CN201952316U - Device for recycling tanning advanced treatment waste water - Google Patents

Device for recycling tanning advanced treatment waste water Download PDF

Info

Publication number
CN201952316U
CN201952316U CN2011200444305U CN201120044430U CN201952316U CN 201952316 U CN201952316 U CN 201952316U CN 2011200444305 U CN2011200444305 U CN 2011200444305U CN 201120044430 U CN201120044430 U CN 201120044430U CN 201952316 U CN201952316 U CN 201952316U
Authority
CN
China
Prior art keywords
ultrafiltration membrane
wastewater
water
electrodialysis
outlet
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
CN2011200444305U
Other languages
Chinese (zh)
Inventor
张世文
王峰
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.)
Boying Xiamen Science and Technology Co Ltd
Original Assignee
Boying Xiamen Science and Technology Co Ltd
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 Boying Xiamen Science and Technology Co Ltd filed Critical Boying Xiamen Science and Technology Co Ltd
Priority to CN2011200444305U priority Critical patent/CN201952316U/en
Application granted granted Critical
Publication of CN201952316U publication Critical patent/CN201952316U/en
Anticipated expiration legal-status Critical
Expired - Fee Related 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
    • Y02ATECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
    • Y02A20/00Water conservation; Efficient water supply; Efficient water use
    • Y02A20/124Water desalination
    • Y02A20/131Reverse-osmosis

Landscapes

  • Water Treatment By Electricity Or Magnetism (AREA)
  • Separation Using Semi-Permeable Membranes (AREA)

Abstract

制革深度处理废水循环利用装置,涉及一种废水处理。装置设纳米催化电解系统、浸没式超滤膜过滤分离系统、超滤膜清洗系统和电渗析系统;纳米催化电解系统设第1截止阀、水泵、纳米催化电解机、沉淀罐和过滤装置;浸没式超滤膜过滤分离系统设第2截止阀、浸没式超滤膜池、鼓风机、曝气器、超滤膜系统、抽吸泵和透析液贮罐;超滤膜清洗系统设清洗液罐、反冲洗泵、第4截止阀和联接管道;电渗析系统设第5截止阀、电渗析机、透析液贮罐和浓缩水贮罐。基于纳米催化电解技术、浸没式超滤技术与电渗析技术相结合应用,且成本较低,效能较高,达到废水再生循环利用。

The utility model relates to a tannery advanced treatment waste water recycling device, which relates to waste water treatment. The device is equipped with nano catalytic electrolysis system, submerged ultrafiltration membrane filtration separation system, ultrafiltration membrane cleaning system and electrodialysis system; The ultrafiltration membrane filtration separation system is equipped with a second cut-off valve, submerged ultrafiltration membrane pool, blower, aerator, ultrafiltration membrane system, suction pump and dialysate storage tank; the ultrafiltration membrane cleaning system is equipped with a cleaning fluid tank, Backwash pump, No. 4 cut-off valve and connecting pipeline; Electrodialysis system is equipped with No. 5 cut-off valve, electrodialysis machine, dialysate storage tank and concentrated water storage tank. Based on the combination of nano-catalytic electrolysis technology, submerged ultrafiltration technology and electrodialysis technology, the cost is low and the efficiency is high, so as to achieve the regeneration and recycling of wastewater.

Description

制革深度处理废水循环利用装置Tannery Advanced Treatment Wastewater Recycling Device

技术领域technical field

本实用新型涉及一种废水处理,尤其是涉及一种基于纳米催化电解技术与电渗析技术的制革深度处理废水循环利用装置。The utility model relates to a waste water treatment, in particular to a tanning advanced treatment waste water recycling device based on nano-catalyzed electrolysis technology and electrodialysis technology.

背景技术Background technique

据统计,我国制革行业每年向环境排放废水达10000万t以上,约占我国工业废水排放总量的0.3%;皮革工业万元产值排污量在轻工行业居第3位,仅次于造纸和酿造行业,可见,制革工业不仅每年消耗大量的淡水资源,同时也排放了大量的废水,对人类健康和整个社会的可持续发展造成了严重威胁。因此应加大制革废水的治理力度,开展制革废水处理和中水回用无论是从节约淡水资源角度还是从环保角度而言都是十分必要的,具有重要的现实意义和战略意义。According to statistics, my country's tanning industry discharges more than 100 million tons of wastewater to the environment every year, accounting for about 0.3% of my country's total industrial wastewater discharge; the output value of the leather industry ranks third in the light industry, second only to papermaking And the brewing industry, it can be seen that the tanning industry not only consumes a large amount of fresh water resources every year, but also discharges a large amount of wastewater, which poses a serious threat to human health and the sustainable development of the entire society. Therefore, the treatment of tannery wastewater should be strengthened, and the treatment of tannery wastewater and the reuse of reclaimed water are very necessary both from the perspective of saving fresh water resources and from the perspective of environmental protection, and have important practical and strategic significance.

制革工业排放的废水存在有机污染浓度高、悬浮物质多、水量大、废水成份复杂等问题,其中含有有毒物质硫与铬。按照生产工艺过程,制革工业废水由七部分组成:高浓度氯化物的原皮洗涤水和酸浸水、含石灰与硫化钠的强碱性脱毛浸灰废水、含三价铬的兰色铬鞣废水、含丹宁与没食子酸的茶褐色植鞣废水、含油脂及其皂化物的脱脂废水、加脂染色废水和各工段冲洗废水。其中,以脱脂废水,脱毛浸灰废水、铬鞣废水污染最为严重。The wastewater discharged by the tanning industry has problems such as high concentration of organic pollution, large amount of suspended matter, large water volume, and complex wastewater components, which contain toxic substances such as sulfur and chromium. According to the production process, tannery industrial wastewater is composed of seven parts: raw hide washing water and pickling water with high concentration of chloride, strong alkaline dehairing and liming wastewater containing lime and sodium sulfide, blue chrome tanning wastewater containing trivalent chromium , tea brown vegetable tanning wastewater containing tannin and gallic acid, degreasing wastewater containing oil and its saponification, fatliquoring dyeing wastewater and washing wastewater of various workshops. Among them, degreasing wastewater, dehairing and liming wastewater, and chrome tanning wastewater are the most polluted.

(1)脱脂废水:我国猪皮生产占制革生产的80%,在猪皮生产的脱脂废水中,油脂含量高达10000(mg/L),CODCr20000(mg/L)。油脂废水占总废水4%,但油脂废水的耗氧负荷却占到总负荷的30%~40%。(1) Degreasing wastewater: pigskin production in my country accounts for 80% of tanning production. In the degreasing wastewater produced from pigskin, the oil content is as high as 10,000 (mg/L), and the CODCr is 20,000 (mg/L). Grease wastewater accounts for 4% of the total wastewater, but the oxygen consumption load of grease wastewater accounts for 30% to 40% of the total load.

(2)脱水浸灰废水:脱毛浸灰废水是硫化物的污染源。废水CODCr20000~40000(mg/L),BOD54000(mg/L),硫化钠1200~1500(mg/L),pH为12,脱毛浸灰废水占总废水的10%,而耗氧负荷占总负荷40%。(2) Dehydration and liming wastewater: Depilation and liming wastewater is a pollution source of sulfide. Wastewater CODCr20000~40000(mg/L), BOD54000(mg/L), sodium sulfide 1200~1500(mg/L), pH 12, dehairing and liming wastewater accounted for 10% of the total wastewater, and the oxygen consumption load accounted for the total load 40%.

(3)铬鞣废水:铬鞣废水是三价铬的污染源。铬鞣过程,铬盐的附着率60%~70%,即有30%~40%的铬盐进入废水。铬鞣度水Cr3+3000-4000(mg/L),CODCr10000(mg/L),BOD52000mg/L。(3) Chrome tanning wastewater: Chrome tanning wastewater is a pollution source of trivalent chromium. In the chrome tanning process, the adhesion rate of chromium salt is 60% to 70%, that is, 30% to 40% of chromium salt enters the wastewater. Chrome tanning water Cr3+3000-4000(mg/L), CODCr10000(mg/L), BOD52000mg/L.

传统的制革废水处理技术是将各工序废水收集混合,一起纳入污水处理系统,但由于废水中含有大量的硫化物和铬离子,极易对微生物产生抑制作用。所以目前比较合理的是“原液单独处理、综合废水统一处理”的工艺路线[8],将脱脂废水、浸灰脱毛废水、铬鞣废水分别进行处理并回收有价值的资源,然后与其它废水混合统一处理。The traditional tannery wastewater treatment technology is to collect and mix the wastewater from various processes and put them into the sewage treatment system together. However, because the wastewater contains a large amount of sulfide and chromium ions, it is very easy to inhibit microorganisms. Therefore, at present, it is more reasonable to use the process route of "separate treatment of raw liquid and unified treatment of comprehensive wastewater" [8], to treat degreasing wastewater, liming and dehairing wastewater, and chrome tanning wastewater separately and recover valuable resources, and then mix them with other wastewater Unified processing.

