CN102491568A - Method for treating wastewater of electrolytic zinc rinsing technology - Google Patents

Method for treating wastewater of electrolytic zinc rinsing technology Download PDF

Info

Publication number
CN102491568A
CN102491568A CN2011103805988A CN201110380598A CN102491568A CN 102491568 A CN102491568 A CN 102491568A CN 2011103805988 A CN2011103805988 A CN 2011103805988A CN 201110380598 A CN201110380598 A CN 201110380598A CN 102491568 A CN102491568 A CN 102491568A
Authority
CN
China
Prior art keywords
rinsing
electrodeposition
water
countercurrent
zinc
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.)
Pending
Application number
CN2011103805988A
Other languages
Chinese (zh)
Inventor
刘晗
李振山
曹光亮
包立超
邱松
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.)
Peking University
Original Assignee
Peking 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 Peking University filed Critical Peking University
Priority to CN2011103805988A priority Critical patent/CN102491568A/en
Publication of CN102491568A publication Critical patent/CN102491568A/en
Pending legal-status Critical Current

Links

Images

Classifications

    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02PCLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P10/00Technologies related to metal processing
    • Y02P10/20Recycling

Landscapes

  • Separation Using Semi-Permeable Membranes (AREA)

Abstract

本发明公开电解锌漂洗工艺废水处理方法,方法是逆流漂洗、电沉积、膜分离的组合处理:逆流漂洗:电解锌生产中使用的阴极板进入逆流漂洗装置进行漂洗,包括:先进入第一级逆流漂洗槽,即浓水槽,极板清洗方向与水流方向相反,再进入最后一级槽,即清水槽,完成漂洗过程;电沉积:漂洗后的浓水进入平板式电沉积装置、三维电沉积装置,回收废水中金属锌;膜分离:电沉积后的废水,依次进入超滤膜系统、反渗透膜系统,膜系统产生的浓缩液回流到电沉积装置中,回收膜浓缩液中的金属锌,膜出水回流到逆流漂洗装置中。本发明的优点:利用逆流漂洗、电沉积和膜分离工艺结合,实现了废水的循环使用,重金属污染物基本实现完全回收和零排放。

The invention discloses a method for treating wastewater in an electrolytic zinc rinsing process. The method is a combined treatment of countercurrent rinsing, electrodeposition, and membrane separation: countercurrent rinsing: the cathode plate used in electrolytic zinc production enters a countercurrent rinsing device for rinsing, including: entering the first stage first Countercurrent rinsing tank, that is, concentrated water tank, the cleaning direction of the plate is opposite to the direction of water flow, and then enters the last level tank, that is, clear water tank, to complete the rinsing process; electrodeposition: the concentrated water after rinsing enters the flat plate electrodeposition device, three-dimensional electrodeposition device to recover metal zinc in wastewater; membrane separation: the wastewater after electrodeposition enters the ultrafiltration membrane system and reverse osmosis membrane system in turn, and the concentrated solution produced by the membrane system flows back into the electrodeposition device to recover the metal zinc in the membrane concentrated solution , the membrane effluent is returned to the countercurrent rinsing device. The invention has the advantages of realizing the recycling of waste water through the combination of countercurrent rinsing, electrodeposition and membrane separation technology, and basically realizing complete recovery and zero discharge of heavy metal pollutants.

Description

电解锌漂洗工艺废水处理方法Electrolytic zinc rinsing process wastewater treatment method

技术领域 technical field

本发明涉及一种工业废水处理方法,具体地说,是涉及电解锌生产过程中使用的阴极板的逆流漂洗、对漂洗后废水进行电沉积和膜分离组合处理方法。The invention relates to a method for treating industrial waste water, in particular to a combined treatment method for countercurrent rinsing of cathode plates used in the production process of electrolytic zinc, electrodeposition and membrane separation for the waste water after rinsing.

