CN102432123A - Reproducible heavy metal complexing agent and application method thereof - Google Patents

Reproducible heavy metal complexing agent and application method thereof Download PDF

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CN102432123A
CN102432123A CN2011103437153A CN201110343715A CN102432123A CN 102432123 A CN102432123 A CN 102432123A CN 2011103437153 A CN2011103437153 A CN 2011103437153A CN 201110343715 A CN201110343715 A CN 201110343715A CN 102432123 A CN102432123 A CN 102432123A
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complexing agent
equalizing tank
heavy metal
waste water
membrane
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包立超
李振山
曹光亮
宋立娜
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Peking University
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Abstract

The invention aims to provide a reproducible heavy metal complexing agent and an application method thereof. In the method, hydrolyzed collagen serving as a complexing agent is applied to a membrane separating process, and heavy metal copper-containing waste water is integrally treated by performing membrane separation-electrolysis. The method mainly comprises the following steps of: enriching; filtering; concentrating; decomplexing; electrodepositing; refluxing and the like to realize efficient recovery of heavy metal copper-containing waste water.

Description

一种可再生重金属络合剂及使用方法A kind of renewable heavy metal complexing agent and using method

技术领域 technical field

本发明属于水处理技术领域,尤其涉及一种工业废水处理方法,具体地说是涉及含重金属铜废水的处理方法。The invention belongs to the technical field of water treatment, and in particular relates to a method for treating industrial wastewater, in particular to a method for treating wastewater containing heavy metal copper.

背景技术 Background technique

重金属废水是对环境污染严重和对人类健康危害极大的工业废水之一。重金属废水来源广泛,主要产生于电镀、矿冶、电子、机械制造和化工等行业。随着这些行业的迅猛发展,重金属废水大量排放,日益引起人们的重视。根据废水的不同的来源与组分,重金属废水所采取的处理方法有所不同。一般来说,处理重金属废水的主要方法有:化学沉淀法、吸附法、离子交换法、电化学法和膜分离法等。化学沉淀法易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。吸附法具有操作简单、金属离子去除效率高等优点,但是吸附剂吸附了重金属之后仍存在着后处理问题,所经富集的含有高浓度重金属的洗脱液有待于进一步处理才能实现资源回收,限制了吸附法的工业化应用。离子交换法装置价格昂贵,处理成本较高,树脂易受污染或氧化失效。电沉积法能够将重金属离子还原为单质,电沉积过程结束后可以将极板上的金属单质剥离,轻松实现资源的回收,产生一定的经济效益。但是电沉积法只适合处理高浓度的重金属废水,处理低浓度重金属废水电耗大、投资成本高。Heavy metal wastewater is one of the industrial wastewater that seriously pollutes the environment and is extremely harmful to human health. Heavy metal wastewater comes from a wide range of sources, mainly in electroplating, mining and metallurgy, electronics, machinery manufacturing and chemical industries. With the rapid development of these industries, a large amount of heavy metal wastewater has been discharged, which has increasingly attracted people's attention. According to the different sources and components of wastewater, the treatment methods of heavy metal wastewater are different. Generally speaking, the main methods for treating heavy metal wastewater are: chemical precipitation, adsorption, ion exchange, electrochemical and membrane separation. The chemical precipitation method is easily affected by the precipitating agent and environmental conditions. The concentration of the effluent of the precipitation method often does not meet the requirements, and further treatment is required. The adsorption method has the advantages of simple operation and high metal ion removal efficiency, but there are still post-processing problems after the adsorbent absorbs heavy metals. The enriched eluate containing high concentrations of heavy metals needs further treatment to realize resource recovery. The industrial application of adsorption method. The ion exchange method device is expensive, the processing cost is high, and the resin is easily polluted or oxidized. The electrodeposition method can reduce heavy metal ions to simple substances. After the electrodeposition process, the simple metal substances on the plate can be peeled off, which can easily realize the recovery of resources and generate certain economic benefits. However, the electrodeposition method is only suitable for the treatment of high-concentration heavy metal wastewater, and the treatment of low-concentration heavy metal wastewater requires high power consumption and high investment costs.