制革厂的各路废水集中后,称为制革综合废水制革废水中有机物含量及硫化物、铬化物含量高,耗氧量大,其废水的污染情况十分严重,主要表现在以下几个方面:After the wastewater from various channels of the tannery is concentrated, it is called comprehensive tannery wastewater. The content of organic matter, sulfide and chromium in the tannery wastewater is high, and the oxygen consumption is large. The pollution of the wastewater is very serious, mainly in the following aspects aspect:

(1)色度:皮革废水色度较大,主要由植鞣、染色、铬鞣和灰碱废液造成;(1) Chromaticity: leather wastewater has relatively high chromaticity, which is mainly caused by vegetable tanning, dyeing, chrome tanning and gray alkali waste liquid;

(2)碱性:皮革废水总体上呈碱性,综合废水pH值在8~12之间。其碱性主要来自于脱毛等工序用的石灰、烧碱和硫化钠;(2) Alkaline: The leather wastewater is generally alkaline, and the pH value of the comprehensive wastewater is between 8 and 12. Its alkalinity mainly comes from lime, caustic soda and sodium sulfide used in depilation and other processes;

(3)硫化物:制革废水中的硫化物主要来自于灰碱法脱毛废液,少部分来自于硫化物助软的浸水废液及蛋白质的分解产物。含硫废液遇酸易产生H2S气体,含硫污泥在厌氧条件下也会释放出H2S气体;(3) Sulfides: The sulfides in tannery wastewater mainly come from the ash-alkali hair removal waste liquid, and a small part comes from the immersion waste liquid and protein decomposition products softened by sulfides. Sulfur-containing waste liquid is easy to produce H 2 S gas when it encounters acid, and sulfur-containing sludge will also release H 2 S gas under anaerobic conditions;

(4)铬离子:制革废水中的铬离子主要以Cr3+形态存在,含量一般在100~3000mg/L。通常是先经过中和沉淀,过滤后汇入综合废水池中;(4) Chromium ions: Chromium ions in tannery wastewater mainly exist in the form of Cr3+, and the content is generally 100-3000mg/L. Usually, after neutralization and sedimentation, it is filtered and then poured into the comprehensive wastewater pool;

(5)有机污染物:制革废水中蛋白质等有机物含量较高,又含有一定量的还原性物质,所以BOD5和CODCr很高。(5) Organic pollutants: The content of organic matter such as protein in tannery wastewater is relatively high, and it also contains a certain amount of reducing substances, so BOD5 and CODCr are very high.

制革过程中各个工段排放的废水水质相差很大,各工段排放的废水汇集后的综合废水pH在8~12之间,色度、CODCr、SS、BOD5浓度都很高,有毒、有害物质及盐类的浓度也很高,制革行业综合废水水质(测试平均值)参见下表。The quality of wastewater discharged from each section of the tanning process varies greatly. After the wastewater discharged from each section is collected, the pH of the comprehensive wastewater is between 8 and 12, and the concentration of chroma, CODCr, SS, and BOD5 is very high. Toxic and harmful substances and The concentration of salts is also very high. See the table below for the comprehensive wastewater quality (test average) of the tannery industry.

 pHpH   色度(倍)Chromaticity (times)   CODCrCODCr   SSSS   NH3-NNH 3 -N   S2- S 2-  CrCr   BOD5BOD5  8~128~12   500~3500500~3500   3000~40003000~4000   2000~40002000~4000   250~300250~300   50~10050~100  100~3000100~3000   1500~20001500~2000

注:单位除pH、色度外其余均为mg/LNote: The unit is mg/L except for pH and chroma

目前,用于制革废水治理的方法主要有:混凝沉淀法、吸附法、高级氧化法、直接循环回用法、气浮法、加酸吸收法、催化氧化法、生化法等,每种方法都具有各种的优缺点。由于单一的处理方法很难达到效果,在实际运用中,通常是根据要处理废水的实际情况,将几种方法结合使用。黄振雄介绍了广东某皮革厂采用絮凝沉淀-活性污泥法-接触氧化法组合工艺处理制革废水,自2003年12月投产至今处理效果稳定,进水COD为3000~3500mg/L时,出水COD约40mg/L,各项出水指标均达到广东省地方标准(DB44/26-2001)一级标准。张杰等应用序批式活性污泥法(SBR)对河南某制革厂的废水进行处理。首先采用物化法除去废水中的大量有毒物质和部分有机物,再经过SBR法生化降解可溶性有机物。设计日处理量为800m3,当进水COD在2500mg/L时,出水COD在100mg/L左右,远低于国标二级标准(COD<300mg/L),该工程的运行成本为0.8元/吨。运行结果表明,用SBR工艺处理制革废水,对水质变化的适应性好,耐负荷冲击能力强,尤其适合制革废水相对集中排放及水质多变的特点。而且,SBR处理工艺投资较省,运行成本较一般活性污泥法低。贾秋平等采用涡凹气浮+二段接触氧化工艺,对沈阳市某制革厂的废水处理设施进行改造,不仅使处理后的废水达到排放要求,提高了处理能力和效果,而且回收了80%以上的Cr3+,使处理后的废水部分回用。在进水COD 3647mg/L时,经本工艺处理后,出水COD浓度为77mg/L,低于辽宁省《DB21-60-89》新扩改二级标准(COD<100mg/L)。杨建军、高忠柏介绍了辛集市试炮营制革小区采用物化+氧化沟工艺,对原有射流曝气污水处理系统进行改造和增容,改造后的处理水量增至4800m3/d,可对进水COD为6100mg/L左右的废水进行有效处理。实际运行表明,该改造工艺的处理效率较高,出水水质达到国家《污水综合排放标准》二级标准。陶如钧介绍好浙江某制革工业区采用混凝沉淀+水解酸化+CAST工艺,对来自于准备、鞣制和其它湿加工工段的综合废水进行处理。设计最大进水流量6000m3/d,废水中的硫离子通过预曝气,并在反应池加FeSO4和助凝剂PAC,从而沉淀去除,Cr3+通过在反应池中与NaOH发生沉淀反应而去除。生化处理采用兼氧和好氧相结合的工艺,兼氧采用接触式水解酸化工艺,可提高废水的可生化性,同时去除部分COD和SS。好氧采用CAST工艺为改良的SBR工艺,具有有机物去除率高、抗冲击负荷能力强等特点。孙亚兵等人在中国专利CN100371268C公开了一种采用电解处理制革废水的方法,处理后的废水COD去除率达60%~80%、氨氮去除率达50%~70%、硫化物去除率达95%以上、悬浮物去除率达70%~80%、色度去除率达85%以上,对大肠杆菌的灭杀率达99%以上,但是,这一方法存在阳极消耗量多,能耗高。At present, the methods used for tannery wastewater treatment mainly include: coagulation precipitation method, adsorption method, advanced oxidation method, direct recycling method, air flotation method, acid absorption method, catalytic oxidation method, biochemical method, etc., each method Both have various advantages and disadvantages. Because a single treatment method is difficult to achieve the effect, in practical applications, several methods are usually combined according to the actual situation of the wastewater to be treated. Huang Zhenxiong introduced that a tannery in Guangdong adopts the combined process of flocculation sedimentation-activated sludge method-contact oxidation method to treat tannery wastewater. Since it was put into operation in December 2003, the treatment effect has been stable. About 40mg/L, all effluent indicators have reached the first-level standard of the local standard of Guangdong Province (DB44/26-2001). Zhang Jie et al applied sequencing batch activated sludge process (SBR) to treat wastewater from a tannery in Henan. Firstly, the physicochemical method is used to remove a large amount of toxic substances and some organic matter in the wastewater, and then the SBR method is used to biochemically degrade the soluble organic matter. The designed daily treatment capacity is 800m 3 . When the influent COD is 2500mg/L, the effluent COD is about 100mg/L, which is far below the national standard secondary standard (COD<300mg/L). The operating cost of the project is 0.8 yuan/L Ton. The operation results show that using SBR process to treat tannery wastewater has good adaptability to water quality changes and strong load impact resistance, especially suitable for the relatively concentrated discharge of tannery wastewater and the characteristics of variable water quality. Moreover, the investment of SBR treatment process is relatively low, and the operating cost is lower than that of general activated sludge process. Jia Qiuping used the vortex concave air flotation + two-stage contact oxidation process to transform the wastewater treatment facilities of a tannery in Shenyang City. Not only did the treated wastewater meet the discharge requirements, but the treatment capacity and effect were improved, and 80 % Cr 3+ , so that part of the treated wastewater can be reused. When the influent COD is 3647mg/L, after being treated by this process, the effluent COD concentration is 77mg/L, which is lower than the newly expanded secondary standard of "DB21-60-89" in Liaoning Province (COD<100mg/L). Yang Jianjun and Gao Zhongbai introduced that the Xinji City Test Paoying tannery area adopted the physicochemical + oxidation ditch process to transform and increase the capacity of the original jet aeration sewage treatment system. Effectively treat wastewater with a COD of about 6100 mg/L. The actual operation shows that the treatment efficiency of the transformation process is high, and the effluent water quality meets the second-level standard of the national "Comprehensive Wastewater Discharge Standard". Tao Rujun introduced that a tanning industrial zone in Zhejiang Province adopts coagulation sedimentation + hydrolysis acidification + CAST process to treat comprehensive wastewater from preparation, tanning and other wet processing sections. The maximum influent flow rate is designed to be 6000m 3 /d. The sulfur ions in the wastewater are pre-aerated, and FeSO 4 and coagulant PAC are added to the reaction tank to remove them by precipitation. Cr 3+ is precipitated and reacted with NaOH in the reaction tank. And removed. The biochemical treatment adopts a combination of facultative and aerobic processes, and the facultative process adopts a contact hydrolysis acidification process, which can improve the biodegradability of wastewater and remove part of COD and SS at the same time. The aerobic CAST process is an improved SBR process, which has the characteristics of high organic matter removal rate and strong impact load resistance. Sun Yabing and others disclosed a method of electrolytic treatment of tannery wastewater in Chinese patent CN100371268C. The COD removal rate of the treated wastewater reached 60% to 80%, the ammonia nitrogen removal rate reached 50% to 70%, and the sulfide removal rate reached 95%. %, the removal rate of suspended solids is 70%-80%, the removal rate of chroma is more than 85%, and the killing rate of Escherichia coli is more than 99%. However, this method has a lot of anode consumption and high energy consumption.