背景技术 Background technique

电解法生产锌工艺在金属剥离和极板清洗过程中,会产生大量的漂洗废水。漂洗废水中含有锌、铅、镉等多种重金属离子。由于其水量较大,重金属(尤其是锌离子)浓度较高,如果不经处理直接排放,将会对周围环境造成严重的影响,同时其中所含的重金属资源也将被浪费,如何有效处理电解锌漂洗工艺废水是当前采矿、电镀、电解法生产锌等行业所关注的焦点问题。高效、低耗地去除废水中重金属离子的同时,实现废水回用和重金属回收是今后重金属废水处理的发展方向。传统处理重金属的废水的方法包括:化学处理法、生物处理法、电化学处理法,但化学法处理含重金属废水时,由于受沉淀剂和环境条件的影响,沉淀法往往出水浓度达不到要求,需作进一步处理;生物处理法虽然具有成本低,处理方便的优点,一般的微生物对重金属离子的耐受浓度很小,很难大规模处理重金属废水;在以往应用电化学方法处理,当废水中重金属浓度降低时,存在能耗大,处理效果较差的问题。In the process of electrolytic production of zinc, a large amount of rinsing wastewater will be generated during the process of metal stripping and plate cleaning. Rinsing wastewater contains zinc, lead, cadmium and other heavy metal ions. Due to its large amount of water and high concentration of heavy metals (especially zinc ions), if it is discharged directly without treatment, it will have a serious impact on the surrounding environment. At the same time, the heavy metal resources contained in it will also be wasted. How to effectively deal with electrolysis Zinc rinsing process wastewater is the focus of attention in mining, electroplating, electrolytic production of zinc and other industries. Efficient and low-cost removal of heavy metal ions in wastewater, while realizing wastewater reuse and heavy metal recovery is the development direction of heavy metal wastewater treatment in the future. Traditional methods for treating heavy metal wastewater include: chemical treatment, biological treatment, and electrochemical treatment. However, when chemical methods are used to treat wastewater containing heavy metals, due to the influence of precipitants and environmental conditions, the effluent concentration of precipitation methods often does not meet the requirements. , needs further treatment; although the biological treatment method has the advantages of low cost and convenient treatment, the tolerance concentration of general microorganisms to heavy metal ions is very small, and it is difficult to treat heavy metal wastewater on a large scale; in the past, electrochemical methods were used for wastewater treatment. When the concentration of medium and heavy metals is reduced, there are problems of high energy consumption and poor treatment effect.

国内主要采用电解法来进行锌冶炼和电镀企业的工业废水;采用传统重金属沉淀工艺处理重金属废水很难达标,废水外排后严重污染环境,回收率低,回收水质差,重金属污染物无法回收,浪费资源,且容易造成二次污染的现状,本发明开发的新的处理方法重金属污染物基本可以实现完全回收和零排放,水资源完全循环使用的新工艺。Domestically, electrolysis is mainly used to process industrial wastewater from zinc smelting and electroplating enterprises; it is difficult to meet the standard for heavy metal wastewater treatment by traditional heavy metal precipitation process, and the wastewater will seriously pollute the environment after being discharged, the recovery rate is low, the recycled water quality is poor, and heavy metal pollutants cannot be recycled. In the current situation of wasting resources and easily causing secondary pollution, the new treatment method developed by the present invention can basically realize complete recovery and zero discharge of heavy metal pollutants, and a new process of completely recycling water resources.

发明内容 Contents of the invention

本发明的目的在于克服现有技术中存在的不足之处,而提供一种投资少、效益高的电解锌漂洗工艺废水处理方法。The purpose of the present invention is to overcome the deficiencies existing in the prior art, and provide a kind of electrolytic zinc rinsing process wastewater treatment method with low investment and high benefit.

本发明的技术方案为:电解锌漂洗工艺废水处理方法,该方法是逆流漂洗、电沉积、膜分离的组合处理三个步骤:The technical scheme of the present invention is: the electrolytic zinc rinsing process wastewater treatment method, the method is a combination of three steps of countercurrent rinsing, electrodeposition, and membrane separation:

第一步骤:逆流漂洗Step 1: Rinse with countercurrent

逆流清洗是由若干水槽串联组成,在最后一级槽(清水槽)内进水,从第一级槽(浓水槽)排水,水流方向和极板的清洗流程方向相反。电解锌生产中使用的阴极板进入逆流漂洗装置进行漂洗,先进入第一级逆流漂洗槽(浓水槽),最后进入最后一级槽(清水槽),完成漂洗过程;Countercurrent cleaning is composed of several tanks connected in series. Water is fed into the last tank (clean water tank) and drained from the first tank (concentrated water tank). The direction of water flow is opposite to that of the plate cleaning process. The cathode plate used in the production of electrolytic zinc enters the countercurrent rinsing device for rinsing, first enters the first level of countercurrent rinsing tank (concentrated water tank), and finally enters the last level of tank (clear water tank) to complete the rinsing process;

通过逆流漂洗,极板随着生产方向移动的电极板越洗越干净,而清洗水中的污染物浓度则越来越高,用水量少,清洗效率高。Through countercurrent rinsing, the electrode plate moves with the production direction and the electrode plate is washed more and more cleanly, while the concentration of pollutants in the cleaning water is getting higher and higher, with less water consumption and high cleaning efficiency.