膜分离技术是利用一种特殊的半透膜将溶液隔开,以压力为驱动力,当废水流经膜面时,其中的污染物被截留,而水分子透过膜,废水得到净化。膜技术作为一种新型的水处理技术具有低耗、高效、操作方便等优点,普遍受到国内外水处理者的关注,特别是可以在实现水回用的同时,提高浓水中的重金属含量,有利于重金属的进一步回收利用。目前所用的膜分离技术主要是微滤技术、超滤技术、纳滤技术和反渗透技术。纳滤和反渗透对于金属去除率高但是膜孔小,膜通量低,需要的操作压力高,一般用于饮用水的净化处理。超滤膜和微滤膜通量大,操作压力低,但是由于膜孔径远远大于金属离子直径,无法将其直接拦截,需要加入表面活性剂形成胶束或加入水溶性高分子聚合物与金属络合,使其体积增大而被截留。由此便形成了含有高浓度金属与有机物的浓缩液,如果不进一步处理直接排放到环境中,会造成二次污染。另一方面,工业废水水量大,需要在处理过程中不断加入表面活性剂或络合剂,增加了运行成本。Membrane separation technology uses a special semi-permeable membrane to separate the solution, with pressure as the driving force. When the wastewater flows through the membrane surface, the pollutants in it are intercepted, and the water molecules pass through the membrane to purify the wastewater. As a new type of water treatment technology, membrane technology has the advantages of low consumption, high efficiency, and convenient operation. Conducive to the further recycling of heavy metals. The currently used membrane separation technologies are mainly microfiltration technology, ultrafiltration technology, nanofiltration technology and reverse osmosis technology. Nanofiltration and reverse osmosis have high metal removal rates but small membrane pores, low membrane flux, and high operating pressure. They are generally used for drinking water purification. Ultrafiltration membranes and microfiltration membranes have large flux and low operating pressure, but because the membrane pore size is much larger than the diameter of metal ions, they cannot be directly intercepted. It is necessary to add surfactants to form micelles or add water-soluble polymers and metal ions. Complexation increases its volume and is trapped. As a result, a concentrated solution containing high concentrations of metals and organic substances is formed. If it is directly discharged into the environment without further treatment, it will cause secondary pollution. On the other hand, the volume of industrial wastewater is large, and surfactants or complexing agents need to be continuously added during the treatment process, which increases operating costs.

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浓缩液难以处理、运行成本高的问题,而提供一种可再生的重金属络合剂及其使用方法,由于该络合剂与金属的络合性和在电沉积中不易被氧化还原的性质,可以将该络合剂运用于超滤-电沉积组合法中,不仅使浓缩液得到有效处理,降低二次污染的危险,而且络合剂可以在电沉积过程中得到再生,通过络合剂的重复利用,有效的降低运行成本。The purpose of the present invention is to overcome the problem that the concentrated solution existing in the prior art is difficult to handle and the running cost is high, and provide a kind of reproducible heavy metal complexing agent and its use method, because the complexing property of this complexing agent and metal And the property that it is not easy to be oxidized and reduced in electrodeposition, the complexing agent can be used in the ultrafiltration-electrodeposition combination method, not only can the concentrated solution be effectively treated, reduce the risk of secondary pollution, and the complexing agent can be used in It is regenerated during the electrodeposition process, and the operation cost is effectively reduced through the reuse of the complexing agent.

为实现上述目的,本发明所采用的技术方案是:To achieve the above object, the technical solution adopted in the present invention is:

在对重金属废水的处理过程中使用一种可再生的重金属络合剂,通过膜分离、电沉积两个步骤的组合处理。在所述组合处理的步骤中包括络合剂与铜离子络合及溶液浓缩、络合剂再生及回用。In the process of treating heavy metal wastewater, a renewable heavy metal complexing agent is used, and the combination of two steps of membrane separation and electrodeposition is used for treatment. The steps of combined treatment include complexing of the complexing agent and copper ions, concentration of the solution, regeneration and recycling of the complexing agent.

膜分离过程中实现络合剂与铜离子络合;电沉积步骤中实现溶液浓缩、络合剂再生及回用。The complexing agent and copper ion complexation are realized in the membrane separation process; the solution concentration, complexing agent regeneration and reuse are realized in the electrodeposition step.

具体方案为:The specific plan is:

(1)将待处理的含重金属铜的废水放入一个带有搅拌器的调节池中。(1) Put the wastewater containing heavy metal copper to be treated into a regulating tank with a stirrer.

(2)向调节池-1中加入水解胶原蛋白作为络合剂,并加入NaOH,控制加入后废水的pH保持在5.5-7.0之间,搅拌器的转速保持在400-600rpm之间,在常温下反应1-2小时,以保证铜离子全部与水解胶原蛋白络合。(2) Add hydrolyzed collagen as a complexing agent in the adjustment tank-1, and add NaOH, control the pH of the wastewater after adding and keep it between 5.5-7.0, the speed of the agitator is kept between 400-600rpm, at normal temperature React for 1-2 hours to ensure that all the copper ions are complexed with the hydrolyzed collagen.

(3)在提升泵-1的作用下,调节池-1中的废水进入多介质过滤器、超滤膜系统,水分子在压力作用下透过超滤膜成为净化水,滤液中铜离子截留率达90%以上,可以回用于生产工艺。铜离子与水解胶原蛋白络合物由于大于超滤膜的微孔孔径而被超滤膜截留,形成浓缩液。(3) Under the action of the lifting pump-1, the wastewater in the regulating tank-1 enters the multi-media filter and ultrafiltration membrane system, and the water molecules pass through the ultrafiltration membrane under pressure to become purified water, and the copper ions in the filtrate are intercepted The rate is more than 90%, and it can be reused in the production process. Copper ions and hydrolyzed collagen complexes are intercepted by the ultrafiltration membrane because they are larger than the micropore diameter of the ultrafiltration membrane, forming a concentrated solution.

