: the microwave excites the electrodeless lamp to generate ultraviolet-visible light, and generates high-potential OH or OOH after irradiating the surface of the nano-catalyst film, and oxidizes organic pollutants; or excites the generated Ultraviolet-visible light directly degrades organic matter and realizes the purification of wastewater.

上述的微波光催化处理废水的装置,包括微波反应炉、废水反应室和无电极灯,微波反应炉腔中安放废水反应室,废水反应室内壁的凸柱上架设环形固定器,无电极灯插入环形固定器的小孔中,石英搅拌器置于废水反应室中,石英搅拌器中轴经废水反应室上部和微波反应炉上部的开口与外部旋转电机相连。The above-mentioned device for treating waste water by microwave photocatalysis includes a microwave reaction furnace, a waste water reaction chamber and an electrodeless lamp. A quartz stirrer is placed in the waste water reaction chamber in the small hole of the annular fixer, and the central axis of the quartz stirrer is connected with the external rotating motor through openings in the upper part of the waste water reaction chamber and the upper part of the microwave reaction furnace.

本发明提出的微波光催化处理废水的装置,微波反应炉两侧壁内置有波导器和5~20个磁控管,每个磁控管的功率为0.5~2.0kW,微波反应炉内壁采用不锈钢材料或含镍、铝的材料;废水反应室容器为透过微波的材料,采用聚四氟乙烯、聚苯乙烯、陶瓷等材质,容器上盖为可拆式开口盖;废水反应室内壁凸起有3~9个凸柱,凸柱上放置环形固定器,用以固定无电极灯;环形固定器采用不吸收紫外光的石英材料,环形固定器上有4~8个大小合适的小孔;石英搅拌器为-同轴多页石英板,石英板上负载纳米催化剂,石英搅拌器不但具有搅拌作用,还有催化剂载体和可透过紫外光、提高光利用率的功能;微波无电极灯为石英中空的圆柱体或长方体,无电极灯的底圆直径与环行固定器上的小孔直径相一致,其高度不低于废水反应室高度的2/3;无电极灯的制作工艺为抽空气至2.5~5.0kPa后,充入0.5~2.0kPa氩气或氦气,并滴加金属汞1~5滴,最后密封;废水反应室的进水口和出水口与聚四氟乙烯水管相连;微波反应炉侧面和上部的开口处均裹有铝套。In the microwave photocatalytic waste water treatment device proposed by the present invention, waveguides and 5-20 magnetrons are built in the two side walls of the microwave reaction furnace, the power of each magnetron is 0.5-2.0kW, and the inner wall of the microwave reaction furnace is made of stainless steel. materials or materials containing nickel and aluminum; the waste water reaction chamber container is made of microwave-permeable materials such as polytetrafluoroethylene, polystyrene, ceramics, etc., and the upper cover of the container is a detachable opening cover; the inner wall of the waste water reaction chamber is raised There are 3 to 9 convex pillars, and a ring holder is placed on the boss to fix the electrodeless lamp; the ring holder is made of quartz material that does not absorb ultraviolet light, and there are 4 to 8 small holes of appropriate size on the ring holder; The quartz stirrer is a coaxial multi-page quartz plate, and the nano-catalyst is loaded on the quartz plate. The quartz stirrer not only has the function of stirring, but also has the function of catalyst carrier and can transmit ultraviolet light and improve the light utilization rate; the microwave electrodeless lamp is Quartz hollow cylinder or cuboid, the diameter of the bottom circle of the electrodeless lamp is consistent with the diameter of the small hole on the ring holder, and its height is not less than 2/3 of the height of the wastewater reaction chamber; the manufacturing process of the electrodeless lamp is to pump air After reaching 2.5-5.0kPa, fill it with 0.5-2.0kPa argon or helium gas, and drop 1-5 drops of metallic mercury, and finally seal it; the water inlet and outlet of the wastewater reaction chamber are connected with polytetrafluoroethylene water pipes; microwave The side and upper openings of the reaction furnace are covered with aluminum sleeves.