所使用的串联水槽数一般为4-10个,优选为4-8个,特别优选为6-8个,本领域技术人员可以根据相应的具体情况进行调整;The number of series water tanks used is generally 4-10, preferably 4-8, particularly preferably 6-8, and those skilled in the art can adjust according to the corresponding specific conditions;

第二步骤:电沉积Step 2: Electrodeposition

漂洗后的浓水进入调节池,调节其水量和流速,再依次进入平板式电沉积装置、三维电沉积装置,回收废水中金属锌;The concentrated water after rinsing enters the regulating tank, adjusts its water volume and flow rate, and then enters the flat-plate electrodeposition device and the three-dimensional electrodeposition device in turn to recover metal zinc in the wastewater;

电沉积指平板式电沉积装置和三维电沉积装置;Electrodeposition refers to flat-plate electrodeposition devices and three-dimensional electrodeposition devices;

调节水量和流速要根据具体实验的要求来确定,本实验中,调节后的水量为5m3,流速为1m3/h。The adjusted water volume and flow rate should be determined according to the requirements of specific experiments. In this experiment, the adjusted water volume is 5m 3 and the flow rate is 1m 3 /h.

第三步骤:膜分离Step Three: Membrane Separation

电沉积后的废水,依次进入超滤膜系统、反渗透膜系统,废水经过两级膜分离系统,即超滤膜系统和反渗透膜系统所得浓缩液,回流到电沉积之前的调节池,然后经过平板式电沉积装置、三维电沉积装置,回收膜浓缩液中的金属锌。超滤膜系统的出水进入反渗透膜系统进一步处理,反渗透膜系统出水回流到逆流漂洗装置中的最后一级槽(清水槽);The wastewater after electrodeposition enters the ultrafiltration membrane system and the reverse osmosis membrane system in turn. The wastewater passes through the two-stage membrane separation system, that is, the concentrated solution obtained from the ultrafiltration membrane system and the reverse osmosis membrane system, and returns to the regulating tank before electrodeposition, and then Metal zinc in the membrane concentrate is recovered through a flat-plate electrodeposition device and a three-dimensional electrodeposition device. The effluent from the ultrafiltration membrane system enters the reverse osmosis membrane system for further treatment, and the effluent from the reverse osmosis membrane system flows back to the last stage tank (clean water tank) in the countercurrent rinsing device;

膜分离指超滤膜系统和反渗透膜系统分离;Membrane separation refers to the separation of ultrafiltration membrane system and reverse osmosis membrane system;

而经过电沉积和膜系统处理后的废水回用出水只有1个口,来自反渗透系统;The wastewater reused after electrodeposition and membrane system treatment has only one outlet, which comes from the reverse osmosis system;

金属锌的回收来源于两个部分,一部分是来源于逆流漂洗后废水的电沉积过程,回收的是逆流漂洗后废水的金属锌;另外一部分来源于电沉积后的废水,经过超滤膜系统、反渗透膜系统后产生的浓缩液回流到电沉积装置后的电沉积过程,回收的是本组合处理方法中膜系统产生的浓缩液中的金属锌。The recovery of metal zinc comes from two parts, one part is from the electrodeposition process of the wastewater after countercurrent rinsing, and the metal zinc in the wastewater after countercurrent rinsing is recovered; the other part comes from the wastewater after electrodeposition, which is passed through the ultrafiltration membrane system, The concentrated solution produced after the reverse osmosis membrane system is returned to the electrodeposition process after the electrodeposition device, and the metal zinc in the concentrated solution produced by the membrane system in this combined treatment method is recovered.

下面陈述各部件的工艺条件及功能:The process conditions and functions of each component are stated below:

逆流漂洗通过清洗极板的次数控制逆流漂洗出水Zn2+浓度在3000mg/L左右;Countercurrent rinsing controls the concentration of Zn 2+ in the countercurrent rinsing water to about 3000mg/L by the number of times the plates are cleaned;

调节池:用于蓄水,调节其水量和流速,稳定水流;调节水量和流速要根据具体实验的要求来确定,本实验中,调节后的水量为5m3,流速为1m3/h。Adjusting pool: used for water storage, adjusting its water volume and flow rate, and stabilizing water flow; the adjustment of water volume and flow rate should be determined according to the requirements of specific experiments. In this experiment, the adjusted water volume is 5m 3 and the flow rate is 1m 3 /h.

平板式电沉积装置的Zn2+的最低浓度降低达到800mg/L;The minimum concentration of Zn 2+ in the flat-plate electrodeposition device is reduced to 800mg/L;

常用的平板式电沉积装置包括:如CN1930325公布的用于电化学工艺的电解槽,CN1995461公布的隔膜法金属阳极电解槽。Commonly used flat-plate electrodeposition devices include: an electrolytic cell for electrochemical process disclosed in CN1930325, and a diaphragm method metal anode electrolytic cell disclosed in CN1995461.