综上所述,采用现有的制革废水处理方法处理的废水只能达到排放标准,但没有达到工业废水再生循环利用标准。在此,把采用现有的制革废水处理方法处理后达到排放标准的二沉池废水称为制革深度处理废水,它排放多,水资源浪费大,成本高,容易带来二次污染,故急需一种原材料消耗少、废水经过处理后能够再生循环利用,且成本低、操作简易的制革深度处理废水净化再生循环利用方法,以利于降低皮革生产中的单位产品物料消耗,节约淡水资源,保护环境。To sum up, the wastewater treated by the existing tannery wastewater treatment method can only meet the discharge standard, but does not meet the industrial wastewater regeneration and recycling standard. Here, the secondary sedimentation tank wastewater that meets the discharge standard after being treated by the existing tannery wastewater treatment method is called tannery advanced treatment wastewater, which has a lot of discharge, a large waste of water resources, high cost, and is likely to cause secondary pollution. Therefore, there is an urgent need for a method for purifying, regenerating and recycling tannery advanced treatment wastewater that consumes less raw materials, can be regenerated and recycled after treatment, and is low in cost and easy to operate, so as to reduce the material consumption per unit product in leather production and save fresh water resources. ,protect environment.

发明内容Contents of the invention

本实用新型的目的在于针对现有的制革废水处理方法中所存在的固定资产投资大,能耗大,废水的再生成本较高,回用率偏低,浪费水资源等问题,提供一种基于纳米催化电解技术、浸没式超滤技术与电渗析技术相结合应用,且成本较低,效能较高,使之达到废水再生循环利用的制革深度处理废水循环利用装置。The purpose of the utility model is to solve the existing problems in the existing tannery wastewater treatment method, such as large investment in fixed assets, high energy consumption, high regeneration cost of wastewater, low reuse rate, waste of water resources, etc., to provide a Based on the combination of nano-catalytic electrolysis technology, submerged ultrafiltration technology and electrodialysis technology, the cost is low and the efficiency is high, making it a tannery advanced treatment wastewater recycling device for wastewater regeneration and recycling.

本实用新型设有纳米催化电解系统、浸没式超滤膜过滤分离系统、超滤膜清洗系统和电渗析系统;The utility model is equipped with a nano-catalysis electrolysis system, a submerged ultrafiltration membrane filtration separation system, an ultrafiltration membrane cleaning system and an electrodialysis system;

所述纳米催化电解系统用于纳米催化电解、沉淀和过滤等处理,纳米催化电解系统设有第1截止阀、水泵、纳米催化电解机、沉淀罐和过滤装置;第1截止阀的进口外接制革废水生化处理系统的二沉池排水口,水泵的进口接第1截止阀的出口,水泵的出口接纳米催化电解机的进口,纳米催化电解机的出口接沉淀罐的进口,过滤装置的进口接沉淀罐的出口;The nano-catalysis electrolysis system is used for nano-catalysis electrolysis, precipitation and filtration, etc. The nano-catalysis electrolysis system is provided with a first cut-off valve, a water pump, a nano-catalysis electrolysis machine, a sedimentation tank and a filter device; The outlet of the secondary sedimentation tank of the leather wastewater biochemical treatment system, the inlet of the water pump is connected to the outlet of the first stop valve, the outlet of the water pump is connected to the inlet of the nano-catalyzed electrolyzer, the outlet of the nano-catalyzed electrolyzer is connected to the inlet of the sedimentation tank, and the inlet of the filter device Connect to the outlet of the sedimentation tank;

所述浸没式超滤膜过滤分离系统用于将纳米催化电解系统所得制革净化废水过滤、分离得透析水和浓缩水,浸没式超滤膜过滤分离系统设有第2截止阀、浸没式超滤膜池、鼓风机、曝气器、超滤膜系统、抽吸泵和透析液贮罐,所述浸没式超滤膜池经进水管和第2截止阀与纳米催化电解系统的沉淀罐出口连接,超滤膜系统的超滤膜浸没在浸没式超滤膜池中的制革净化废水中,抽吸泵从超滤膜内侧将水负压抽吸过膜壁,产生的透析水通过抽吸泵收集到透析液贮罐用于进一步经过电渗析脱盐得供生产上循环利用的再生水,浸没式超滤膜池的出口依次经过抽吸泵、第3截止阀接透析液贮罐;The submerged ultrafiltration membrane filtration separation system is used to filter and separate the tannery purification wastewater obtained from the nano-catalytic electrolysis system to obtain dialysis water and concentrated water. Membrane pool, blower, aerator, ultrafiltration membrane system, suction pump and dialysate storage tank, the submerged ultrafiltration membrane pool is connected to the outlet of the sedimentation tank of the nanocatalytic electrolysis system through the water inlet pipe and the second shut-off valve , the ultrafiltration membrane of the ultrafiltration membrane system is immersed in the tannery purification wastewater in the submerged ultrafiltration membrane pool, the suction pump sucks the water through the membrane wall from the inside of the ultrafiltration membrane under negative pressure, and the dialysis water produced is passed through the suction The pump collects the dialysate storage tank for further electrodialysis desalination to obtain regenerated water for recycling in production. The outlet of the submerged ultrafiltration membrane pool passes through the suction pump and the third stop valve to connect to the dialysate storage tank in sequence;

所述超滤膜清洗系统用于清洗超滤膜过滤分离系统,超滤膜清洗系统设有清洗液罐、反冲洗泵、第4截止阀和联接管道,清洗液罐的出口接反冲洗泵的进口,反冲洗泵的出口接第4截止阀的进口,第4截止阀的出口接浸没式超滤膜过滤分离系统的超滤膜系统;The ultrafiltration membrane cleaning system is used to clean the ultrafiltration membrane filtration separation system. The ultrafiltration membrane cleaning system is provided with a cleaning liquid tank, a backwash pump, the 4th shut-off valve and a connecting pipeline, and the outlet of the cleaning liquid tank is connected to the backwash pump. The inlet and the outlet of the backwash pump are connected to the inlet of the fourth stop valve, and the outlet of the fourth stop valve is connected to the ultrafiltration membrane system of the submerged ultrafiltration membrane filtration separation system;

所述电渗析系统设有第5截止阀、电渗析机、透析液贮罐和浓缩水贮罐,第5截止阀的出口接浸没式超滤膜过滤分离系统的浸没式超滤膜池的出口,电渗析机的进水口接第5截止阀的出口,电渗析机的透析水出口接透析液贮罐,电渗析机的浓缩水出口接浓缩水贮罐。The electrodialysis system is provided with the 5th stop valve, electrodialysis machine, dialysate storage tank and concentrated water storage tank, the outlet of the 5th stop valve is connected to the outlet of the submerged ultrafiltration membrane pool of the submerged ultrafiltration membrane filtration separation system , the water inlet of the electrodialysis machine is connected to the outlet of the fifth stop valve, the dialysis water outlet of the electrodialysis machine is connected to the dialysate storage tank, and the concentrated water outlet of the electrodialysis machine is connected to the concentrated water storage tank.

所述过滤可采用砂滤、多介质过滤或微滤等。The filtration can be sand filtration, multimedia filtration or microfiltration.

所述浸没式超滤膜过滤系统可去除废水中的固体杂质、浮游生物、细菌、胶体等,浸没式膜采用外压开放式过滤设计,可被直接浸入到废水中,因此系统的占地面积小。其工作条件是:常温~45℃,工作压力为3~50kPa。The submerged ultrafiltration membrane filtration system can remove solid impurities, plankton, bacteria, colloids, etc. in wastewater. The submerged membrane adopts an external pressure open filtration design and can be directly immersed in wastewater, so the system occupies an area of Small. Its working conditions are: room temperature ~ 45 ℃, working pressure 3 ~ 50kPa.