有益效果Beneficial effect

本发明与现有技术相比,将微波无电极灯浸于废水溶液中,使其表面温度始终保持在100℃(水的沸点)以下,可延长无电极灯使用寿命,且无电极灯产生的紫外-可见光直接作用于有机废水,能提高光催化降解效率;该装置简单,占地面积少,反应压力为常压,能耗少;综合了微波作用与紫外-可见光、催化剂的光催化氧化技术,能够催化降解有毒有害、用常规方法难以降解的有机污染物,特别是酚类、染料、激素、农药等,对有机物浓度小于100mg/L的废水,去除率达90%以上。Compared with the prior art, the present invention immerses the microwave electrodeless lamp in the waste water solution to keep its surface temperature below 100°C (the boiling point of water), which can prolong the service life of the electrodeless lamp, and the electrodeless lamp produces The ultraviolet-visible light directly acts on the organic wastewater, which can improve the efficiency of photocatalytic degradation; the device is simple, occupies a small area, the reaction pressure is normal pressure, and consumes less energy; the photocatalytic oxidation technology integrating microwave action, ultraviolet-visible light and catalyst , can catalyze the degradation of toxic and harmful organic pollutants that are difficult to degrade by conventional methods, especially phenols, dyes, hormones, pesticides, etc., and the removal rate of organic matter concentration is less than 100mg/L in wastewater. The removal rate is over 90%.

四、附图说明4. Description of drawings

图1是本发明方法流程示意图。Fig. 1 is a schematic flow chart of the method of the present invention.

图2是本发明装置剖视图。Fig. 2 is a sectional view of the device of the present invention.

图3是石英搅拌器结构示意图。Fig. 3 is a schematic diagram of the structure of a quartz stirrer.

图4是环形固定器俯视图。Fig. 4 is a top view of the ring fixer.

五、具体实施方式5. Specific implementation

以下通过实例进一步说明。The following is further illustrated by examples.

实施例1Example 1

配制50mg/L间硝基苯酚水溶液模拟含酚废水,无需格栅除杂,静置后调节溶液pH3~7,含酚废水经流量计[4]及泵[5]以1.5L/min的流速进入25L的废水反应室[11],速度控制在使废水反应室[11]内的废水停留15~20分钟,水流方向为上进下出的方式。微波功率1000W,位于微波场中的4根无电极灯[17]受到微波激发后,产生紫外-可见光,利用溶胶-凝胶法负载在石英搅拌器[13]上的Ti02纳米催化剂受到紫外-可见光照射,同时,石英搅拌器[13]在电机[12]带动下以30r/m的速度旋转,此时,含酚废水溶液同时受到微波、紫外-可见光以及TiO2纳米催化剂的作用。废水反应室[11]中产生的蒸气通过上部开口排出,浸于废水中的无电极灯[17]温度小于100℃。经废水出口[19]排出的间硝基苯酚浓度小于5mg/L,TOC减少76%。Prepare a 50 mg/L m-nitrophenol aqueous solution to simulate phenol-containing wastewater, without needing a grid to remove impurities. After standing still, adjust the pH of the solution to 3-7. The phenol-containing wastewater passes through the flow meter [4] and the pump [5] at a flow rate of 1.5 L/min Enter the 25L waste water reaction chamber [11], the speed is controlled so that the waste water in the waste water reaction chamber [11] stays for 15 to 20 minutes, and the water flow direction is the way of going in and out. The microwave power is 1000W, and the four electrodeless lamps [17] located in the microwave field are excited by the microwave to generate ultraviolet-visible light. The Ti0 2 nanocatalyst loaded on the quartz stirrer [13] by the sol-gel method is exposed to the ultraviolet-visible light. Visible light irradiation, at the same time, the quartz agitator [13] is driven by the motor [12] to rotate at a speed of 30r/m. At this time, the phenolic wastewater solution is simultaneously affected by microwaves, ultraviolet-visible light and TiO2 nano catalysts. The steam generated in the wastewater reaction chamber [11] is discharged through the upper opening, and the temperature of the electrodeless lamp [17] immersed in the wastewater is lower than 100°C. The m-nitrophenol concentration discharged through the wastewater outlet [19] is less than 5mg/L, and the TOC is reduced by 76%.