所说的三维电沉积处理含锌废水的条件为:电极材料选用石墨阳极/不锈钢阴极配对电极,槽电压和电解时间需根据废水中锌离子的浓度和水力停留时间确定,一般情况下槽电压为4.0V-8.0V,电解时间为60min-90min;三维电沉积,是在传统二维电解槽电极间装填粒状或其他碎屑状工作电极材料,并使装填粒状电极材料表面带电,成为新的一极(第三极),在工作电极材料表面能发生电化学反应;经三维电沉积装置处理后的Zn2+的最低浓度低于80mg/L,锌离子的去除率达90%以上;The conditions for the three-dimensional electrodeposition treatment of zinc-containing wastewater are as follows: the electrode material is a graphite anode/stainless steel cathode paired electrode, and the cell voltage and electrolysis time need to be determined according to the concentration of zinc ions in the wastewater and the hydraulic retention time. Generally, the cell voltage is 4.0V-8.0V, the electrolysis time is 60min-90min; three-dimensional electrodeposition is to fill granular or other debris-like working electrode materials between the electrodes of the traditional two-dimensional electrolytic cell, and to charge the surface of the filled granular electrode materials, which has become a new Pole (third pole), electrochemical reaction can occur on the surface of the working electrode material; the minimum concentration of Zn 2+ treated by the three-dimensional electrodeposition device is lower than 80mg/L, and the removal rate of zinc ions is more than 90%;

常用的三维电沉积装置包括:如CN101186361公布的三维电极反应器及利用其处理氯苯废水的方法中的三维电极反应器,CN101514040公布的一种三维电极反应器及其在难降解有机废水处理中的应用中的三维电极反应器。Commonly used three-dimensional electrodeposition devices include: a three-dimensional electrode reactor disclosed in CN101186361 and a three-dimensional electrode reactor in a method for treating chlorobenzene wastewater using it, a three-dimensional electrode reactor disclosed in CN101514040 and its application in refractory organic wastewater treatment Three-dimensional electrode reactors in applications.

超滤膜系统是去除水中悬浮物、胶体等物质,水质达到反渗透进水要求(主要为SDI(淤积指数)<3.0,浊度小于0.10),在超滤分离过程锌离子的平均去除效率为60%~70%,加入15mg/L酒石酸钾钠PST,锌离子的去除效率达到99%;The ultrafiltration membrane system removes suspended solids, colloids and other substances in the water. The water quality meets the requirements of reverse osmosis (mainly SDI (silting index) < 3.0, turbidity is less than 0.10). The average removal efficiency of zinc ions in the ultrafiltration separation process is 60% to 70%, adding 15mg/L potassium sodium tartrate PST, the removal efficiency of zinc ions reaches 99%;

常用的超滤膜系统如美国密理博公司的Millipore超滤系统(labscale TFF小型切向流超滤系统、Congent-M超滤系统、Pellicon超滤系统),GE公司生产的1500压力式超滤膜系统、SIEMENS公司的

Figure BDA0000112265130000032
CP压力式超滤系统。Commonly used ultrafiltration membrane systems, such as the Millipore ultrafiltration system (labscale TFF small tangential flow ultrafiltration system, Congent-M ultrafiltration system, Pellicon ultrafiltration system) produced by Millipore Corporation of the United States, GE’s 1500 pressure ultrafiltration membrane system, SIEMENS company
Figure BDA0000112265130000032
CP pressure ultrafiltration system.

所说的在反渗透分离过程中,使用的操作压力控制在0.7~1.0MPa,出水中Zn2+浓度降低到0.1-0.5mg/L,锌离子的平均去除效率为90%,出水电导降低到50μS/cm;废水工作温度25℃~35℃,反渗透膜工艺产水率为60%~70%,平均截留率在92%~95%,产水水质优于工业循环水水质标准,可回用于工业循环水系统或者水质要求高的用水点;Said in the reverse osmosis separation process, the operating pressure used is controlled at 0.7-1.0MPa, the concentration of Zn 2+ in the effluent water is reduced to 0.1-0.5mg/L, the average removal efficiency of zinc ions is 90%, and the conductivity of the effluent water is reduced to 50μS/cm; the working temperature of wastewater is 25℃~35℃, the water production rate of reverse osmosis membrane process is 60%~70%, and the average retention rate is 92%~95%. Used in industrial circulating water systems or water points with high water quality requirements;

常用的反渗透膜系统如东莞市益民水处理科技有限公司生产的YMRO-0.25-500反渗透水处理系统、北京开能立源环境工程技术有限公司生成的2T/H单级反渗透设备。Commonly used reverse osmosis membrane systems such as YMRO-0.25-500 reverse osmosis water treatment system produced by Dongguan Yimin Water Treatment Technology Co., Ltd., and 2T/H single-stage reverse osmosis equipment produced by Beijing Kaineng Liyuan Environmental Engineering Technology Co., Ltd.