(4)膜分离获得的浓缩液回到调节池-1中,当调节池-1中的浓缩液达到2-4倍的浓缩倍率后,关闭调节池到超滤膜系统的提升泵-1,打开调节池-1与调节池-2之间的提升泵-2,将调节池-1中的料液打入调节池-2中。(4) The concentrated solution obtained by membrane separation is returned to the adjustment tank-1, and when the concentrated solution in the adjustment tank-1 reaches a concentration ratio of 2-4 times, the lift pump-1 from the adjustment tank to the ultrafiltration membrane system is closed, Turn on the lifting pump-2 between the adjustment tank-1 and the adjustment tank-2, and pump the feed liquid in the adjustment tank-1 into the adjustment tank-2.

(5)向调节池-2中加入硫酸,控制加入后废水的pH在2-4之间,使水解胶原蛋白与铜离子解络。(5) Add sulfuric acid to the adjustment tank-2, and control the pH of the wastewater after adding to be between 2-4, so as to decomplex the hydrolyzed collagen and copper ions.

(6)打开调节池-2到平板电沉积装置间的提升泵-3,将溶液打入电解槽中进行电解,铜在阴极板上析出,水解胶原蛋白留在电解液中,实现了金属离子与络合剂的分离。(6) Turn on the lifting pump-3 between the adjustment tank-2 and the flat plate electrodeposition device, pour the solution into the electrolytic tank for electrolysis, copper is precipitated on the cathode plate, and the hydrolyzed collagen remains in the electrolyte, realizing the metal ion Separation from complexing agents.

(7)电沉积过程结束后,开启电解槽与调节池-1之间的阀门,再生后的水解胶原蛋白回流到调节池-1中循环使用。(7) After the electrodeposition process is finished, open the valve between the electrolytic cell and the adjustment tank-1, and the regenerated hydrolyzed collagen is returned to the adjustment tank-1 for recycling.

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:

调节池-1:位于超滤膜系统之前,加入的络合剂为水解胶原蛋白,是牛、猪及鱼毛皮中蛋白质经过常规方法水解所得,其分子量为2000-3000。本领域技术人员可以通过常用的技术方法获得,例如:CN101948900A,CN1903918A等。本发明中水解胶原蛋白来源为河北学洋明胶蛋白厂(公司地址:河北省阜城县古城镇武千路78.2公里处北侧),产品名称为水解胶原蛋白粉,CAS号为9007-34-5。废水中重金属铜与加入的水解胶原蛋白质量比为1∶10-1∶25。调节pH为5.5~7.0,搅拌器的转速保持在400-600rpm之间,在常温下反应1-2小时;Conditioning tank-1: Located before the ultrafiltration membrane system, the complexing agent added is hydrolyzed collagen, which is obtained by hydrolyzing the protein in cow, pig and fish fur by conventional methods, and its molecular weight is 2000-3000. Those skilled in the art can obtain it through common technical methods, for example: CN101948900A, CN1903918A, etc. The source of hydrolyzed collagen in the present invention is Hebei Xueyang Gelatin Protein Factory (company address: the north side of 78.2 kilometers away from Wuqian Road, Gucheng Town, Fucheng County, Hebei Province), the product name is hydrolyzed collagen powder, and the CAS number is 9007-34- 5. The mass ratio of the heavy metal copper in the waste water to the added hydrolyzed collagen is 1:10-1:25. Adjust the pH to 5.5-7.0, keep the speed of the agitator between 400-600rpm, and react at room temperature for 1-2 hours;