实施例2Example 2

配制50mg/L若丹明-B水溶液模拟染料废水,调节pH值为3~7,静置后经流量计[4]及泵[5]以1L/min的流速进入25L的废水反应室[11],速度控制在使反应室内的废水停留25~30分钟,水流方向为上进下出的方式。微波功率1500W,安置于反应室中的6根无电极灯[17]受到微波激发后,产生紫外-可见光,石英搅拌器[13]上负载Mn/TiO2催化剂,掺杂量0.5%,石英搅拌器在外部电机[12]带动下以20r/min的速度旋转。废水反应室中的温度小于100℃,常压。经废水出口排出的废水中若丹明-B的浓度小于10mg/L,TOC减少70%。将排出的废水经回流再处理[8],其余步骤同前,出水经检测,剩余若丹明-B小于1mg/L,剩余TOC减少至初始浓度的5%。Prepare 50mg/L rhodamine-B aqueous solution to simulate dye wastewater, adjust the pH value to 3-7, and after standing still, enter the 25L wastewater reaction chamber at a flow rate of 1L/min through the flow meter [4] and pump [5] [11 ], the speed is controlled so that the wastewater in the reaction chamber stays for 25 to 30 minutes, and the direction of water flow is in the way of going up and down. The microwave power is 1500W, and the 6 electrodeless lamps [17] placed in the reaction chamber are excited by the microwave to generate ultraviolet-visible light. The Mn/TiO 2 catalyst is loaded on the quartz stirrer [13], the doping amount is 0.5%, and the quartz stirrer [13] is loaded with Mn/TiO2 catalyst. The device rotates at a speed of 20r/min driven by an external motor [12]. The temperature in the waste water reaction chamber is less than 100°C and normal pressure. The rhodamine-B concentration in the wastewater discharged through the wastewater outlet is less than 10mg/L, and the TOC is reduced by 70%. The discharged wastewater was refluxed and reprocessed [8], and the rest of the steps were the same as before. The effluent was tested, and the remaining rhodamine-B was less than 1 mg/L, and the remaining TOC was reduced to 5% of the initial concentration.

实施例3Example 3

配制40mg/L双酚A水溶液模拟含环境激素废水,调节pH3~7,静置后经流量计[4]及泵[5]以1L/min的流速进入25L的废水反应室[11],速度控制在使反应室内的废水停留25~30分钟,水流方向为上进下出的方式。微波功率1500W,安置于反应室中6根无电极灯[17]受到微波激发后,产生紫外-可见光,石英搅拌器[13]上负载的Ni/TiO2催化剂(掺杂量0.5%)受到紫外-可见光的照射,同时,石英搅拌器在外部电机[12]带动下以20r/min的速度旋转。废水反应室中的温度小于100℃,常压。经废水出口排出的废水中双酚A的浓度为10mg/L左右,TOC减少50%。将排出的废水经回流再处理[8],其余步骤同前,出水经检测,剩余双酚A2mg/L,剩余TOC为初始浓度的8%。Prepare a 40mg/L bisphenol A aqueous solution to simulate wastewater containing environmental hormones, adjust the pH to 3-7, and after standing still, enter the 25L wastewater reaction chamber [11] at a flow rate of 1L/min through a flow meter [4] and a pump [5]. Control the waste water in the reaction chamber to stay for 25 to 30 minutes, and the direction of water flow is in the way of going up and down. The microwave power is 1500W, and the 6 electrodeless lamps [17] placed in the reaction chamber are excited by microwaves to generate ultraviolet-visible light. - Irradiation of visible light, at the same time, the quartz stirrer is driven by an external motor [12] to rotate at a speed of 20r/min. The temperature in the waste water reaction chamber is less than 100°C and normal pressure. The concentration of bisphenol A in the wastewater discharged from the wastewater outlet is about 10mg/L, and the TOC is reduced by 50%. The discharged waste water was refluxed and reprocessed [8], and the rest of the steps were the same as before. After the effluent was tested, the remaining bisphenol A was 2 mg/L, and the remaining TOC was 8% of the initial concentration.