所述电渗析系统可采用倒极电渗析系统(EDR)、液膜电渗析系统(EDLM)、填充电渗析系统(EDI)、双极性电渗析系统(EDMB)或无极水电渗析系统等;所述电渗析系统可以将经过浸没式超滤膜过滤分离系统所得透析水经过电渗析分离成透析水(脱盐水)和浓缩水,使其满足工业生产中不同的生产工艺用水的质量要求。电渗析的工作条件是0.5~3.0kg/cm2,操作电压50~250V,电流强度1~3A。所述电渗析系统可以根据废水中的含盐量进行一段脱盐、两段脱盐或三段脱盐,从而使再生水的含盐量满足工业生产的工艺用水要求,其脱盐率可以达45%~80%。The electrodialysis system can adopt inverted electrodialysis system (EDR), liquid membrane electrodialysis system (EDLM), filled electrodialysis system (EDI), bipolar electrodialysis system (EDMB) or electrodeless hydrodialysis system etc.; The electrodialysis system can separate the dialysis water obtained through the submerged ultrafiltration membrane filtration separation system into dialysis water (de-salted water) and concentrated water through electrodialysis, so that it can meet the quality requirements of different production process water in industrial production. The working condition of electrodialysis is 0.5-3.0kg/cm 2 , the operating voltage is 50-250V, and the current intensity is 1-3A. The electrodialysis system can perform one-stage desalination, two-stage desalination or three-stage desalination according to the salt content in the wastewater, so that the salt content of the regenerated water meets the process water requirements for industrial production, and its desalination rate can reach 45% to 80%. .

所述电渗析系统可采用一段电渗析系统、二段电渗析系统、三段电渗析系统和四段电渗析系统。The electrodialysis system can adopt one-stage electrodialysis system, two-stage electrodialysis system, three-stage electrodialysis system and four-stage electrodialysis system.

采用本实用新型可进行制革深度处理废水循环利用,具体方法包括以下步骤:Adopting the utility model can carry out tannery advanced treatment wastewater recycling, and the specific method includes the following steps:

1)纳米催化电解:将经过生化处理后二沉池的制革深度处理废水经水泵提取后,输入纳米催化电解机中进行纳米催化电解,再经过阀门进入沉淀罐沉淀,然后输入过滤装置过滤,除去废水中因纳米催化电解产生的固体杂质、浮游生物、细菌、胶体得净化废水。1) Nano-catalyzed electrolysis: After biochemical treatment, the tanning advanced treatment wastewater in the secondary sedimentation tank is extracted by the water pump, and then input into the nano-catalytic electrolysis machine for nano-catalytic electrolysis, and then enters the sedimentation tank through the valve for precipitation, and then enters the filter device for filtration. Remove solid impurities, plankton, bacteria, and colloids produced by nano-catalytic electrolysis in wastewater to purify wastewater.

2)浸没式超滤过滤:将经过纳米催化电解系统系处理后的净化制革废水经管道流入浸没式超滤系统进行超滤膜过滤处理,得透析水。2) Submerged ultrafiltration filtration: The purified tannery wastewater treated by the nano-catalytic electrolysis system flows into the submerged ultrafiltration system through the pipeline for ultrafiltration membrane filtration to obtain dialysis water.

3)电渗析:将经过浸没式超滤系统处理所得的净化制革废水经过水泵送入电渗析系统,进行电渗析脱盐,得脱盐水和浓缩水。3) Electrodialysis: The purified tannery wastewater treated by the submerged ultrafiltration system is pumped into the electrodialysis system for desalination by electrodialysis to obtain desalted water and concentrated water.

在步骤1)中,所述纳米催化电解的工作电压可为2~250V,相邻两个电极间的电压可为2~18V,相邻两个电极间的最佳电压为3~8V,电流密度可为10~280mA/cm2,电流密度最佳为50~230mA/cm2,制革深度处理废水经过电解后经阀门流入沉淀罐中。In step 1), the working voltage of the nano-catalyzed electrolysis can be 2-250V, the voltage between two adjacent electrodes can be 2-18V, the optimal voltage between two adjacent electrodes is 3-8V, and the current The density can be 10-280mA/cm 2 , and the best current density is 50-230mA/cm 2 . The advanced treatment wastewater of tannery is electrolyzed and flows into the sedimentation tank through the valve.

所述制革废水的氯化钠含量可为6‰~30‰,最好为0.6‰~1.3‰,氯化钠含量不够时可添加工业氯化钠补充至6‰~30‰。The sodium chloride content of the tanning wastewater can be 6‰-30‰, preferably 0.6‰-1.3‰. If the sodium chloride content is not enough, industrial sodium chloride can be added to supplement it to 6‰-30‰.

所述纳米催化电解是将制革深度处理废水经过纳米催化电解使之生成初生态的氯[Cl]、羟基和初生态的氧[O],用以氧化分解废水中的有机物和氨氮,并杀灭废水中微生物,同时,在电场作用下使废水中的悬浮物、胶体、带电微粒凝聚形成较大颗粒。The nano-catalytic electrolysis is to generate nascent chlorine [Cl], hydroxyl and nascent oxygen [O] through nano-catalyzed electrolysis of tannery advanced treatment wastewater, which is used to oxidize and decompose organic matter and ammonia nitrogen in wastewater, and kill Kill the microorganisms in the wastewater, and at the same time, under the action of the electric field, the suspended solids, colloids, and charged particles in the wastewater are agglomerated to form larger particles.

在步骤2)中,所述超滤膜过滤的工作条件可为:常温~45℃,工作压力3~50kPa。In step 2), the working conditions of the ultrafiltration membrane filtration may be: normal temperature to 45° C., working pressure of 3 to 50 kPa.

在步骤3)中,所述电渗析系统的工作条件可为:0.5~3.0kg/cm2,操作电压50~250V,电流强度1~3A。In step 3), the working conditions of the electrodialysis system may be: 0.5-3.0 kg/cm 2 , operating voltage 50-250V, and current intensity 1-3A.

透析水用于制革生产中的柔革和染色工序,浓缩水用于制革生产中的洗皮和浸灰工序。因此,废水可以全部再生循环利用。The dialyzed water is used in softening and dyeing processes in tanning production, and the concentrated water is used in rinsing and liming processes in tanning production. Therefore, the waste water can be completely regenerated and recycled.

本实用新型与双膜法(超滤+反渗透或超滤+纳滤)处理方法比较,既克服了其成本过高的缺陷,又克服了废水处理效果不理想,排放的废水污染环境和的缺陷,并且可以化腐朽为神气,变废物为资源,将现有的制革深度处理废水净化及回收再生循环利用,具有以下突出优点:Compared with the double-membrane method (ultrafiltration+reverse osmosis or ultrafiltration+nanofiltration) treatment method, the utility model not only overcomes the defect of high cost, but also overcomes the unsatisfactory wastewater treatment effect, the discharged wastewater pollutes the environment and defects, and can turn decay into spirit, turn waste into resources, purify and recycle the existing tannery advanced treatment wastewater, and has the following outstanding advantages:

1、水的回收率高、成本低水的回收率高达85%~100%,排放废水少,能耗低,运行费用低于传统生化末端双膜过滤处理技术的成本,吨水(回用水)成本远低于现行自来水价;1. High water recovery rate and low cost The water recovery rate is as high as 85% to 100%, less waste water discharge, low energy consumption, and the operating cost is lower than the cost of traditional biochemical terminal double-membrane filtration treatment technology, per ton of water (reuse water) The cost is much lower than the current tap water price;

2、脱色效果好迅速氧化分解废水中的有色物质,脱色效果好。如:二沉池废水色度为200时,经纳米催化电解机处理后,色度小于8;2. Good decolorization effect It quickly oxidizes and decomposes the colored substances in the wastewater, and the decolorization effect is good. For example: when the chromaticity of the wastewater in the secondary sedimentation tank is 200, the chromaticity is less than 8 after being treated by a nano-catalyzed electrolytic machine;

3、大幅度降低废水COD的总排放量传统的生化末端加膜过滤技术,虽然可以实现部分中水回用,但不能降低废水COD的总排放量,本实用新型能迅速氧化分解废水中的有机物,大幅度降低废水COD的总排放量;3. Significantly reduce the total discharge of wastewater COD. Although the traditional biochemical end-membrane filtration technology can realize partial reuse of reclaimed water, it cannot reduce the total discharge of wastewater COD. The utility model can quickly oxidize and decompose organic matter in wastewater , significantly reducing the total discharge of wastewater COD;

4、根除膜的生物污染能杀灭废水中的细菌,根除膜的生物污染,大幅度减少膜的清洗次数,降低膜清洁再生成本,提高膜的使用效率,延长膜的使用寿命,减少膜更换成本;4. Eradication of membrane biofouling can kill bacteria in wastewater, eradicate membrane biofouling, greatly reduce membrane cleaning times, reduce membrane cleaning and regeneration costs, improve membrane usage efficiency, prolong membrane life, and reduce membrane replacement cost;

5、没有二次污染采用纳米催化电解技术对二沉池废水处理的工艺替代物化处理工艺,不用加入絮凝剂、脱色剂和气浮剂等化学物质,不仅节省成本,而且节约物质消耗和不产生二次污染;5. There is no secondary pollution. Nano catalytic electrolysis technology is used to replace the physical and chemical treatment process of secondary sedimentation tank wastewater without adding flocculants, decolorizers, air flotation agents and other chemical substances, which not only saves costs, but also saves material consumption and does not produce secondary secondary pollution;

6、大幅度减少污泥采用本实用新型处理废水时,在二沉池出水后采用纳米催化电解技术替代物化工艺,不用加入絮凝剂、脱色剂等化学物质,污泥只有传统技术的二分之一;6. Significantly reduce sludge When the utility model is used to treat wastewater, nano-catalyzed electrolysis technology is used to replace the physical and chemical process after the water is discharged from the secondary sedimentation tank, without adding flocculant, decolorizer and other chemical substances, and the sludge is only half of the traditional technology one;

7、占地少生产工艺流程短,设备结构紧凑,占地少;7. Less land occupation, short production process, compact equipment structure and less land occupation;

8、回用水质高再生循环水无色、无味,水质远高于GB/T19923-2005《城市污水再生水利用工业用水水质》标准;8. Recycled water is of high quality, colorless and odorless, and the water quality is much higher than the standard of GB/T19923-2005 "Water Quality for Urban Sewage Recycled Water Utilization Industry";

9、以电渗析脱盐替代反渗析脱盐或纳滤脱盐,固定资产投资大幅度减少,设备运行时能耗大幅度下降。9. Replacing reverse osmosis desalination or nanofiltration desalination with electrodialysis desalination, the investment in fixed assets is greatly reduced, and the energy consumption during equipment operation is greatly reduced.