多介质过滤器:去除水中的悬浮物,降低水的浊度,满足超滤进水要求(浊度小于1.0NTU),市场上现有的商业化、成熟的过滤器都可实现该技术效果,如秦皇岛嘉会环保设备有限公司生产的JX-010型石英砂过滤器(型号JHD-18,JHD-22,JHD-36)、北京源莱水处理设备有限公司生产的YLSS系列石英过滤器(YLSS-500,YLSS-750,YLSS-1000,YLSS-1200)、北京(中西泰安)技术服务有限公司提供的ZWJ29-JDL-3型石英砂过滤器(型号JDL-3,JDL-6,JDL-10,JDL-15)等。本发明所用的为多介质过滤器中的石英砂过滤器。所说的超滤膜系统分离过程中,超滤膜组件为板框式,膜材料采用聚醚砜膜,截留分子量为1000道尔顿。超滤分离过程中,使用的操作压力为0.4-0.6Mpa,废水工作温度25℃~35℃,铜离子平均截留率为90%-92%,出水水质达到工业循环水水质标准,可以回用于工业循环水系统。市场上现有的商业化、成熟的组件都可实现该技术效果,例如:上海世远生物设备工程有限公司生产的小型微滤、超滤平板膜分离系统(SY-MU2010、SY-MU2050、SY-MU-2-500),中试型超滤、纳滤、反渗透膜分离系统(SY-UNR-D3-4040);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)。超滤膜组件:杭州泓泉膜技术有限公司研制生产的改性聚砜(PS)中空纤维膜组件(HQM-4040PS、HQM-6040PS)、立昇企业生产的立升LH3系列超滤膜组件(LH3-1060-V、LH3-0680-V、LH3-0660-V、LH3-0650-V、LH3-0450-V)。膜材料:美国Sepro公司生产的聚砜(PS)膜(PS-20),聚偏氟乙烯(PVDF)膜(PVDF-200,PVDF-350,PVDF-400,PVDF-700),聚丙烯腈(PAN)膜(PAN-50,PAN-200,PAN-350,PAN-400),聚醚砜(PES)膜(PES-5、PES-10、PES-20、PES-900C/D);安得膜分离技术工程(北京)有限公司生产的聚醚砜(PES)超滤膜(PES-1、PES-3、PES-5、PES-8、PES-10、PES-20、PES-30、PES-50),聚砜(PS)超滤膜(PS-20、PS-50),聚偏氟乙烯(PVDF)膜(PVDF-50,PVDF-100),聚丙烯腈(PAN)膜(PAN-100)。上述超滤膜系统分离过程,经过超滤膜处理,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。浓缩比达到2-4倍时超滤过程结束。Multi-media filter: remove suspended solids in water, reduce water turbidity, and meet ultrafiltration water inlet requirements (turbidity is less than 1.0NTU). The existing commercial and mature filters on the market can achieve this technical effect. Such as the JX-010 quartz sand filter (model JHD-18, JHD-22, JHD-36) produced by Qinhuangdao Jiahui Environmental Protection Equipment Co., Ltd., and the YLSS series quartz filter (YLSS) produced by Beijing Yuanlai Water Treatment Equipment Co., Ltd. -500, YLSS-750, YLSS-1000, YLSS-1200), ZWJ29-JDL-3 quartz sand filter (model JDL-3, JDL-6, JDL-10) provided by Beijing (Zhongxi Tai'an) Technical Service Co., Ltd. , JDL-15) etc. What the present invention uses is the quartz sand filter in the multimedia filter. In the separation process of the ultrafiltration membrane system, the ultrafiltration membrane module is a plate and frame type, the membrane material is polyethersulfone membrane, and the molecular weight cut-off is 1000 Daltons. In the process of ultrafiltration separation, the operating pressure used is 0.4-0.6Mpa, the working temperature of wastewater is 25°C-35°C, the average retention rate of copper ions is 90%-92%, and the quality of the effluent water meets the quality standard of industrial circulating water, which can be reused for Industrial circulating water system. The existing commercial and mature components on the market can achieve this technical effect, for example: small microfiltration and ultrafiltration flat membrane separation systems (SY-MU2010, SY-MU2050, SY -MU-2-500), pilot-scale ultrafiltration, nanofiltration, reverse osmosis membrane separation system (SY-UNR-D3-4040); Millipore ultrafiltration system (labscale TFF small tangential flow ultrafiltration system, Congent-M ultrafiltration system, Pellicon ultrafiltration system). Ultrafiltration membrane modules: modified polysulfone (PS) hollow fiber membrane modules (HQM-4040PS, HQM-6040PS) developed and produced by Hangzhou Hongquan Membrane Technology Co., Ltd., Lisheng LH3 series ultrafiltration membrane modules produced by Lisheng Enterprise ( LH3-1060-V, LH3-0680-V, LH3-0660-V, LH3-0650-V, LH3-0450-V). Membrane materials: polysulfone (PS) membrane (PS-20) produced by Sepro Corporation of the United States, polyvinylidene fluoride (PVDF) membrane (PVDF-200, PVDF-350, PVDF-400, PVDF-700), polyacrylonitrile ( PAN) membrane (PAN-50, PAN-200, PAN-350, PAN-400), polyethersulfone (PES) membrane (PES-5, PES-10, PES-20, PES-900C/D); Polyethersulfone (PES) ultrafiltration membranes (PES-1, PES-3, PES-5, PES-8, PES-10, PES-20, PES-30, PES) produced by Membrane Separation Technology Engineering (Beijing) Co., Ltd. -50), polysulfone (PS) ultrafiltration membrane (PS-20, PS-50), polyvinylidene fluoride (PVDF) membrane (PVDF-50, PVDF-100), polyacrylonitrile (PAN) membrane (PAN- 100). In the separation process of the above-mentioned ultrafiltration membrane system, after the ultrafiltration membrane treatment, the heavy metals in the waste liquid are fully concentrated, so that the concentration of metal ions in the concentrated liquid is greatly increased, which is suitable for the recovery of heavy metals by electrodeposition. The ultrafiltration process ends when the concentration ratio reaches 2-4 times.

调节池-2:位于二维平板电沉积装置之前,调节pH为2-4,搅拌器的转速保持在400-600rpm之间,使水解胶原蛋白与铜离子的络合物发生解络合反应。所采用的装置也都为本领域技术人员可以获得的,例如CN03820055.4公布的电化学处理槽,CN86107225公布的双极式电解装置及其单元电解槽,CN1930325公布的用于电化学工艺的电解槽,CN1986898公布的一种惰性电极铝电解槽,CN1995461公布的隔膜法金属阳极电解槽,CN2173247公布的阴极转动分隔式电解槽。Regulating tank-2: located before the two-dimensional plate electrodeposition device, adjust the pH to 2-4, keep the rotation speed of the agitator between 400-600rpm, and decomplex the complex of hydrolyzed collagen and copper ions. The devices adopted are also all available to those skilled in the art, such as the electrochemical treatment tank announced by CN03820055.4, the bipolar electrolysis device and unit electrolyzer thereof announced by CN86107225, the electrolytic process for electrochemical process announced by CN1930325 Tank, a kind of inert electrode aluminum electrolytic cell announced by CN1986898, the diaphragm method metal anode electrolytic cell announced by CN1995461, and the cathode rotating partition type electrolytic cell announced by CN2173247.