实施例4Example 4

配制30mg/L阿特拉津水溶液模拟农药废水,无需过滤,调节pH 3~7,静置后经流量计[4]及泵[5]以1L/min的流速进入25L的废水反应室[11],废水在反应室内的停留时间为25~30分钟,水流方向为上进下出的方式。微波功率1500W,已安置于反应室中6根无电极灯[17]受到微波激发后,产生紫外-可见光,石英搅拌器[13]上负载的Co/TiO2催化剂(掺杂量1.0%)受到紫外-可见光的照射,同时,石英搅拌器在外部电机[12]带动下以20r/m的速度旋转,此时,含农药废水溶液同时受到微波、紫外-可见光以及Co/TiO2催化剂的作用。废水反应室中的温度小于100℃,常压。经废水出口排出的废水中阿特拉津的浓度小于5mg/L,TOC减少60%。将排出的废水经回流再处理[8],其余方法同前,出水经检测,无阿特拉津剩余,剩余TOC为初始浓度的5%。Prepare 30mg/L atrazine aqueous solution to simulate pesticide wastewater without filtering, adjust the pH to 3-7, and after standing still, enter the 25L wastewater reaction chamber at a flow rate of 1L/min through the flow meter [4] and pump [5] [11 ], the residence time of wastewater in the reaction chamber is 25-30 minutes, and the direction of water flow is the way of going in and out from top to bottom. The microwave power is 1500W, and 6 electrodeless lamps [17] placed in the reaction chamber are excited by microwaves to generate ultraviolet -visible light. Under the irradiation of ultraviolet-visible light, at the same time, the quartz stirrer is driven by an external motor [12] to rotate at a speed of 20r/m. At this time, the pesticide-containing wastewater solution is simultaneously subjected to microwave, ultraviolet-visible light and Co/TiO 2 catalyst. The temperature in the waste water reaction chamber is less than 100°C and normal pressure. The concentration of atrazine in the wastewater discharged through the wastewater outlet is less than 5mg/L, and the TOC is reduced by 60%. The discharged wastewater was refluxed for retreatment [8], and the remaining methods were the same as before. The effluent was tested and found that there was no atrazine remaining, and the remaining TOC was 5% of the initial concentration.

实施例5Example 5

某实验室混合废水,主要成份为苯酚、对氯苯酚、间硝基苯酚、甲基橙、若丹明-B、双酚A、壬基酚、阿特拉津、对硫磷,处理前TOC为82mg/L,经格栅除杂,静置后,调节pH3~7,清夜经流量计[4]及泵[5]以1L/min的流速进入25L的废水反应室[11],废水在反应室内停留25~30分钟,水流方向为上进下出的方式。微波功率3000W,环行固定器上插入8根无电极灯[17],石英搅拌器[13]上负载Cu/TiO2催化剂,掺杂量1.0%,同时,石英搅拌器在电机[12]带动下以20r/m的速度旋转。废水反应室中的温度小于100℃,常压。经废水出口排出的废水,TOC减少65%。将排出的废水经回流再处理[8]一次,剩余TOC为初始溶液TOC的6%。A laboratory mixed wastewater, the main components are phenol, p-chlorophenol, m-nitrophenol, methyl orange, rhodamine-B, bisphenol A, nonylphenol, atrazine, parathion, TOC before treatment It is 82mg/L, and the impurity is removed by the grid. After standing still, the pH is adjusted to 3~7, and the flow meter [4] and the pump [5] enter the 25L wastewater reaction chamber [11] at a flow rate of 1L/min in the clear night. Stay in the reaction chamber for 25 to 30 minutes, and the direction of water flow is in the way of up and down. The microwave power is 3000W, 8 electrodeless lamps [17] are inserted into the circular holder, Cu/TiO 2 catalyst is loaded on the quartz stirrer [13], and the doping amount is 1.0%. At the same time, the quartz stirrer is driven by the motor [12] Rotate at a speed of 20r/m. The temperature in the waste water reaction chamber is less than 100°C and normal pressure. The TOC of the wastewater discharged through the wastewater outlet is reduced by 65%. The discharged waste water is refluxed and reprocessed [8] once, and the remaining TOC is 6% of the TOC of the initial solution.

实施例6Example 6

某造纸厂废水,处理前pH=13,TOC大于100mg/L,经格栅除杂[1],静置沉淀[2],清水稀释溶液TOC至70mg/L,pH调节[3]调节溶液pH值为3~7,经流量计[4]及泵[5]以1L/min的流速进入微波光催化处理废水的装置中25L的废水反应室[11],废水在反应室内停留25~30分钟,水流方向为上进下出的方式。微波功率3000W,环行固定器上插入8根无电极灯[17],石英搅拌器[13]上负载Cu/TiO2催化剂,掺杂量1.0%,同时,石英搅拌器在电机[12]带动下以20r/m的速度旋转。废水反应室中的温度小于100℃,常压。经废水出口进行出水排放[7],TOC减少50%。将排出的废水经回流再处理[8]一次,剩余TOC10mg/L。Wastewater from a paper mill, pH = 13 before treatment, TOC greater than 100mg/L, impurity removal through grids [1], static precipitation [2], dilute solution TOC to 70mg/L with water, pH adjustment [3] to adjust the pH of the solution The value is 3 to 7, and the flow rate of 1L/min enters the 25L wastewater reaction chamber [11] of the microwave photocatalytic wastewater treatment device through the flow meter [4] and the pump [5], and the wastewater stays in the reaction chamber for 25 to 30 minutes , the direction of water flow is the way of up-in and down-out. The microwave power is 3000W, 8 electrodeless lamps [17] are inserted into the circular holder, Cu/TiO 2 catalyst is loaded on the quartz stirrer [13], and the doping amount is 1.0%. At the same time, the quartz stirrer is driven by the motor [12] Rotate at a speed of 20r/m. The temperature in the waste water reaction chamber is less than 100°C and normal pressure. The effluent is discharged through the wastewater outlet [7], and the TOC is reduced by 50%. The discharged waste water is refluxed and reprocessed [8] once, and the remaining TOC is 10mg/L.