采用纳米催化电解具有如下突出效果:(1)用纳米催化电解产生的初生态的氯[Cl]、羟基和初生态氧[O]杀灭废水中微生物,使废水中微生物活体下降到30个/ml以下,消除微生物对膜材料的污染。(2)氧化分解废水中的氨氮,使残留氨氮进一步氧化,氨氮的脱除率可达60~90%。(3)大幅度降低废水的色度,经过了生化、物化等多种方法处理后二沉池的制革深度处理废水的色度在60~200之间,一般的处理方法很难进一步脱色度,经过纳米催化电解可以将制革深度处理废水的色度从60~200之间降低到1~8。(4)氧化分解废水中的有机物,残留染料快速降低CODCr。(5)使废水中的悬浮物、胶体、带电微粒在电场作用下凝聚形成较大颗粒后,经过过滤去除得净化废水。(6)废水中的重金属离子向电解机电解槽的阴极移动,在阴极形成沉淀,从而降低废水中的重金属离子含量。The use of nano-catalyzed electrolysis has the following outstanding effects: (1) Use the nascent chlorine [Cl], hydroxyl and nascent oxygen [O] produced by nano-catalyzed electrolysis to kill microorganisms in wastewater, reducing the number of microorganisms in wastewater to 30/ Below ml, to eliminate microbial contamination of membrane materials. (2) Oxidize and decompose the ammonia nitrogen in the wastewater to further oxidize the residual ammonia nitrogen, and the removal rate of ammonia nitrogen can reach 60-90%. (3) Significantly reduce the chromaticity of wastewater. After biochemical, physical and chemical treatment, the chromaticity of the tanning advanced treatment wastewater in the secondary sedimentation tank is between 60 and 200. It is difficult to further decolorize by general treatment methods , After nano-catalyzed electrolysis, the chromaticity of tannery advanced treatment wastewater can be reduced from 60 to 200 to 1 to 8. (4) Oxidize and decompose the organic matter in the wastewater, and the residual dye quickly reduces COD Cr . (5) After the suspended solids, colloids, and charged particles in the wastewater are condensed under the action of an electric field to form larger particles, they are filtered and removed to obtain purified wastewater. (6) The heavy metal ions in the wastewater move to the cathode of the electrolytic cell of the electrolyzer and form a precipitate at the cathode, thereby reducing the content of heavy metal ions in the wastewater.

附图说明Description of drawings

图1为本实用新型实施例的结构组成示意图。Fig. 1 is a schematic diagram of the structure and composition of an embodiment of the utility model.

具体实施方式Detailed ways

本实用新型是在对现有制革深度处理废水的成份、性质和现有处理方案进行深入系统的对比研究之后完成的对制革深度处理废水的净化和循环利用用工艺的设计,它通过纳米催化电解、沉淀、过滤、浸没式超滤和电渗析等方法的组合运用,从而形成一种特别适合于制革深度处理废水的净化及循环利用的装置及其方法。The utility model is a process design for the purification and recycling of the advanced treatment wastewater of the tannery after the in-depth and systematic comparative study of the components, properties and existing treatment schemes of the advanced treatment wastewater of the tannery industry. The combination of catalytic electrolysis, precipitation, filtration, immersion ultrafiltration and electrodialysis forms a device and method that is especially suitable for the purification and recycling of tannery advanced treatment wastewater.

以下实施例将结合附图对本实用新型作进一步的说明。The following embodiments will further illustrate the utility model in conjunction with the accompanying drawings.

参见图1,本实用新型实施例设有:Referring to Fig. 1, the utility model embodiment is provided with:

纳米催化电解系统:纳米催化电解系统用于纳米催化电解、沉淀等处理步骤。纳米催化电解系统设有截止阀11、供水泵12、纳米催化电解机13、沉淀罐14;截止阀11的进口外接印染废水(二沉池)排出口,供水泵12的进口接截止阀11的出口,供水泵12的出口接纳米催化电解机13的进口,纳米催化电解罐13的出口接沉淀罐14的进口。Nano catalytic electrolysis system: The nano catalytic electrolysis system is used for nano catalytic electrolysis, precipitation and other processing steps. The nano-catalysis electrolysis system is provided with stop valve 11, water supply pump 12, nano-catalysis electrolysis machine 13, sedimentation tank 14; The outlet, the outlet of the water supply pump 12 is connected to the inlet of the nano-catalysis electrolysis machine 13, and the outlet of the nano-catalysis electrolysis tank 13 is connected to the inlet of the sedimentation tank 14.

浸没式超滤膜过滤分离系统:浸没式超滤膜过滤分离系统用于将纳米催化电解系统所得制革净化废水过滤、分离得透析液(水)和浓缩液;浸没式超滤膜过滤分离系统设有截止阀21、超滤膜系统22、鼓风机23、曝气器24、浸没式超滤膜池25、抽吸泵26、截止阀27和透析液(水)贮罐28;截止阀21的进口接纳米催化电解系统沉淀罐14的出口,截止阀21的出口接浸没式超滤膜池25的进口,浸没式超滤膜池25的出口依次经过抽吸泵26、截止阀27进入透析液(水)贮罐28。Submerged ultrafiltration membrane filtration separation system: The submerged ultrafiltration membrane filtration separation system is used to filter and separate the tannery purification wastewater obtained from the nano-catalytic electrolysis system to obtain dialysate (water) and concentrate; the submerged ultrafiltration membrane filtration separation system Be provided with stop valve 21, ultrafiltration membrane system 22, air blower 23, aerator 24, submerged ultrafiltration membrane pool 25, suction pump 26, stop valve 27 and dialysate (water) storage tank 28; The inlet is connected to the outlet of the sedimentation tank 14 of the nanocatalytic electrolysis system, the outlet of the stop valve 21 is connected to the inlet of the submerged ultrafiltration membrane pool 25, and the outlet of the submerged ultrafiltration membrane pool 25 enters the dialysate through the suction pump 26 and the shut-off valve 27 in turn (water) storage tank 28.

超滤膜清洗系统:超滤膜清洗系统用于清洗超滤膜过滤分离系统,设有清洗液罐31、反冲洗泵32、截止阀33;清洗液罐31的出口接反冲洗泵32的进口,反冲洗泵32的出口接截止阀33的进口,截止阀33的出口接超滤膜系统22。Ultrafiltration membrane cleaning system: the ultrafiltration membrane cleaning system is used to clean the ultrafiltration membrane filtration separation system, and is equipped with a cleaning liquid tank 31, a backwash pump 32, and a stop valve 33; the outlet of the cleaning liquid tank 31 is connected to the inlet of the backwash pump 32 , the outlet of the backwash pump 32 is connected to the inlet of the stop valve 33 , and the outlet of the stop valve 33 is connected to the ultrafiltration membrane system 22 .

电渗析系统:电渗析系统设有截止阀41、供水泵42、电渗析机43、透析液(水)贮罐44、浓缩液贮罐45。电渗析机设有进水口、透析液(水)出口、浓缩水出口。浸没式超滤系统所得制革净化废水通过截止阀41和供水泵42进入电渗析机43,经过电渗析机分离成透析液(水)和浓缩液,透析液(水)经过透析液(水)出口贮存于透析液(水)贮罐44中,浓缩液经过浓缩水出口贮存于浓缩液贮罐45;透析水用于制革生产中的柔革和染色工序,浓缩水用于制革生产中的洗皮和浸灰工序。Electrodialysis system: The electrodialysis system is equipped with a stop valve 41 , a water supply pump 42 , an electrodialysis machine 43 , a dialysate (water) storage tank 44 , and a concentrated solution storage tank 45 . The electrodialysis machine is provided with a water inlet, a dialysate (water) outlet, and a concentrated water outlet. The tannery purified wastewater obtained by the submerged ultrafiltration system enters the electrodialysis machine 43 through the shut-off valve 41 and the water supply pump 42, and is separated into the dialysate (water) and concentrated liquid through the electrodialysis machine, and the dialysate (water) passes through the dialysate (water) The outlet is stored in the dialysate (water) storage tank 44, and the concentrated solution is stored in the concentrated solution storage tank 45 through the concentrated water outlet; the dialyzed water is used for soft leather and dyeing processes in the leather production, and the concentrated water is used in the leather production Peeling and liming process.