所说的电沉积过程中,对溶液进行常温搅拌,搅拌速度为300-500rpm,可以促进铜的传质过程并减小水解胶原蛋白在极板上的吸附;电极材料选用石墨阳极/不锈钢阴极配对电极,槽电压为6.0V-16.0V,电解时间为90min-180min,经电沉积处理后的Cu2+最低浓度小于20mg/L,铜在极板上的回收率最高可达89%。水解胶原蛋白的再生率为84%-86%。During the electrodeposition process, the solution is stirred at room temperature, and the stirring speed is 300-500rpm, which can promote the mass transfer process of copper and reduce the adsorption of hydrolyzed collagen on the plate; the electrode material is a pair of graphite anode/stainless steel cathode Electrode, the cell voltage is 6.0V-16.0V, the electrolysis time is 90min-180min, the minimum concentration of Cu 2+ after electrodeposition treatment is less than 20mg/L, and the recovery rate of copper on the plate can reach up to 89%. The regeneration rate of hydrolyzed collagen is 84%-86%.

上述电沉积过程得到的含再生胶原蛋白的浓缩液回流到调节池中重复利用,与新加入的含铜重金属废水混合并充分反应,在提升泵的作用下再进入多介质过滤器、超滤膜系统,在无新的胶原蛋白补充情况下,对于重金属铜的去除率达到70%以上。The concentrated solution containing regenerated collagen obtained from the above electrodeposition process is returned to the regulating tank for reuse, mixed with the newly added copper-containing heavy metal wastewater and fully reacted, and then enters the multimedia filter and ultrafiltration membrane under the action of the lift pump System, in the absence of new collagen supplementation, the removal rate of heavy metal copper can reach more than 70%.

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,将水解胶原蛋白应用在聚合物强化超滤法和电沉积组合法中,充分发挥了水解胶原蛋白的优势:既容易与铜离子形成络合物,提高超滤过程中铜的去除率,又容易通过特定方法解络合而再生,且在电解过程中不会在极板发生氧化还原反应而遭到破坏。First, the application of hydrolyzed collagen in the combined method of polymer-enhanced ultrafiltration and electrodeposition gives full play to the advantages of hydrolyzed collagen: it is easy to form complexes with copper ions and improve the removal rate of copper in the ultrafiltration process , and it is easy to regenerate by decomplexation by a specific method, and it will not be damaged by redox reaction on the plate during the electrolysis process.

第二,水解胶原蛋白是一种天然物质,无毒性,与超滤膜分离中使用的表面活性剂相比,对环境的危害更小。Second, hydrolyzed collagen is a natural substance, non-toxic, and less harmful to the environment than surfactants used in ultrafiltration membrane separations.

第三,实现了再生后的水解胶原蛋白可以在超滤过程中重复利用,有效降低了运行成本。Third, the regenerated hydrolyzed collagen can be reused in the ultrafiltration process, effectively reducing operating costs.

附图说明 Description of drawings

图1为本可再生重金属络合剂的使用方法流程图。Fig. 1 is the flow chart of the usage method of this renewable heavy metal complexing agent.

具体实施方式 Detailed ways

实施例1:Example 1:

采用本发明方法处理浓度为100mg/L的含铜重金属废水,进水pH值为4.6,水温25℃,以水解胶原蛋白为络合剂,经过超滤膜系统使水质得到净化,浓缩液通过电沉积法处理,实现铜的回收、水解胶原蛋白的再生与循环利用.本过程中所使用的水解胶原蛋白、多介质过滤器、超滤膜系统、二维平板电沉积装置等都为常规废水回收处理装置。本发明所使用的水解胶原蛋白为分子量2000~3000为酶解法所得。具体为:按照CN101948900A的方法将新鲜牛皮为原料,用氢氧化钠溶液处理后,分阶段加入木瓜蛋白酶、碱性蛋白酶,同时加入复合酶解保护剂,经两次酶解后再升温灭酶,经氧化脱色,过滤超滤,收集截留液,喷雾干燥后得到分子量为2000~3000的水解胶原蛋白。或直接购于河北学洋明胶蛋白厂,CAS:9007-34-5。多介质过滤器为北京(中西泰安)技术服务有限公司提供的ZWJ29-JDL-3型石英砂过滤器,超滤膜系统为安得膜分离技术工程(北京)有限公司设计生产的UF-2319中试实验机,二维平板电沉积装置电解槽为PP聚丙烯高分子材料电解槽,阴阳极分别为不锈钢板和石墨板。具体工艺流程如下:步骤1:将待处理的含重金属铜的废水放入一个带有搅拌器的调节池-1中。The method of the present invention is used to treat copper-containing heavy metal wastewater with a concentration of 100mg/L. The pH value of the influent is 4.6, the water temperature is 25°C, and the hydrolyzed collagen is used as a complexing agent. The water quality is purified through an ultrafiltration membrane system, and the concentrated solution is passed through an electric Copper recovery, regeneration and recycling of hydrolyzed collagen are achieved by deposition method. The hydrolyzed collagen, multi-media filter, ultrafiltration membrane system, two-dimensional plate electrodeposition device, etc. used in this process are all recycled from conventional wastewater. Processing device. The hydrolyzed collagen used in the present invention has a molecular weight of 2000-3000 and is obtained by enzymatic hydrolysis. Specifically: according to the method of CN101948900A, fresh cowhide is used as raw material, after being treated with sodium hydroxide solution, papain and alkaline protease are added in stages, and a compound enzymolysis protection agent is added at the same time, after two enzymatic hydrolysis, the temperature is raised to kill the enzyme, After oxidative decolorization, filtration and ultrafiltration, the retentate is collected and spray-dried to obtain hydrolyzed collagen with a molecular weight of 2000-3000. Or directly purchased from Hebei Xueyang Gelatin Protein Factory, CAS: 9007-34-5. The multi-media filter is ZWJ29-JDL-3 quartz sand filter provided by Beijing (Zhongxi Tai'an) Technology Service Co., Ltd., and the ultrafiltration membrane system is UF-2319 designed and produced by Ande Membrane Separation Technology Engineering (Beijing) Co., Ltd. The experimental machine, the two-dimensional flat plate electrodeposition device, the electrolytic cell is a PP polypropylene polymer material electrolytic cell, and the cathode and anode are respectively stainless steel plate and graphite plate. The specific technological process is as follows: Step 1: Put the waste water containing heavy metal copper to be treated into a regulating tank-1 with an agitator.