上述处理后的废水,先进行超滤膜处理工艺,再进行反渗透膜分离,以保证反渗透的出水效果,并节约反渗透设备所需能源,充分浓缩废液中重金属,使浓缩液中的金属离子浓度得到较大提高,适用于电沉积回收重金属;The waste water after the above treatment is firstly treated with ultrafiltration membrane, and then separated by reverse osmosis membrane to ensure the water effluent effect of reverse osmosis, save the energy required by reverse osmosis equipment, fully concentrate the heavy metals in the waste liquid, and make the concentrated liquid The concentration of metal ions has been greatly improved, which is suitable for the recovery of heavy metals by electrodeposition;

两级膜分离工艺产生30%~40%的浓缩液,经过循环再进入调节池回用,回收金属锌,出水回用到逆流漂洗装置中的清水槽,,而实现整个装置中重金属污染物基本可以实现完全回收和零排放。The two-stage membrane separation process produces 30% to 40% of the concentrated solution, which is recycled into the regulating tank for reuse, metal zinc is recovered, and the effluent is reused in the clear water tank in the countercurrent rinsing device, so that the heavy metal pollutants in the entire device are basically eliminated. Complete recycling and zero emissions can be achieved.

本发明与现有技术相比,具有如下的优点:Compared with the prior art, the present invention has the following advantages:

第一,使用逆流漂洗装置对电解锌生产过程中使用的阴极板进行漂洗,随着生产方向移动的电极板越洗越干净,而清洗水中的污染物浓度则越来越高,用水量少,清洗效率高,并有利于废水的回用和重金属离子的回收。First, use a countercurrent rinsing device to rinse the cathode plates used in the electrolytic zinc production process. The electrode plates moving along the production direction become cleaner and cleaner, while the concentration of pollutants in the washing water is getting higher and higher, and the water consumption is less. The cleaning efficiency is high, and it is beneficial to the reuse of waste water and the recovery of heavy metal ions.

第二,利用电沉积先对锌离子含量较高的逆流漂洗出水进行金属锌的回收,然后废水经过膜的处理,可以充分浓缩废液中重金属,使浓缩液中的金属离子浓度得到较大提高,与电沉积技术结合,非常适用于电解回收重金属,易于实现废水的循环再利用。把电沉积技术和膜分离处理工艺结合起来,充分发挥电沉积和膜分离技术的优点,解决了以往电化学还原处理方式存在的问题。Second, using electrodeposition to recover metal zinc from the countercurrent rinsing effluent with high zinc ion content, and then the wastewater is treated with a membrane, which can fully concentrate the heavy metals in the waste liquid and greatly increase the concentration of metal ions in the concentrated liquid , combined with electrodeposition technology, is very suitable for electrolytic recovery of heavy metals, and is easy to realize the recycling of wastewater. Combining electrodeposition technology and membrane separation treatment process, the advantages of electrodeposition and membrane separation technology are fully utilized, and the problems existing in the previous electrochemical reduction treatment method are solved.

第三,重金属废水处理的废水净化回用和重金属回收同时完成,实现了生产和处理的良性循环。Third, the waste water purification reuse and heavy metal recovery of heavy metal wastewater treatment are completed at the same time, realizing a virtuous cycle of production and treatment.

第四,针对不同浓度和组成的废水提出相应的处理工艺方式,为装置的合理设计和操作过程的优化提供理论指导。Fourth, propose corresponding treatment process methods for wastewater with different concentrations and compositions, and provide theoretical guidance for rational design of devices and optimization of operating processes.

本发明该工艺处理后的废水全部回流到逆流漂洗装置中,补充逆流漂洗装置中所需的水量,从废水产生到处理后废水回流,形成了一个水循环,运行成本低,整个工艺只有一个清水的排出回用出口,而重金属污染物基本可以实现完全回收和零排放。The waste water treated by the process of the present invention is all returned to the countercurrent rinsing device to supplement the required water volume in the countercurrent rinsing device. From the generation of waste water to the reflux of treated waste water, a water cycle is formed, and the operation cost is low. The whole process only has one clean water tank. It is discharged and reused at the outlet, and the heavy metal pollutants can basically achieve complete recovery and zero discharge.