以下给出采用图1所示的制革深度处理废水净化装置实施例的制革废水的净化再生和循环利用方法。The method for purifying, regenerating and recycling tannery wastewater using the embodiment of the tannery advanced treatment wastewater purification device shown in FIG. 1 is given below.

实施例1Example 1

150吨/日制革深度处理废水的净化再生及循环利用方法。150 tons/day tannery advanced treatment wastewater purification regeneration and recycling method.

所述的印染深度处理废水经测定指标如表1所示。The measured indexes of the printing and dyeing advanced treatment wastewater are shown in Table 1.

表1Table 1

  序号serial number   项目 project   单位unit   测定值 measured value   序号serial number   项目 project   单位unit   测定值 measured value   1 1   CODCr COD Cr   mg/Lmg/L   130130   55   氨氮Ammonia nitrogen   mg/Lmg/L   3.83.8   2 2   SSSS   mg/Lmg/L   2525   66   含盐量Salt content   ‰   7.67.6   33   浊度Turbidity   NTUNTU   9 9   77   pHpH   8.18.1   44   色度Chroma   8080   8 8   电导率Conductivity   μS/cmμS/cm   23502350

150吨制革深度处理废水经供水泵按7.5T/h的流速提取后,输入纳米催化电解机中,纳米催化电解水直接进入沉淀罐,沉淀后进入浸没超滤膜系统除去水中的固体杂质、浮游生物、细菌、胶体得净化废水。150 tons of tannery advanced treatment wastewater is extracted by the water supply pump at a flow rate of 7.5T/h, and then input into the nano-catalytic electrolysis machine. The nano-catalytic electrolyzed water directly enters the sedimentation tank, and after precipitation, it enters the submerged ultrafiltration membrane system to remove solid impurities in the water. Plankton, bacteria, and colloids can purify wastewater.

所述纳米催化电解的工作电压为8~9V,电流强度为500~510A,纳米催化电解产生的初生态的氯[Cl]、羟基和初生态氧[O],杀灭废水中微生物、氧化分解废水中的有机物,并使废水中的悬浮物、胶体、带电微粒在电场作用下形成较大颗粒后,经过浸没式超滤膜过滤分离系统去除,使废水净化,测定SDI为0.9。The working voltage of the nano-catalytic electrolysis is 8-9V, and the current intensity is 500-510A. The nascent chlorine [Cl], hydroxyl and nascent oxygen [O] produced by the nano-catalytic electrolysis can kill microorganisms in wastewater, oxidize and decompose The organic matter in the wastewater, and the suspended solids, colloids, and charged particles in the wastewater are formed into larger particles under the action of an electric field, and then are removed by the submerged ultrafiltration membrane filtration separation system to purify the wastewater. The measured SDI is 0.9.

经过纳米催化电解单元和浸没式超滤膜过滤分离系统净化所得的净化废水经过截止阀、供水泵和进水口进入电渗析机中进行电渗析脱盐处理,分离成透析水和浓缩水,透析水经过透析水出口和管道进入透析液贮罐,浓缩水经过浓缩水出口和管道进入浓缩水贮罐中。The purified wastewater purified by the nano-catalytic electrolysis unit and the submerged ultrafiltration membrane filtration separation system enters the electrodialysis machine through the stop valve, water supply pump and water inlet for electrodialysis desalination treatment, and is separated into dialysis water and concentrated water, and the dialysis water passes through The dialysis water outlet and the pipeline enter the dialysis fluid storage tank, and the concentrated water enters the concentrated water storage tank through the concentrated water outlet and the pipeline.

所述的电渗析系统为倒极电渗析系统(EDR),电渗析的工作条件是0.5kg/cm2,操作电压50~250V,电流强度1~3A。The electrodialysis system is an inverted electrode electrodialysis system (EDR), and the working condition of the electrodialysis is 0.5kg/cm 2 , the operating voltage is 50-250V, and the current intensity is 1-3A.

所述透析水和浓缩液的流速分别为7T/h和1.0T/h,透析水用于制革生产中的柔革和染色工序,浓缩水用于制革生产中的洗皮和浸灰工序,废水的回收率为100%,回用水的质量如表2所示,浓缩废水的指标如表3所示。The flow rates of the dialysis water and the concentrated solution are 7T/h and 1.0T/h respectively, the dialysis water is used for soft leather and dyeing process in tanning production, and the concentrated water is used for rinsing and liming process in tanning production , the recovery rate of wastewater is 100%, the quality of recycled water is shown in Table 2, and the index of concentrated wastewater is shown in Table 3.

表2Table 2

  序号serial number   项目 project   单位unit   测定值 measured value   序号serial number   项目 project   单位unit   测定值 measured value   1 1   CODCr COD Cr   mg/Lmg/L   1919   44   色度Chroma   1 1   2 2   SSSS   mg/Lmg/L   未检出 not detected   55   pHpH   6.76.7   33   浊度Turbidity   NTUNTU   1.11.1   66   电导率Conductivity   μS/cmμS/cm   420420

表3table 3

  序号serial number   项目 project   单位unit   测定值 measured value   序号serial number   项目 project   单位unit   测定值 measured value   1 1   CODCr COD Cr   mg/Lmg/L   8888   55   含盐量Salt content   ‰   1.81.8   2 2   SSSS   mg/Lmg/L   2525   66   pHpH   8.58.5   33   浊度Turbidity   NTUNTU   2.52.5   77   电导率Conductivity   μS/cmμS/cm   39003900   44   色度Chroma   8 8

实施例2Example 2

3000吨/日制革深度处理废水的净化再生及循环利用方法。3000 tons/day tannery advanced treatment wastewater purification regeneration and recycling method.

所述的制革深度处理废水经测定制革深度处理印染废水的指标如表4所示:The indicators of the advanced treatment of tannery wastewater after determination are shown in Table 4:

表4Table 4

  序号serial number   项目 project   单位unit   测定值 measured value   序号serial number   项目 project   单位unit   测定值 measured value   1 1   CODCr COD Cr   mg/Lmg/L   5656   55   含盐量Salt content   ‰   0.60.6

  2 2   SSSS   mg/Lmg/L   1111   66   pHpH   7.77.7   33   浊度Turbidity   NTUNTU   66   77   电导率Conductivity   μS/cmμS/cm   11001100   44   色度Chroma   6060

制革深度处理废水经供水泵按150T/h流速提取后,输入纳米催化电解罐中,纳米催化电解水直接进入沉淀罐,中和沉淀后经超滤膜系统除去水中的固体杂质、浮游生物、细菌、胶体得净化废水。After being extracted by the water supply pump at a flow rate of 150T/h, the advanced treatment wastewater of tannery is input into the nano-catalytic electrolysis tank, and the nano-catalytic electrolyzed water directly enters the sedimentation tank, and after neutralization and precipitation, the solid impurities, plankton, and Bacteria and colloids can purify wastewater.

所述制革深度处理废水由于含盐量较低,先加入工业氯化钠将其含盐量调节到8.5‰,然后再进行纳米催化电解,纳米催化电解的工作电压为5~6V,电流强度为1560~1580A,纳米催化电解产生初生态的氯[Cl]、羟基和初生态氧[O],以杀灭废水中微生物、氧化分解废水中的有机物,并使废水中的悬浮物、胶体、带电微粒在电场作用下形成较大颗粒后,经过浸没式超滤膜过滤分离系统去除使水净化废水,测定SDI为1.3。Due to the low salt content of the tannery advanced treatment wastewater, industrial sodium chloride is first added to adjust its salt content to 8.5‰, and then nano-catalytic electrolysis is performed. The working voltage of nano-catalytic electrolysis is 5-6V, and the current intensity 1560~1580A, nano-catalyzed electrolysis produces nascent chlorine [Cl], hydroxyl and nascent oxygen [O] to kill microorganisms in wastewater, oxidize and decompose organic matter in wastewater, and make suspended solids, colloids, After the charged particles form larger particles under the action of the electric field, they are removed by the submerged ultrafiltration membrane filtration separation system to purify the wastewater, and the measured SDI is 1.3.

经过纳米催化电解单元和浸没式超滤膜过滤分离单元净化所得的净化废水经过经过截止阀、供水泵和进水口进入电渗析机中进行电渗析脱盐处理,分离成透析水和浓缩水,透析水经过透析水出口和管道进入透析液贮罐,浓缩水经过浓缩水出口和管道进入浓缩水贮罐中。The purified wastewater purified by the nano-catalytic electrolysis unit and the submerged ultrafiltration membrane filtration separation unit enters the electrodialysis machine through the stop valve, water supply pump and water inlet for electrodialysis desalination treatment, and is separated into dialysis water and concentrated water, and dialysis water The dialysate storage tank enters through the dialysis water outlet and the pipeline, and the concentrated water enters the concentrated water storage tank through the concentrated water outlet and the pipeline.

