[go: up one dir, main page]

CN111573969A - A combined biological treatment method for high-concentration COD-containing chromium-containing electroplating cleaning wastewater - Google Patents

A combined biological treatment method for high-concentration COD-containing chromium-containing electroplating cleaning wastewater Download PDF

Info

Publication number
CN111573969A
CN111573969A CN202010364734.3A CN202010364734A CN111573969A CN 111573969 A CN111573969 A CN 111573969A CN 202010364734 A CN202010364734 A CN 202010364734A CN 111573969 A CN111573969 A CN 111573969A
Authority
CN
China
Prior art keywords
wastewater
chromium
unit
concentration
biological treatment
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Pending
Application number
CN202010364734.3A
Other languages
Chinese (zh)
Inventor
马晨
王丽英
赵子军
刘忠斌
高阳
朱雪松
赵明涛
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.)
Ansteel Group Zhongyuan Industrial Development Co Ltd
Original Assignee
Angang Zhongyuan Anshan Environmental Protection 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 Angang Zhongyuan Anshan Environmental Protection Co ltd filed Critical Angang Zhongyuan Anshan Environmental Protection Co ltd
Priority to CN202010364734.3A priority Critical patent/CN111573969A/en
Publication of CN111573969A publication Critical patent/CN111573969A/en
Pending legal-status Critical Current

Links

Images

Classifications

    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F9/00Multistage treatment of water, waste water or sewage
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/001Processes for the treatment of water whereby the filtration technique is of importance
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/72Treatment of water, waste water, or sewage by oxidation
    • C02F1/725Treatment of water, waste water, or sewage by oxidation by catalytic oxidation
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/72Treatment of water, waste water, or sewage by oxidation
    • C02F1/74Treatment of water, waste water, or sewage by oxidation with air
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/72Treatment of water, waste water, or sewage by oxidation
    • C02F1/78Treatment of water, waste water, or sewage by oxidation with ozone
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/10Inorganic compounds
    • C02F2101/20Heavy metals or heavy metal compounds
    • C02F2101/22Chromium or chromium compounds, e.g. chromates
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/30Organic compounds
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2103/00Nature of the water, waste water, sewage or sludge to be treated
    • C02F2103/16Nature of the water, waste water, sewage or sludge to be treated from metallurgical processes, i.e. from the production, refining or treatment of metals, e.g. galvanic wastes
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F3/00Biological treatment of water, waste water, or sewage
    • C02F3/28Anaerobic digestion processes

Landscapes

  • Life Sciences & Earth Sciences (AREA)
  • Hydrology & Water Resources (AREA)
  • Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Treatment Of Water By Oxidation Or Reduction (AREA)

Abstract

本发明涉及一种高浓度COD含铬电镀清洗废水的组合生物处理方法,废水依次经调节池、初级过滤单元、氧化单元、生物降解单元及后过滤单元处理后达标排放、直接回用或经深度处理后回用。本发明将非均相催化氧化技术与生物技术有机组合,两类处理技术相辅相成,针对难处理的高浓度COD含铬电镀清洗有机废水,完成高浓度COD、低氨氮、总磷、六价铬等重金属及其它多种污染物的协同脱除。这类难降解废水经非均相催化氧化调节,为后续生物处理特定菌种创造优势环境,从而同时完成六价铬去毒性化与有机污染物脱除。处理工艺全程无需投加化学药剂,不增加废水中的离子浓度,最终实现达标排放或作为企业生产补充水回用,实现废水的净化或资源化利用。

Figure 202010364734

The invention relates to a combined biological treatment method for high-concentration COD-containing chromium-containing electroplating cleaning wastewater. The wastewater is sequentially treated by a conditioning tank, a primary filtering unit, an oxidation unit, a biodegradation unit and a post-filtering unit, and then discharged up to the standard, directly reused or processed through a deep reuse after processing. The invention organically combines heterogeneous catalytic oxidation technology and biological technology, and the two types of treatment technologies complement each other. For the refractory high-concentration COD-containing chromium-containing electroplating and cleaning organic wastewater, high-concentration COD, low ammonia nitrogen, total phosphorus, hexavalent chromium, etc. Synergistic removal of heavy metals and other pollutants. This kind of refractory wastewater is regulated by heterogeneous catalytic oxidation to create an advantageous environment for the subsequent biological treatment of specific bacterial species, so as to complete the detoxification of hexavalent chromium and the removal of organic pollutants at the same time. There is no need to add chemicals in the whole process of the treatment process, and it does not increase the ion concentration in the wastewater, and finally achieves standard discharge or reuse as supplementary water for enterprise production, and realizes wastewater purification or resource utilization.

Figure 202010364734

Description

一种高浓度COD含铬电镀清洗废水的组合生物处理方法A combined biological treatment method for high-concentration COD-containing chromium-containing electroplating cleaning wastewater

技术领域technical field

本发明涉及工业废水净化处理技术领域,尤其涉及一种高浓度COD含铬电镀清洗废水的组合生物处理方法。The invention relates to the technical field of industrial wastewater purification and treatment, in particular to a combined biological treatment method for high-concentration COD-containing chromium-containing electroplating cleaning wastewater.