依据逆流漂洗、电沉积和膜分离技术的优点,可以达到最低的运行费用和最佳的分离效果,实现水的达标排放的同时,有效回收废水中重金属资源,在有效回收废水中重金属的同时,实现水的循环使用。According to the advantages of countercurrent rinsing, electrodeposition and membrane separation technology, it can achieve the lowest operating cost and the best separation effect, realize the discharge of water up to the standard, and effectively recover the heavy metal resources in the wastewater. While effectively recovering the heavy metals in the wastewater, Realize water recycling.

附图说明 Description of drawings

图1为本发明电解锌漂洗工艺废水“零排放”处理工艺方法流程图Fig. 1 is the process flow chart of the "zero discharge" treatment process of electrolytic zinc rinsing process wastewater of the present invention

具体实施方式 Detailed ways

下面列举1个实施例,结合附图,对本发明加以进一步说明,但本发明不只限于这个实施例。An embodiment is listed below, and the present invention is further described in conjunction with the accompanying drawings, but the present invention is not limited to this embodiment.

实施例1Example 1

本发明方法步骤采用逆流漂洗-平板式电沉积装置-三维电沉积装置-超滤膜系统-反渗透膜系统的工艺组合,具体工艺流程如下:The method step of the present invention adopts the process combination of countercurrent rinsing-flat plate electrodeposition device-three-dimensional electrodeposition device-ultrafiltration membrane system-reverse osmosis membrane system, and the specific process flow is as follows:

第一步骤:逆流漂洗Step 1: Rinse with countercurrent

逆流清洗是由四个水槽串联组成,在最后一级槽(清水槽)内进水,从第一级槽(浓水槽)排水,水流方向和极板的清洗流程方向相反。电解锌生产中使用的阴极板进入逆流漂洗装置进行漂洗,先进入第一级逆流漂洗槽(浓水槽),最后进入最后一级槽(清水槽),完成漂洗过程,逆流漂洗出水Zn2+浓度为3000mg/L左右;Countercurrent cleaning is composed of four tanks connected in series. Water is fed into the last tank (clean water tank) and drained from the first tank (concentrated water tank). The direction of water flow is opposite to that of the plate cleaning process. The cathode plate used in the production of electrolytic zinc enters the countercurrent rinsing device for rinsing, first enters the first stage countercurrent rinsing tank (concentrated water tank), and finally enters the last stage tank (clear water tank) to complete the rinsing process, and the concentration of Zn 2+ in the countercurrent rinsing water is About 3000mg/L;

第二步骤:电沉积Step 2: Electrodeposition

漂洗后的浓水进入调节池,调节其水量和流速,再进入平板式电沉积装置、三维电沉积装置,回收废水中金属锌,电沉积后废水中Zn2+浓度为100mg/L左右;The concentrated water after rinsing enters the regulating tank, adjusts its water volume and flow rate, and then enters the flat plate electrodeposition device and three-dimensional electrodeposition device to recover metal zinc in the wastewater. The concentration of Zn 2+ in the wastewater after electrodeposition is about 100mg/L;

第三步骤:膜分离Step Three: Membrane Separation

电沉积出来的废水,温度控制在20℃~35℃,进入超滤膜系统,加入15mg/L酒石酸钾钠PST,去除水中的悬浮物、胶体等物质,锌离子的去除效率达到99%,再进入反渗透膜系统,反渗透膜系统出水中Zn2+浓度为0.1-0.5mg/L,膜分离系统出水回流到逆流漂洗装置中,废水经过两级膜分离系统所得浓缩液,回流到电沉积之前的调节池,然后经过平板式电沉积装置、三维电沉积装置,回收膜浓缩液中的金属锌。The temperature of the electrodeposited wastewater is controlled at 20°C to 35°C, and it enters the ultrafiltration membrane system, and 15mg/L potassium sodium tartrate PST is added to remove suspended solids, colloids and other substances in the water. The removal efficiency of zinc ions reaches 99%. Enter the reverse osmosis membrane system, the concentration of Zn 2+ in the effluent water of the reverse osmosis membrane system is 0.1-0.5mg/L, the effluent water from the membrane separation system is returned to the countercurrent rinsing device, and the waste water passes through the concentrated solution obtained by the two-stage membrane separation system, and then flows back to the electrodeposition The previous regulating tank then passes through a flat-plate electrodeposition device and a three-dimensional electrodeposition device to recover the metal zinc in the membrane concentrate.

而废水回用只有1个口,来自反渗透系统。重金属污染物基本可以实现完全回收和零排放,处理后的废水全部回流到逆流漂洗装置中,形成一个水循环。There is only one port for wastewater reuse, which comes from the reverse osmosis system. Heavy metal pollutants can basically be completely recovered and zero discharged, and all the treated wastewater is returned to the countercurrent rinsing device to form a water cycle.