所述的电渗析系统为填充电渗析系统(EDI),电渗析的工作条件是操作电压3.0kg/cm2,操作电压150~250V,电流强度2~3A。The electrodialysis system is a filled electrodialysis system (EDI), and the working conditions of the electrodialysis are operating voltage 3.0kg/cm 2 , operating voltage 150-250V, and current intensity 2-3A.

所述透析水和浓缩水的流速分别为105T/h和45T/h,透析水用于制革生产中的柔革和染色工序,浓缩水用于制革生产中的洗皮和浸灰工序,废水的回收率为100%,回用水的质量如表5所示,浓缩废水的指标如表6所示。The flow rates of the dialysis water and concentrated water are 105T/h and 45T/h respectively, the dialysis water is used for soft leather and dyeing process in tanning production, and the concentrated water is used for leather washing and liming process in tanning production, The recovery rate of waste water is 100%, the quality of recycled water is shown in Table 5, and the indicators of concentrated waste water are shown in Table 6.

表5table 5

  序号serial number   项目 project   单位unit   测定值 measured value   序号serial number   项目 project   单位unit   测定值 measured value   1 1   CODCr COD Cr   mg/Lmg/L   1919   44   色度Chroma   1 1   2 2   SSSS   mg/Lmg/L   未检出 not detected   55   pHpH   7.17.1   33   浊度Turbidity   NTUNTU   1.11.1   66   电导率Conductivity   μS/cmμS/cm   359359

表6Table 6

  序号serial number   项目 project   单位unit   测定值 measured value   序号serial number   项目 project   单位unit   测定值 measured value   1 1   CODCr COD Cr   mg/Lmg/L   7575   44   含盐量Salt content   ‰   15.515.5   2 2   SSSS   mg/Lmg/L   3838   55   pHpH   7.97.9

  33   浊度Turbidity   NTUNTU   2.62.6   66   电导率Conductivity   μS/cmμS/cm   32003200

实施例3Example 3

6000吨/日制革深度处理废水的净化再生及循环利用方法。6000 tons/day tannery advanced treatment wastewater purification regeneration and recycling method.

所述制革深度处理废水的净化再生及循环利用装置,经测定印染深度处理印染废水的指标如表7所示。The indicators of the purification, regeneration and recycling device for the advanced treatment of tannery wastewater are shown in Table 7.

表7Table 7

  序号serial number   项目 project   单位unit   测定值 measured value   序号serial number   项目 project   单位unit   测定值 measured value   1 1   CODCr COD Cr   mg/Lmg/L   9191   44   含盐量Salt content   ‰   0.90.9   2 2   SSSS   mg/Lmg/L   22 twenty two   55   pHpH   7.77.7   33   浊度Turbidity   NTUNTU   7.47.4   66   电导率Conductivity   μS/cmμS/cm   31003100

制革深度处理废水经供水泵按300T/h流速提取后,输入纳米催化电解罐中,纳米催化电解水直接进入沉淀罐,沉淀后经浸没式超滤膜系统除去水中的固体杂质、浮游生物、细菌、胶体得净化废水。After being extracted by the water supply pump at a flow rate of 300T/h, the advanced treatment wastewater of tannery is input into the nano-catalysis electrolysis tank, and the nano-catalysis electrolysis water directly enters the sedimentation tank, and after precipitation, the solid impurities, plankton, and Bacteria and colloids can purify wastewater.

所述的制革深度处理废水含盐量较低,纳米催化电解的工作电压为12~13V,电流强度为3760~3800A。纳米催化电解产生的初生态的氯[Cl]、羟基和初生态氧[O],杀灭废水中微生物、氧化分解废水中的有机物,并使废水中的悬浮物、胶体、带电微粒在电场作用下形成较大颗粒后,经过浸没式超滤膜过滤分离系统去除使水净化废水,测定SDI为1.3。The tannery advanced treatment wastewater has a low salt content, the working voltage of the nano-catalyzed electrolysis is 12-13V, and the current intensity is 3760-3800A. The nascent chlorine [Cl], hydroxyl, and nascent oxygen [O] produced by nano-catalytic electrolysis kill microorganisms in wastewater, oxidize and decompose organic matter in wastewater, and make suspended solids, colloids, and charged particles in wastewater act in an electric field After the larger particles are formed, they are removed by the submerged ultrafiltration membrane filtration separation system to purify the waste water, and the measured SDI is 1.3.

经过纳米催化电解单元和浸没式超滤膜过滤分离单元净化所得的净化废水经过经过截止阀、供水泵和进水口进入电渗析机中进行电渗析脱盐处理,分离成透析水和浓缩水,透析水经过透析水出口和管道进入透析液贮罐,浓缩水经过浓缩水出口和管道进入浓缩水贮罐中。The purified wastewater purified by the nano-catalytic electrolysis unit and the submerged ultrafiltration membrane filtration separation unit enters the electrodialysis machine through the stop valve, water supply pump and water inlet for electrodialysis desalination treatment, and is separated into dialysis water and concentrated water, and dialysis water The dialysate storage tank enters through the dialysis water outlet and the pipeline, and the concentrated water enters the concentrated water storage tank through the concentrated water outlet and the pipeline.

所述的电渗析系统为双极性电渗析系统(EDMB),电渗析的工作条件是操作电压2.3kg/cm2,操作电压190~250V,电流强度2~3A。The electrodialysis system is a bipolar electrodialysis system (EDMB), and the working conditions of the electrodialysis are operating voltage 2.3kg/cm 2 , operating voltage 190-250V, and current intensity 2-3A.

所述透析水和浓缩水的流速分别为255T/h和45T/h,透析水用于制革生产中的柔革和染色工序,浓缩水用于制革生产中的洗皮和浸灰工序,废水的回收率为100%,回用水的质量如表8所示,浓缩废水的指标如表9所示。The flow rates of the dialysis water and the concentrated water are 255T/h and 45T/h respectively, the dialysis water is used for soft leather and dyeing process in the tanning production, and the concentrated water is used for the washing and liming process in the tanning production, The recovery rate of wastewater is 100%, the quality of reused water is shown in Table 8, and the indicators of concentrated wastewater are shown in Table 9.

表8Table 8

  序号serial number   项目 project   单位unit   测定值 measured value   序号serial number   项目 project   单位unit   测定值 measured value   1 1   CODCr COD Cr   mg/Lmg/L   21 twenty one   44   色度Chroma   1 1   2 2   SSSS   mg/Lmg/L   未检出 not detected   55   pHpH   7.37.3   33   浊度Turbidity   NTUNTU   1.31.3   66   电导率Conductivity   μS/cmμS/cm   480480

表9Table 9

  序号serial number   项目 project   单位unit   测定值 measured value   序号serial number   项目 project   单位unit   测定值 measured value   1 1   CODCr COD Cr   mg/Lmg/L   9696   55   含盐量Salt content   ‰   2.72.7   2 2   SSSS   mg/Lmg/L   1515   66   pHpH   7.97.9   33   浊度Turbidity   NTUNTU   33   77   电导率Conductivity   μS/cmμS/cm   45004500   44   色度Chroma   8 8

Claims (4)