实施例7Example 7

微波光催化处理废水的装置,包括微波反应炉[10]、废水反应室[11]和无电极灯[17],微波反应炉[10]腔中安放废水反应室[11],废水反应室[11]内壁的凸柱[18]上架设环形固定器[14],无电极灯[17]插入环形固定器[14]的小孔中,石英搅拌器[13]置于废水反应室[11]中,石英搅拌器[13]中轴经废水反应室[11]上部和微波反应炉[10]上部的开口与外部旋转电机[12]相连。微波反应炉[10]两侧壁内置有波导器[16]和10个磁控管[15],每个磁控管的功率为1kW,无电极灯高度为废水反应室[11]高度的1/2。石英搅拌器[13]为一同轴多页石英板,置于环行固定器的空心圆中央,其轴通过废水反应室[11]和微波反应炉[10]上部的开口与旋转电机[12]相连。废水反应室内壁凸起有6个凸柱[18],废水反应室上盖为可拆式开口盖,环形固定器[14]上有6个小孔,无电极灯[17]插入环形固定器[14]的小孔中。无电极灯[17]的制作方法为抽空气至2.5~5.0kPa后,充入0.5~2.0kPa氩气、氦气等惰性气体,并滴加金属汞1~10滴,最后密封。废水反应室[11]为聚四氟乙烯、聚苯乙烯、陶瓷等耐热、耐腐蚀材料,微波反应炉[10]内壁采用不锈钢材料或含镍、铝的材料。A device for microwave photocatalytic treatment of wastewater, including a microwave reaction furnace [10], a wastewater reaction chamber [11] and an electrodeless lamp [17]. 11] An annular holder [14] is erected on the convex column [18] of the inner wall, the electrodeless lamp [17] is inserted into the small hole of the annular holder [14], and the quartz agitator [13] is placed in the waste water reaction chamber [11] Among them, the central shaft of the quartz agitator [13] is connected to the external rotating motor [12] through the openings on the upper part of the waste water reaction chamber [11] and the upper part of the microwave reaction furnace [10]. There are waveguides [16] and 10 magnetrons [15] built in the two side walls of the microwave reaction furnace [10], the power of each magnetron is 1 kW, and the height of the electrodeless lamp is 1 /2. The quartz stirrer [13] is a coaxial multi-page quartz plate, placed in the center of the hollow circle of the ring holder, and its axis passes through the opening of the waste water reaction chamber [11] and the upper part of the microwave reaction furnace [10] and the rotating motor [12]. connected. There are 6 protrusions [18] on the inner wall of the wastewater reaction chamber, the upper cover of the wastewater reaction chamber is a detachable opening cover, and there are 6 small holes on the ring holder [14], and the electrodeless lamp [17] is inserted into the ring holder [14] in the small hole. The manufacturing method of the electrodeless lamp [17] is to pump the air to 2.5-5.0kPa, fill it with 0.5-2.0kPa argon, helium and other inert gases, add 1-10 drops of metallic mercury, and finally seal it. The wastewater reaction chamber [11] is heat-resistant and corrosion-resistant materials such as polytetrafluoroethylene, polystyrene, pottery, etc., and the inner wall of the microwave reaction furnace [10] is made of stainless steel or materials containing nickel and aluminum.