Claims (3)

1. electrolytic zinc rinsing process method of wastewater treatment is characterized in that this method comprises three steps of combined treatment of countercurrent rinsing, galvanic deposit, membrane sepn:
First step: countercurrent rinsing
Countercurrent rinsing is to be composed in series by some tanks, water inlet in the one-level groove (that is, Rinsing Area) in the end, and from first step groove (that is, dense tank) draining, the cleaning process of water (flow) direction and pole plate is in the opposite direction.The negative plate that uses in the electrolytic zinc production technique gets in the countercurrent rinsing device and carries out rinsing, is introduced into first step countercurrent rinsing groove (that is, dense tank), gets into the last step groove (that is, Rinsing Area) of countercurrent rinsing groove at last, accomplishes the rinse cycle of pole plate.
Second step: galvanic deposit
Dense water after the rinsing gets into equalizing tank, regulates its water yield and flow velocity, gets into flat electric deposition device, three-dimensional electric deposition device again, reclaims metallic zinc in the waste water;
Third step: membrane sepn
Waste water after the galvanic deposit; Get into ultrafiltration membrane system, reverse osmosis membrane system successively; Waste water is back to galvanic deposit equalizing tank before through two-stage film separating system gained liquid concentrator, passes through flat electric deposition device, three-dimensional electric deposition device then; Metallic zinc in the reclamation film liquid concentrator, the film separating system effluent recycling is in countercurrent rinsing device;
Membrane sepn refers to that ultrafiltration membrane system separates with reverse osmosis membrane system;
And the waste water recycling water outlet has only 1 mouth, from reverse osmosis system;
Metallic zinc retrieve to come from two parts, a part is the electrodeposition process that derives from waste water behind the countercurrent rinsing, recovery be the metallic zinc in the waste water behind the countercurrent rinsing; A part derives from the waste water after the galvanic deposit in addition, is back to the electrodeposition process behind the electric deposition device through the liquid concentrator that produces behind ultrafiltration membrane system, the reverse osmosis membrane system, recovery be the metallic zinc in the liquid concentrator that the film system produces in this combination treatment method.
2. electrolytic zinc rinsing process method of wastewater treatment as claimed in claim 1; It is characterized in that: the operational condition of said three-dimensional galvanic deposit is: electrode materials is selected graphite anode/stainless steel cathode counter-electrodes for use; Bath voltage is 4.0V-8.0V, and electrolysis time is 60min-90min.
3. electrolytic zinc rinsing process method of wastewater treatment as claimed in claim 1 is characterized in that: said in the reverse osmosis isolation process, the working pressure of use is controlled at 0.7~1.0MPa, Zn in the water outlet 2+Concentration is 0.1-0.5mg/L, and the average removal efficient of zine ion is 90%.
CN2011103805988A 2011-11-25 2011-11-25 Method for treating wastewater of electrolytic zinc rinsing technology Pending CN102491568A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN2011103805988A CN102491568A (en) 2011-11-25 2011-11-25 Method for treating wastewater of electrolytic zinc rinsing technology

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN2011103805988A CN102491568A (en) 2011-11-25 2011-11-25 Method for treating wastewater of electrolytic zinc rinsing technology

Publications (1)

Publication Number Publication Date
CN102491568A true CN102491568A (en) 2012-06-13

Family

ID=46183439

Family Applications (1)

Application Number Title Priority Date Filing Date
CN2011103805988A Pending CN102491568A (en) 2011-11-25 2011-11-25 Method for treating wastewater of electrolytic zinc rinsing technology

Country Status (1)

Country Link
CN (1) CN102491568A (en)

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN103014782A (en) * 2012-12-27 2013-04-03 云南云铜锌业股份有限公司 Magnesium removal method in zinc electrolysis process
CN103663803A (en) * 2012-09-17 2014-03-26 武汉环材科技有限公司 Efficient electro-deposited heavy metal cleaning system
CN106673285A (en) * 2016-11-29 2017-05-17 环境保护部华南环境科学研究所 Resource recycling method for gold-containing electroplating wastewater
CN111018203A (en) * 2019-12-27 2020-04-17 肇庆学院 A device for recycling nickel-containing heavy metal wastewater

Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2009017479A1 (en) * 2007-07-31 2009-02-05 Perry Equipment Corporation Systems and methods for removal of heavy metal contaminants from fluids
CN101565248A (en) * 2008-04-25 2009-10-28 上海润实防蚀新材料科技有限公司 Electroplating wastewater processing method
CN101575119A (en) * 2009-05-27 2009-11-11 无锡市星亿涂装环保设备有限公司 Method for recovering chromic acid and water from chromeplating rinse water
CN101921032A (en) * 2010-09-10 2010-12-22 北京大学 Electrodeposition-Membrane Separation Combined Treatment Device for Electrolytic Zinc Rinse Wastewater
CN101935126A (en) * 2010-09-10 2011-01-05 北京大学 Electrodeposition and membrane separation combined treatment method for zinc-containing heavy metal wastewater