1.制革深度处理废水循环利用装置,其特征在于设有纳米催化电解系统、浸没式超滤膜过滤分离系统、超滤膜清洗系统和电渗析系统;1. The tannery advanced treatment wastewater recycling device is characterized in that it is equipped with a nano-catalyzed electrolysis system, a submerged ultrafiltration membrane filtration separation system, an ultrafiltration membrane cleaning system and an electrodialysis system; 所述纳米催化电解系统用于纳米催化电解、沉淀和过滤处理,纳米催化电解系统设有第1截止阀、水泵、纳米催化电解机、沉淀罐和过滤装置;第1截止阀的进口外接制革废水生化处理系统的二沉池排水口,水泵的进口接第1截止阀的出口,水泵的出口接纳米催化电解机的进口,纳米催化电解机的出口接沉淀罐的进口,过滤装置的进口接沉淀罐的出口;The nano-catalysis electrolysis system is used for nano-catalysis electrolysis, precipitation and filtration treatment. The nano-catalysis electrolysis system is provided with a first stop valve, a water pump, a nano-catalysis electrolysis machine, a sedimentation tank and a filter device; the import of the first stop valve is externally connected to the tannery The outlet of the secondary settling tank of the wastewater biochemical treatment system, the inlet of the water pump is connected to the outlet of the first stop valve, the outlet of the water pump is connected to the inlet of the nano-catalyzed electrolyzer, the outlet of the nano-catalyzed electrolyzer is connected to the inlet of the sedimentation tank, and the inlet of the filter device is connected to the outlet of the settling tank; 所述浸没式超滤膜过滤分离系统用于将纳米催化电解系统所得制革净化废水过滤、分离得透析水和浓缩水,浸没式超滤膜过滤分离系统设有第2截止阀、浸没式超滤膜池、鼓风机、曝气器、超滤膜系统、抽吸泵和透析液贮罐,所述浸没式超滤膜池经进水管和第2截止阀与纳米催化电解系统的沉淀罐出口连接,超滤膜系统的超滤膜浸没在浸没式超滤膜池中的制革净化废水中,抽吸泵从超滤膜内侧将水负压抽吸过膜壁,产生的透析水通过抽吸泵收集到透析液贮罐用于进一步经过电渗析脱盐得供生产上循环利用的再生水,浸没式超滤膜池的出口依次经过抽吸泵、第3截止阀接透析液贮罐;The submerged ultrafiltration membrane filtration separation system is used to filter and separate the tannery purification wastewater obtained from the nano-catalytic electrolysis system to obtain dialysis water and concentrated water. Membrane pool, blower, aerator, ultrafiltration membrane system, suction pump and dialysate storage tank, the submerged ultrafiltration membrane pool is connected to the outlet of the sedimentation tank of the nanocatalytic electrolysis system through the water inlet pipe and the second shut-off valve , the ultrafiltration membrane of the ultrafiltration membrane system is immersed in the tannery purification wastewater in the submerged ultrafiltration membrane pool, the suction pump sucks the water through the membrane wall from the inside of the ultrafiltration membrane under negative pressure, and the dialysis water produced is passed through the suction The pump collects the dialysate storage tank for further electrodialysis desalination to obtain regenerated water for recycling in production. The outlet of the submerged ultrafiltration membrane pool passes through the suction pump and the third stop valve to connect to the dialysate storage tank in sequence; 所述超滤膜清洗系统用于清洗超滤膜过滤分离系统,超滤膜清洗系统设有清洗液罐、反冲洗泵、第4截止阀和联接管道,清洗液罐的出口接反冲洗泵的进口,反冲洗泵的出口接第4截止阀的进口,第4截止阀的出口接浸没式超滤膜过滤分离系统的超滤膜系统;The ultrafiltration membrane cleaning system is used to clean the ultrafiltration membrane filtration separation system. The ultrafiltration membrane cleaning system is provided with a cleaning liquid tank, a backwash pump, the 4th shut-off valve and a connecting pipeline, and the outlet of the cleaning liquid tank is connected to the backwash pump. The inlet and the outlet of the backwash pump are connected to the inlet of the fourth stop valve, and the outlet of the fourth stop valve is connected to the ultrafiltration membrane system of the submerged ultrafiltration membrane filtration separation system; 所述电渗析系统设有第5截止阀、电渗析机、透析液贮罐和浓缩水贮罐,第5截止阀的出口接浸没式超滤膜过滤分离系统的浸没式超滤膜池的出口,电渗析机的进水口接第5截止阀的出口,电渗析机的透析水出口接透析液贮罐,电渗析机的浓缩水出口接浓缩水贮罐。The electrodialysis system is provided with the 5th stop valve, electrodialysis machine, dialysate storage tank and concentrated water storage tank, the outlet of the 5th stop valve is connected to the outlet of the submerged ultrafiltration membrane pool of the submerged ultrafiltration membrane filtration separation system , the water inlet of the electrodialysis machine is connected to the outlet of the fifth stop valve, the dialysis water outlet of the electrodialysis machine is connected to the dialysate storage tank, and the concentrated water outlet of the electrodialysis machine is connected to the concentrated water storage tank. 2.如权利要求1所述的制革深度处理废水循环利用装置,其特征在于所述浸没式超滤膜过滤系统的工作条件是:常温~45℃,工作压力为3~50kPa。2. The tannery advanced treatment wastewater recycling device according to claim 1, characterized in that the working conditions of the submerged ultrafiltration membrane filtration system are: normal temperature to 45° C., and working pressure of 3 to 50 kPa. 3.如权利要求1所述的制革深度处理废水循环利用装置,其特征在于所述电渗析系统采用倒极电渗析系统、液膜电渗析系统、填充电渗析系统、双极性电渗析系统或无极水电渗析系统。3. The tannery advanced treatment waste water recycling device as claimed in claim 1, characterized in that the electrodialysis system adopts an inverted electrodialysis system, a liquid membrane electrodialysis system, a filled electrodialysis system, and a bipolar electrodialysis system Or electrodeless hydrodialysis system. 4.如权利要求1所述的制革深度处理废水循环利用装置,其特征在于所述电渗析系统的工作条件是0.5~3.0kg/cm2,操作电压50~250V,电流强度1~3A。4. The tannery advanced treatment wastewater recycling device according to claim 1, characterized in that the working conditions of the electrodialysis system are 0.5-3.0kg/cm 2 , operating voltage 50-250V, and current intensity 1-3A.
CN2011200444305U 2011-02-22 2011-02-22 Device for recycling tanning advanced treatment waste water Expired - Fee Related CN201952316U (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN2011200444305U CN201952316U (en) 2011-02-22 2011-02-22 Device for recycling tanning advanced treatment waste water

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN2011200444305U CN201952316U (en) 2011-02-22 2011-02-22 Device for recycling tanning advanced treatment waste water

Publications (1)

Publication Number Publication Date
CN201952316U true CN201952316U (en) 2011-08-31

Family

ID=44496438

Family Applications (1)

Application Number Title Priority Date Filing Date
CN2011200444305U Expired - Fee Related CN201952316U (en) 2011-02-22 2011-02-22 Device for recycling tanning advanced treatment waste water

Country Status (1)

Country Link
CN (1) CN201952316U (en)

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102086072A (en) * 2011-03-11 2011-06-08 波鹰(厦门)科技有限公司 Cyclic utilization device of dyeing and printing advanced treatment wastewater and method thereof
CN102145949A (en) * 2011-02-22 2011-08-10 波鹰(厦门)科技有限公司 Tanning advanced treatment wastewater recycling device and method
CN103130363A (en) * 2011-11-28 2013-06-05 通用电气公司 Desalination system and desalination method
CN104874291A (en) * 2015-06-18 2015-09-02 中国科学院青岛生物能源与过程研究所 Device and method of electro-synthesis coupled membrane separation

Cited By (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102145949A (en) * 2011-02-22 2011-08-10 波鹰(厦门)科技有限公司 Tanning advanced treatment wastewater recycling device and method
CN102145949B (en) * 2011-02-22 2013-02-13 波鹰(厦门)科技有限公司 Tanning advanced treatment wastewater recycling device and method
CN102086072A (en) * 2011-03-11 2011-06-08 波鹰(厦门)科技有限公司 Cyclic utilization device of dyeing and printing advanced treatment wastewater and method thereof
CN102086072B (en) * 2011-03-11 2012-12-26 波鹰(厦门)科技有限公司 Cyclic utilization method of dyeing and printing advanced treatment wastewater
CN103130363A (en) * 2011-11-28 2013-06-05 通用电气公司 Desalination system and desalination method
CN104874291A (en) * 2015-06-18 2015-09-02 中国科学院青岛生物能源与过程研究所 Device and method of electro-synthesis coupled membrane separation

Similar Documents

Publication Publication Date Title
CN101979344B (en) Nano catalytic electrolysis technology and membrane technology-based leather wastewater treatment and recycling method
CN102010107B (en) Treatment and cyclic utilization device and method of tannery wastewater
EP2657198B1 (en) Printing and dyeing wastewater treatment and reuse apparatus and method therefor
CN101428945B (en) Method and apparatus for treating and recycling carbonized wastewater
CN102674628B (en) Sewage treatment and regeneration cyclic utilization device and sewage treatment and regeneration cyclic utilization method
CN102120678B (en) Sewage recycling device based on electrolysis and membrane biological reactor technology and method thereof
CN103253838B (en) Recycling device used for papermaking advanced treatment wastewater and based on chemical decalcification
CN103214153B (en) Regenerative cycle and utilization method for papermaking deep-treatment wastewater
CN102295373A (en) Papermaking wastewater cycling and utilizing apparatus and method based on electrochemical and electrodialysis technologies
CN102086072A (en) Cyclic utilization device of dyeing and printing advanced treatment wastewater and method thereof
CN101781048B (en) Low ammonia nitrogen waste water treatment and recycling method
CN102145949B (en) Tanning advanced treatment wastewater recycling device and method
CN102107971A (en) Papermaking wastewater advanced treatment and recycling device and method thereof
CN201952316U (en) Device for recycling tanning advanced treatment waste water
CN100371268C (en) A kind of treatment method of tannery wastewater
CN103214154B (en) Regenerative cycle and utilization device for papermaking deep-treatment wastewater
CN201842735U (en) Tanning waste water treatment recycling device based on nano catalytic electrolysis technology and membrane technology
CN201915009U (en) Tannery wastewater treatment recycling device based on catalytic electrolysis and biochemical technique
CN2856037Y (en) Sewage reclaiming treatment unit
CN109095726B (en) A kind of leather waste water reuse system
CN201999821U (en) Printing and dyeing advanced treated wastewater recycling device
CN204897577U (en) Mix to congeal and handle and membrane separation combination effluent disposal system
CN205398351U (en) Chemical engineering sewage treatment device
CN203319801U (en) Papermaking advanced treatment wastewater reusing device based on chemical decalcification
CN201873589U (en) Advanced treatment and recycle device for papermaking wastewater

Legal Events

Date Code Title Description
C14 Grant of patent or utility model
GR01 Patent grant
CF01 Termination of patent right due to non-payment of annual fee

Granted publication date: 20110831

Termination date: 20160222

CF01 Termination of patent right due to non-payment of annual fee