Claims (10)

1.一种微波光催化处理废水的方法,包括格栅除杂、静置沉淀、pH调节,其特征在于废水经上述初步处理后进入微波光催化处理废水的装置,进行微波光催化,在所述微波光催化处理废水的装置中,废水的温度保持在100℃以下,微波激发无电极灯产生紫外-可见光,并照射纳米催化剂,实现废水的净化。1. A method for microwave photocatalytic treatment of waste water, comprising grid impurity removal, static precipitation, pH adjustment, characterized in that waste water enters the device for microwave photocatalytic treatment of waste water after the above-mentioned preliminary treatment, and carries out microwave photocatalysis, in place In the microwave photocatalytic waste water treatment device, the temperature of the waste water is kept below 100°C, and the microwave excites the electrodeless lamp to generate ultraviolet-visible light, and irradiates the nano-catalyst to realize the purification of the waste water. 2.根据权利要求1所述的方法,其特征在于废水的pH值控制在2~10,超出范围的,用酸碱进行pH调节。2. The method according to claim 1, characterized in that the pH value of the waste water is controlled at 2 to 10, and if it exceeds the range, the pH value is adjusted with acid and alkali. 3.根据权利要求2所述的方法,其特征在于废水在微波光催化处理废水的装置中的停留时间为20~40分钟,压力为常压。3. The method according to claim 2, characterized in that the residence time of the waste water in the device for microwave photocatalytic treatment of waste water is 20 to 40 minutes, and the pressure is normal pressure. 4.根据权利要求1~3中任一项所述的方法,其特征在于微波光催化的纳米催化剂为纯半导体材料TiO2、ZnO或CdS,或是所述纯半导体材料掺杂金属氧化物的复合催化剂,掺杂金属氧化物的质量百分比为0.1%~5.0%,所述金属氧化物为Cu、Fe、Ag、Cd、Zn、Mn、Co或Ni的金属氧化物。4. The method according to any one of claims 1 to 3, characterized in that the nano-catalyst of microwave photocatalysis is pure semiconductor material TiO 2 , ZnO or CdS, or the pure semiconductor material doped with metal oxide The composite catalyst is doped with a metal oxide in a mass percentage of 0.1% to 5.0%, and the metal oxide is a metal oxide of Cu, Fe, Ag, Cd, Zn, Mn, Co or Ni. 5.根据权利要求1所述的方法,其中所述的微波光催化处理废水的装置,包括微波反应炉[10]、废水反应室[11]和无电极灯[17],其特征在于微波反应炉[10]腔中安放废水反应室[11],废水反应室[11]内壁的凸柱[18]上架设环形固定器[14],无电极灯[17]插入环形固定器[14]的小孔中,石英搅拌器[13]置于废水反应室[11]中,石英搅拌器[13]中轴经废水反应室[11]上部和微波反应炉[10]上部的开口与外部旋转电机[12]相连。5. The method according to claim 1, wherein said device for microwave photocatalytic treatment of waste water comprises a microwave reaction furnace [10], a waste water reaction chamber [11] and an electrodeless lamp [17], and is characterized in that the microwave reaction The waste water reaction chamber [11] is placed in the cavity of the furnace [10], and the ring holder [14] is erected on the convex column [18] of the inner wall of the waste water reaction chamber [11], and the electrodeless lamp [17] is inserted into the ring holder [14]. In the small hole, the quartz agitator [13] is placed in the waste water reaction chamber [11], and the central axis of the quartz agitator [13] passes through the upper part of the waste water reaction chamber [11] and the upper part of the microwave reaction furnace [10] and the external rotating motor [12] connected. 6.根据权利要求5所述的方法,其特征在于微波反应炉[10]两侧壁内置有波导器[16]和5~20个磁控管[15],每个磁控管的功率为0.5~2.0kW,无电极灯高度不低于废水反应室[11]高度的2/3。6. method according to claim 5 is characterized in that waveguide [16] and 5~20 magnetrons [15] are built-in in microwave reactor [10] two side walls, and the power of each magnetron is 0.5 ~ 2.0kW, the height of the electrodeless lamp is not lower than 2/3 of the height of the wastewater reaction chamber [11]. 7.根据权利要求6所述的方法,其特征在于石英搅拌器[13]为一同轴多页石英板,置于环行固定器的空心圆中央,该石英搅拌器的轴通过废水反应室[11]和微波反应炉[10]上部的开口与旋转电机[12]相连。7. The method according to claim 6, characterized in that the quartz stirrer [13] is a coaxial multi-page quartz plate, placed in the center of the hollow circle of the ring fixture, and the shaft of the quartz stirrer passes through the waste water reaction chamber [ 11] and the opening on the top of the microwave reactor [10] is connected with the rotary motor [12]. 8.根据权利要求5或6或7所述的方法,其特征在于废水反应室内壁凸起有3~9个凸柱[18],废水反应室上盖为可拆式开口盖,环形固定器[14]上有4~8个小孔,无电极灯[17]插入环形固定器[14]的小孔中。8. The method according to claim 5 or 6 or 7, characterized in that there are 3 to 9 protrusions [18] protruding from the inner wall of the wastewater reaction chamber, the upper cover of the wastewater reaction chamber is a detachable opening cover, and a ring holder There are 4~8 small holes on [14], and electrodeless lamp [17] is inserted in the small hole of ring holder [14]. 9.根据权利要求5或6或7所述的方法,其特征在于无电极灯[17]的制作方法为抽空气至2.5~5.0kPa后,充入0.5~2.0kPa氩气或氦气,并滴加金属汞1~5滴,最后密封。9. The method according to claim 5 or 6 or 7, characterized in that the electrodeless lamp [17] is made by pumping the air to 2.5-5.0kPa, filling it with argon or helium at 0.5-2.0kPa, and Add 1 to 5 drops of metallic mercury, and finally seal it. 10.根据权利要求5或6或7所述的方法,其特征在于废水反应室[11]为耐热、耐腐蚀材料聚四氟乙烯、聚苯乙烯或陶瓷,微波反应炉[10]内壁采用不锈钢材料或含镍、铝的材料。10. The method according to claim 5 or 6 or 7, characterized in that the wastewater reaction chamber [11] is made of heat-resistant and corrosion-resistant materials such as polytetrafluoroethylene, polystyrene or ceramics, and the inner wall of the microwave reaction furnace [10] is made of Stainless steel materials or materials containing nickel and aluminum.
CNB2004100659797A 2004-12-29 2004-12-29 Method and apparatus for treating waste water by microwave photocatalysis Expired - Fee Related CN1303000C (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CNB2004100659797A CN1303000C (en) 2004-12-29 2004-12-29 Method and apparatus for treating waste water by microwave photocatalysis