步骤2:向调节池-1中加入水解胶原蛋白作为络合剂,水解胶原蛋白与铜的质量比为10∶1-25∶1。加入NaOH,调节加入后废水的pH为5.5-7.0,搅拌器的转速为400rpm,在常温下反应1小时,以保证铜离子全部与水解胶原蛋白络合。Step 2: Adding hydrolyzed collagen as a complexing agent to the adjustment pool-1, the mass ratio of hydrolyzed collagen to copper is 10:1-25:1. Add NaOH, adjust the pH of the waste water after adding to 5.5-7.0, the rotation speed of the stirrer is 400rpm, and react at room temperature for 1 hour to ensure that all the copper ions are complexed with the hydrolyzed collagen.

步骤3:在提升泵-1的作用下,调节池-1中的废水通过多介质过滤器,去除水中的悬浮物,降低水的浊度,满足超滤进水要求;之后进入超滤膜系统,使用的操作压力为0.45Mpa,废水工作温度25℃,水分子在压力作用下透过超滤膜成为净化水,滤液中铜离子截留率为93.1%,可以回用于生产工艺。铜离子与水解胶原蛋白络合物由于大于超滤膜的微孔孔径而被超滤膜截留,形成浓缩液。Step 3: Under the action of the lifting pump-1, the wastewater in the regulating tank-1 passes through the multi-media filter to remove suspended solids in the water, reduce the turbidity of the water, and meet the ultrafiltration water inlet requirements; then enter the ultrafiltration membrane system , the operating pressure used is 0.45Mpa, and the working temperature of wastewater is 25°C. Under the action of pressure, water molecules pass through the ultrafiltration membrane to become purified water. The retention rate of copper ions in the filtrate is 93.1%, which can be reused in the production process. Copper ions and hydrolyzed collagen complexes are intercepted by the ultrafiltration membrane because they are larger than the micropore diameter of the ultrafiltration membrane, forming a concentrated solution.

步骤4:膜分离获得的浓缩液回到调节池-1中,当调节池-1中的浓缩液达到2倍的浓缩倍率后,关闭调节池-1到超滤膜系统的提升泵-1,打开调节池-1与调节池-2之间的提升泵-2,将调节池-1中的料液打入调节池-2中。Step 4: The concentrated solution obtained by membrane separation is returned to the regulating tank-1. When the concentrated solution in the regulating tank-1 reaches a concentration ratio of 2 times, the lift pump-1 from the regulating tank-1 to the ultrafiltration membrane system is closed. Turn on the lifting pump-2 between the adjustment tank-1 and the adjustment tank-2, and pump the feed liquid in the adjustment tank-1 into the adjustment tank-2.

步骤5:向调节池-2中加入硫酸,控制加入后废水的pH为2-4,使水解胶原蛋白与铜离子解络。Step 5: adding sulfuric acid to the adjustment pool-2, controlling the pH of the wastewater after adding to 2-4, so as to decomplex the hydrolyzed collagen and copper ions.