Patent Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2009017479A1 (en) * 2007-07-31 2009-02-05 Perry Equipment Corporation Systems and methods for removal of heavy metal contaminants from fluids
CN101565248A (en) * 2008-04-25 2009-10-28 上海润实防蚀新材料科技有限公司 Electroplating wastewater processing method
CN101575119A (en) * 2009-05-27 2009-11-11 无锡市星亿涂装环保设备有限公司 Method for recovering chromic acid and water from chromeplating rinse water
CN101921032A (en) * 2010-09-10 2010-12-22 北京大学 Electrodeposition-Membrane Separation Combined Treatment Device for Electrolytic Zinc Rinse Wastewater
CN101935126A (en) * 2010-09-10 2011-01-05 北京大学 Electrodeposition and membrane separation combined treatment method for zinc-containing heavy metal wastewater

Cited By (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN103663803A (en) * 2012-09-17 2014-03-26 武汉环材科技有限公司 Efficient electro-deposited heavy metal cleaning system
CN103014782A (en) * 2012-12-27 2013-04-03 云南云铜锌业股份有限公司 Magnesium removal method in zinc electrolysis process
CN103014782B (en) * 2012-12-27 2015-09-02 云南云铜锌业股份有限公司 Row's magnesium method in a kind of process in zinc electrolyzing
CN106673285A (en) * 2016-11-29 2017-05-17 环境保护部华南环境科学研究所 Resource recycling method for gold-containing electroplating wastewater
CN106673285B (en) * 2016-11-29 2018-03-23 环境保护部华南环境科学研究所 A kind of recycling recoverying and utilizing method containing golden electroplating wastewater
CN111018203A (en) * 2019-12-27 2020-04-17 肇庆学院 A device for recycling nickel-containing heavy metal wastewater
CN111018203B (en) * 2019-12-27 2022-02-01 肇庆学院 Nickel-containing heavy metal wastewater resource recovery device

Similar Documents

Publication Publication Date Title
CN103073123B (en) Electroplating Wastewater Recycling and Wastewater Recycling Technology
CN103243348B (en) Method and equipment for recovering heavy metals in electroplating wastewater
CN101343039A (en) A method for recovering pure acid and regenerating alkali from spent acid containing metal ions
CN102321908A (en) Recycling and regenerating process method and metal copper recovery system of acid chloride etching solution
CN101935126B (en) Combined treatment method for electro-deposition and membrane separation of zinc-containing heavy metal waste water
CN102453931A (en) Technology for treating and purifying copper electrolyte by vortex electrolysis
CN202610083U (en) Device for removing heavy metal from sludge in coupled film separating technology and electrokinetic technology
CN110616327A (en) Method and device for recovering elemental nickel from nickel-containing wastewater
CN202492580U (en) Acid etching liquid recycling device of PCB (Printed Circuit Board)
CN110422948A (en) Copper sulphate Sewage treatment metallic copper treatment process is electroplated
CN102491568A (en) Method for treating wastewater of electrolytic zinc rinsing technology
CN106430746A (en) Process for pretreating natural gas produced water with electric flocculation
CN106587459A (en) Online recycling method for electroplating washing wastewater
CN100341801C (en) Method for recovering nickel and removing impurity from nickel-plated wastewater
CN104030500B (en) A kind of Processes and apparatus removing nickel ion in section aluminum waste water
CN115231662A (en) Method and equipment for treating high-concentration cadmium-containing waste liquid through electrochemical reduction
CN107245580B (en) A method of cleaning is effectively separated and recovered from copper, tin and iron from spent acidic etching solution
CN204589307U (en) A kind of modified version regenerating alkaline etching liquid circulation and copper retrieving arrangement
CN204625786U (en) A kind of acidic etching liquid electrolysis cycle regeneration system rapidly
CN204702546U (en) A kind of electrochemical treatment system processing nickel-containing waste water
CN203382824U (en) Device for recovering refined copper from low-copper-content wastewater
CN203307440U (en) Recycling device for processing copper ions in electroplating wastewater
CN112110532A (en) Method for treating chloride ions in chlorine-containing solution by using copper powder
CN204625826U (en) The recycle system of electroplate liquid
CN201873760U (en) Device for recovering metallic nickel ion in electroplating 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
C02 Deemed withdrawal of patent application after publication (patent law 2001)
WD01 Invention patent application deemed withdrawn after publication

Application publication date: 20120613