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CNB2004100659797A CN1303000C (en) 2004-12-29 2004-12-29 Method and apparatus for treating waste water by microwave photocatalysis

Publications (2)

Publication Number Publication Date
CN1654338A CN1654338A (en) 2005-08-17
CN1303000C true CN1303000C (en) 2007-03-07

Family

ID=34892404

Family Applications (1)

Application Number Title Priority Date Filing Date
CNB2004100659797A Expired - Fee Related CN1303000C (en) 2004-12-29 2004-12-29 Method and apparatus for treating waste water by microwave photocatalysis

Country Status (1)

Country Link
CN (1) CN1303000C (en)

Families Citing this family (13)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101857283B (en) * 2010-06-18 2012-07-04 江苏技术师范学院 Device for treating wastewater by microwave electrodeless excimer lamp and gas distribution system of lamp
CN102592946A (en) * 2012-02-26 2012-07-18 烟台同辉照明科技有限公司 Low-frequency and low-voltage electrodeless ultraviolet lamp
CN103214132B (en) * 2013-04-03 2016-09-07 宁波大学 The electrodeless ultraviolet light catalysis wastewater degradation reactor expansion method of aggregate can be cleared up
CN103241883B (en) * 2013-04-12 2016-11-09 宁波大学 Photocatalytic Wastewater Degradation Reactor Expansion Method for Self-checking the Main Inducing Parameters of Agglomeration
CN103288258B (en) * 2013-04-12 2016-11-16 宁波大学 Photocatalytic Wastewater Degradation Reactor Capacity Expansion Method Capable of Self-testing the Main Inducing Parameters of Agglomeration
CN103346064B (en) * 2013-07-11 2016-04-20 成都市巨源光电科技有限公司 A kind of stepless lamp system and ignition method thereof
CN103359858A (en) * 2013-07-18 2013-10-23 李榕生 Large capacity microwave photocatalytic wastewater degradation device of self-inspection electrodeless UV lamp state
CN103435205A (en) * 2013-07-24 2013-12-11 李榕生 High-capacity microwave photocatalytic waste water degradation device capable of precisely preventing catalyst loss
CN104045124B (en) * 2014-07-07 2016-08-24 济宁学院 A kind of microwave and photo catalysis fluid bed wastewater treatment equipment and processing method thereof
CN107128996B (en) * 2017-05-19 2019-12-31 山东大学 A four-chamber rotary microwave wastewater treatment device and method
CN108218068A (en) * 2018-01-22 2018-06-29 沈阳建筑大学 A kind of coagulation-microwave reinforced water treatment experimental device
CN108585108A (en) * 2018-05-11 2018-09-28 南京工业大学 Device for treating arsenic-containing wastewater through photocatalysis
CN114656078A (en) * 2022-01-25 2022-06-24 昆明理工大学 A method for spraying catalytic removal of organic matter in solution in multi-field coupled high-energy field

Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1102402A (en) * 1993-07-12 1995-05-10 石原产业株式会社 Photocatalyst and process for purifying water with same
CN1245147A (en) * 1998-08-19 2000-02-23 株式会社太白环境 Photocatalytic reaction system for treating waste water
US6090296A (en) * 1999-03-17 2000-07-18 Oster; Stephen P. Method and apparatus for UV-oxidation of toxics in water and UV-disinfection of water
CN1482072A (en) * 2002-09-13 2004-03-17 武汉科技学院 Microwave-infinite ultraviolet photocatalytic oxidation water treatment method

Patent Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1102402A (en) * 1993-07-12 1995-05-10 石原产业株式会社 Photocatalyst and process for purifying water with same
CN1245147A (en) * 1998-08-19 2000-02-23 株式会社太白环境 Photocatalytic reaction system for treating waste water
US6090296A (en) * 1999-03-17 2000-07-18 Oster; Stephen P. Method and apparatus for UV-oxidation of toxics in water and UV-disinfection of water
CN1482072A (en) * 2002-09-13 2004-03-17 武汉科技学院 Microwave-infinite ultraviolet photocatalytic oxidation water treatment method

Also Published As

Publication number Publication date
CN1654338A (en) 2005-08-17

Similar Documents

Publication Publication Date Title
CN1303000C (en) Method and apparatus for treating waste water by microwave photocatalysis
CN104909428B (en) A kind of Ag3PO4/TiO2The device and method of catalyst and low temperature plasma Combined Treatment bio-refractory organic wastewater
CN102730906B (en) Combined apparatus for advanced treatment of high concentration organic waste water
CN1199887C (en) Microwave catalytic oxidation process and apparatus for treating waste water containing hard-to-degrade organic matters
US20020187082A1 (en) Photocatalyst coated magnetic composite particle
WO2020010806A1 (en) Cyclic heterogeneous photocatalytic oxidation treatment system and treatment method
CN103387272B (en) Device and method for photo-catalytically degrading phenol-containing wastewater
An et al. Decolourization and COD removal from reactive dye‐containing wastewater using sonophotocatalytic technology
US20140291256A1 (en) Method for treatment of dyeing wastewater by using uv/acetylacetone oxidation process
CN100509160C (en) Synthesis technology of magnet carried photocatalyst composite particle, sewage purification method and device
CN210340579U (en) UV photocatalysis sewage treatment plant
CN103373750A (en) Light source device for removing organic matters and heavy metal ions by visible light and preparation method thereof
CN100558652C (en) Photocatalytic Aeration Filters for Water Treatment
CN207210021U (en) A kind of deep water treatment device
CN106946313A (en) A kind of wastewater treatment equipment of utilization photocatalysis degradation organic contaminant
CN110921769A (en) Method for treating drinking water by photocatalysis
CN105481079B (en) Modified TiO in a kind of rotating disk reactor2The method of catalyst degradation phenol wastewater
CN116535018A (en) Sewage treatment process based on near-field coupling of visible light catalysis and biodegradation
CN110841672A (en) Method for treating antibiotic wastewater by utilizing graphite alkyne modified silver phosphate composite photocatalyst
CN110655143A (en) A stationary photocatalytic cyclone reactor and its construction method and application
CN202558672U (en) Light source device using visible light to remove organics and heavy metal ions
CN107081153B (en) A method for photocatalytic reduction of Cr(VI) based on catalysts
JPH0871573A (en) Method and apparatus for water treatment by photocatalyst
CN109942126A (en) A kind of microwave ultraviolet sewage-treatment plant and method
CN115818769A (en) A continuous flow reaction device for photocatalytic treatment of antibiotic wastewater

Legal Events

Date Code Title Description
C06 Publication
PB01 Publication
C10 Entry into substantive examination
SE01 Entry into force of request for substantive examination
C14 Grant of patent or utility model
GR01 Patent grant
C17 Cessation of patent right
CF01 Termination of patent right due to non-payment of annual fee

Granted publication date: 20070307

Termination date: 20101229