步骤6:打开调节池-2到电解槽之间的提升泵-3,溶液通过提升泵-3打入电解槽中进行电沉积过程,对溶液进行常温搅拌,搅拌速度为300rpm,可以促进铜的传质过程并减小水解胶原蛋白在极板上的吸附;电极材料选用石墨阳极/不锈钢阴极配对电极,槽电压为6.0~16.0V,电解时间为90min~180min,铜在阴极板上析出,经电沉积处理后的溶液中Cu2+浓度为18~24mg/L,铜在极板上的回收率为88%~90%。同时,由于铜的析出,使水解胶原蛋白与铜离子分离,水解胶原蛋白留在电解液中而得到再生,水解胶原蛋白的再生率为84%~86%。Step 6: Turn on the lifting pump-3 between the adjustment tank-2 and the electrolytic tank, the solution is pumped into the electrolytic tank through the lifting pump-3 to carry out the electrodeposition process, and the solution is stirred at room temperature at a stirring speed of 300rpm, which can promote the deposition of copper Mass transfer process and reduce the adsorption of hydrolyzed collagen on the plate; the electrode material is graphite anode/stainless steel cathode paired electrode, the cell voltage is 6.0-16.0V, the electrolysis time is 90min-180min, copper is precipitated on the cathode plate, after The concentration of Cu 2+ in the solution after electrodeposition treatment is 18-24 mg/L, and the recovery rate of copper on the pole plate is 88%-90%. At the same time, due to the precipitation of copper, the hydrolyzed collagen is separated from the copper ions, and the hydrolyzed collagen remains in the electrolyte to be regenerated. The regeneration rate of the hydrolyzed collagen is 84% to 86%.

步骤7:电沉积过程结束后,开启电解槽与调节池-1之间的阀门,再生后的水解胶原蛋白回流到调节池-1中,与新进入的含重金属铜的废水混合,充分反应后由提升泵-1打入多介质过滤器、超滤膜系统,开始了第二个循环处理过程。在无新的络合剂加入的情况下,对于铜离子的去除率为80%。Step 7: After the electrodeposition process is over, open the valve between the electrolytic cell and the adjustment tank-1, and the regenerated hydrolyzed collagen flows back into the adjustment tank-1, and mixes with the newly entered wastewater containing heavy metal copper, and after fully reacting It is pumped into the multi-media filter and ultrafiltration membrane system by the lift pump-1, and the second cycle treatment process starts. In the case that no new complexing agent is added, the removal rate of copper ions is 80%.

Claims (9)

1. the method for use of a renewable heavy metal complexing agent is characterized in that this method carries out the combined treatment of membrane sepn, two steps of galvanic deposit to waste water.
2. method of use as claimed in claim 1 in said combined treatment, is applied to heavy metal containing wastewater treatment with complexing agent, and this application comprises complexing agent and cupric ion complexing and solution concentration, complexing agent regeneration and two steps of reuse.
3. according to claim 1 or claim 2 method of use, it is characterized in that: said membrane sepn step comprises:
(1) the pending waste water that contains heavy metal copper is put into an equalizing tank that has whisking appliance.
(2) in equalizing tank-1, add complexing agent, and add NaOH, the pH that control adds back waste water remains between the 5.5-7.0, and the rotating speed of whisking appliance remains between the 400-600rpm, reacted at normal temperatures 1-2 hour, with guarantee cupric ion all with the complexing agent complexing.
(3) under the effect of lift pump-1, the waste water in the equalizing tank-1 gets into more medium filter, ultrafiltration membrane system, and water molecules becomes through ultra-filtration membrane under pressure purifies waste water, and the cupric ion rejection reaches more than 90% in the filtrating, can be back to production technique.The complex compound that cupric ion and complexing agent form forms liquid concentrator owing to held back by ultra-filtration membrane greater than the micropore size of ultra-filtration membrane.
4. like the described method of use of claim 1-3, it is characterized in that: said electrodeposition step comprises:
(4) liquid concentrator that obtains through membrane sepn is got back in the equalizing tank-1; After the liquid concentrator in the equalizing tank-1 reaches 2-4 concentration rate doubly; Close the lift pump-1 of equalizing tank to ultrafiltration membrane system; Open the lift pump-2 between equalizing tank-1 and the equalizing tank-2, the feed liquid in the equalizing tank-1 is squeezed in the equalizing tank-2.
(5) in equalizing tank-2, add sulfuric acid, control adds the pH of back waste water between 2-4, makes complexing agent and cupric ion decomplexing.
(6) open the lift pump-3 of equalizing tank-2 between the dull and stereotyped electric deposition device, solution is squeezed into carried out electrolysis in the electrolyzer, copper is separated out on negative plate, complexing agent is stayed in the electrolytic solution, has realized separating of metals ion and complexing agent.
(7) after electrodeposition process finishes, open the valve between electrolyzer and the equalizing tank-1, the complexing agent after the regeneration is back in the equalizing tank-1 and recycles.
5. like the described method of use of claim 1-4, it is characterized in that: described complexing agent is a Collagen Hydrolysate, is that protein is through ordinary method hydrolysis gained in ox, pig and the fish fur, and its molecular weight is 2000-3000.
6. like the described method of use of claim 3-5, in step (1), the Collagen Hydrolysate mass ratio of heavy metal copper and adding in the waste water is 1: 10-1: 25.
7. like the described method of use of claim 3-5, in step (3), in the described ultrafiltration membrane system sepn process, hyperfiltration membrane assembly is a plate and frame, and mould material adopts poly (ether sulfone) film, and molecular weight cut-off is 1000 dalton.In the ultra-filtration and separation process, the working pressure that uses is 0.4-0.6Mpa, 25 ℃~35 ℃ of waste water working temperatures.
8. like the described method of use of claim 3-5, in step (6), solution is carried out stirring at normal temperature, stirring velocity is 300-500rpm; Electrode materials is selected graphite anode/stainless steel cathode counter-electrodes for use, and bath voltage is 6.0~16.0V, and electrolysis time is 90~180min.
9. like the described method of use of claim 3-8, the regeneration rate of complexing agent is 84%-86%.
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Cited By (12)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN103084065A (en) * 2013-01-14 2013-05-08 天津工业大学 Ultra-filtration membrane removing method of metal ions
CN103785677A (en) * 2014-01-26 2014-05-14 河北欧美环境工程有限公司 Integrated device for heavy metal contaminated soil remediation and leacheate recycling and method thereof
CN104356317A (en) * 2014-10-17 2015-02-18 武汉纺织大学 Sewage treatment material prepared from waste leather scrap, preparation method and application thereof
CN104860494A (en) * 2015-04-23 2015-08-26 浙江环科环境研究院有限公司 Device and method for reduction treatment of sludge by synergistic effect of chelating agent and complex enzyme preparation
CN105541018A (en) * 2015-12-31 2016-05-04 朱辉 Treatment method for removing heavy metals in industrial wastewater
CN105621793A (en) * 2015-12-31 2016-06-01 朱辉 A treatment system for removing heavy metals in industrial wastewater
CN105621815A (en) * 2016-03-10 2016-06-01 广州聚注专利研发有限公司 Method for treating heavy metal wastewater through fish bone dust
CN105618477A (en) * 2014-10-30 2016-06-01 张自学 Methods for purifying soil contaminated by heavy metal chromium
CN107539991A (en) * 2017-09-29 2018-01-05 四川绿源聚能环保科技有限责任公司 A kind of apparatus system for handling chlorosilane slurry raffinate
CN107721063A (en) * 2016-01-14 2018-02-23 张作玮 A kind of food and drink waste water oil removal treatment system
CN108486199A (en) * 2018-03-27 2018-09-04 北京中科众联新能源技术服务有限公司 Water-soluble chelator, preparation method and the process for treating heavy-metal waste water with it
CN119605601A (en) * 2025-01-24 2025-03-14 重庆致清生态环保科技有限公司 Soil matrix prepared based on pyrite slag and its application

Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1899985A (en) * 2006-07-10 2007-01-24 三达膜科技(厦门)有限公司 Treating, recovering and reutilizing method for electroplating waste liquid containing heavy metals
CN1935678A (en) * 2006-09-20 2007-03-28 江南大学 A clean production method for treating electroplating wastewater by nanofiltration
CN101024533A (en) * 2007-02-01 2007-08-29 天津大学 Method of diaphragm separation electrolyzing integrated treatment of wate, water containing heavy metal copper
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 (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1899985A (en) * 2006-07-10 2007-01-24 三达膜科技(厦门)有限公司 Treating, recovering and reutilizing method for electroplating waste liquid containing heavy metals
CN1935678A (en) * 2006-09-20 2007-03-28 江南大学 A clean production method for treating electroplating wastewater by nanofiltration
CN101024533A (en) * 2007-02-01 2007-08-29 天津大学 Method of diaphragm separation electrolyzing integrated treatment of wate, water containing heavy metal copper
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 (15)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
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CN103785677A (en) * 2014-01-26 2014-05-14 河北欧美环境工程有限公司 Integrated device for heavy metal contaminated soil remediation and leacheate recycling and method thereof
CN103785677B (en) * 2014-01-26 2016-08-17 河北欧美环境工程有限公司 Heavy-metal contaminated soil reparation and leacheate recycle integrated apparatus and method thereof
CN104356317A (en) * 2014-10-17 2015-02-18 武汉纺织大学 Sewage treatment material prepared from waste leather scrap, preparation method and application thereof
CN104356317B (en) * 2014-10-17 2019-05-24 武汉纺织大学 Utilize the sewage treating material and its preparation method and application of leather leftover preparation
CN105618477A (en) * 2014-10-30 2016-06-01 张自学 Methods for purifying soil contaminated by heavy metal chromium
CN104860494A (en) * 2015-04-23 2015-08-26 浙江环科环境研究院有限公司 Device and method for reduction treatment of sludge by synergistic effect of chelating agent and complex enzyme preparation
CN105541018A (en) * 2015-12-31 2016-05-04 朱辉 Treatment method for removing heavy metals in industrial wastewater
CN105621793A (en) * 2015-12-31 2016-06-01 朱辉 A treatment system for removing heavy metals in industrial wastewater
CN107721063A (en) * 2016-01-14 2018-02-23 张作玮 A kind of food and drink waste water oil removal treatment system
CN105621815A (en) * 2016-03-10 2016-06-01 广州聚注专利研发有限公司 Method for treating heavy metal wastewater through fish bone dust
CN107539991A (en) * 2017-09-29 2018-01-05 四川绿源聚能环保科技有限责任公司 A kind of apparatus system for handling chlorosilane slurry raffinate
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CN108486199B (en) * 2018-03-27 2020-12-22 北京中科众联新能源技术服务有限公司 Water-soluble chelating agent, preparation method thereof and heavy metal wastewater treatment method using water-soluble chelating agent
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Application publication date: 20120502