背景技术Background technique

金属铬具有硬度高、摩擦系数小、化学稳定好等优点,被广泛应用为防护及装饰性镀层,在电镀行业中占有很高的比重。企业产生的电镀清洗废水主要为待镀件预处理过程中的清洗除油废水、漂洗废水、钝化废水等的混合水,这种废水的污染物特性是含有大量的油、COD浓度很高、氨氮浓度偏低、pH值多偏强碱性,且夹带有较多无机盐成分,包括重金属离子铬。铬的毒性与其存在的价态相关,六价铬的毒性显著高于三价铬,企业产生的电镀清洗废水因其污染物特性,所含的铬离子中相当一部分为六价铬,具有很高的毒性,且生化性差,属于一种难处理的工业有机废水。Metal chromium has the advantages of high hardness, low friction coefficient and good chemical stability. It is widely used as protective and decorative coatings, and occupies a high proportion in the electroplating industry. The electroplating cleaning wastewater produced by the enterprise is mainly the mixed water of cleaning and degreasing wastewater, rinsing wastewater, passivation wastewater, etc. in the pretreatment process of the parts to be plated. The ammonia nitrogen concentration is low, the pH value is mostly strong alkaline, and there are many inorganic salt components, including the heavy metal ion chromium. The toxicity of chromium is related to its valence. The toxicity of hexavalent chromium is significantly higher than that of trivalent chromium. Due to the characteristics of pollutants, a considerable part of the chromium ions contained in the electroplating cleaning wastewater produced by enterprises is hexavalent chromium, which has a high It is toxic and has poor biochemical properties, and belongs to a kind of industrial organic wastewater that is difficult to treat.

近年来,利用微生物富集、代谢重金属的废水生物技术处理方法的研究逐渐兴起,因其具有经济、高效、无二次污染等特点,被认为是极具发展潜力的污染治理方法。然而受生物体自身的条件限制,特定菌种通常对废水的污染物浓度、pH值、溶解氧、温度等指标有特定的要求。由于电镀清洗废水的毒性大,COD浓度高,且难降解成分高,传统生物处理工艺几乎无法适用,至少也需先考虑降低这类电镀废水的毒性,即首先需要将六价铬还原为三价铬,进而形成沉淀实现污染物分离。这类处理技术目前常见的有亚硫酸盐法、硫酸亚铁-石灰法、电解还原法等还原处理技术,以及电渗析、反渗透、离子交换、活性炭吸附、絮凝等物化处理技术,这些处理技术普遍存在能源及药剂消耗量大,投资及运行费用高,同时会产生大量含铬废弃物需另行处理的问题,并且电镀清洗废水的铬离子浓度不在上述处理技术的适用浓度区间内,技术经济指标也会很差。In recent years, the research on wastewater biotechnology treatment methods using microorganisms to enrich and metabolize heavy metals has gradually emerged. Because of its economical, efficient, and no secondary pollution, it is considered to be a pollution control method with great development potential. However, limited by the conditions of the organism itself, specific bacterial species usually have specific requirements on the pollutant concentration, pH value, dissolved oxygen, temperature and other indicators of wastewater. Due to the high toxicity of electroplating cleaning wastewater, high COD concentration, and high refractory components, traditional biological treatment processes are almost unsuitable. At least, it is necessary to consider reducing the toxicity of this type of electroplating wastewater, that is, it is necessary to reduce hexavalent chromium to trivalent first. Chromium, and then form a precipitate to achieve the separation of pollutants. Such treatment technologies are currently common reduction treatment technologies such as sulfite method, ferrous sulfate-lime method, and electrolytic reduction method, as well as physicochemical treatment technologies such as electrodialysis, reverse osmosis, ion exchange, activated carbon adsorption, and flocculation. There are generally problems such as large consumption of energy and chemicals, high investment and operating costs, and a large amount of chromium-containing waste that needs to be treated separately, and the concentration of chromium ions in electroplating cleaning wastewater is not within the applicable concentration range of the above-mentioned treatment technology. Technical and economic indicators will be bad too.

因此,针对电镀企业产生的高浓度COD含铬电镀清洗废水,依然需要寻找一种高效、低成本的方法进行有针对性的净化处理。Therefore, it is still necessary to find an efficient and low-cost method for targeted purification treatment of high-concentration COD-containing chromium-containing electroplating cleaning wastewater produced by electroplating enterprises.

发明内容SUMMARY OF THE INVENTION

本发明提供了一种高浓度COD含铬电镀清洗废水的组合生物处理方法,将非均相催化氧化技术与生物技术有机组合;针对难处理的高浓度COD含铬电镀清洗有机废水,完成高浓度COD、低氨氮、总磷、六价铬等重金属及其它多种污染物的协同脱除。将这类难降解废水经非均相催化氧化调节,为后续生物处理特定菌种创造优势环境,从而同时完成六价铬去毒性化与有机污染物脱除。处理工艺全程无需外部投加化学药剂,不增加废水中的离子浓度,最终实现达标排放或作为企业生产补充水回用,实现废水的净化或资源化利用。The invention provides a combined biological treatment method for high-concentration COD-chromium-containing electroplating cleaning wastewater, which organically combines heterogeneous catalytic oxidation technology and biological technology; Synergistic removal of COD, low ammonia nitrogen, total phosphorus, hexavalent chromium and other heavy metals and other pollutants. This kind of refractory wastewater is regulated by heterogeneous catalytic oxidation to create a favorable environment for the subsequent biological treatment of specific bacterial species, so as to complete the detoxification of hexavalent chromium and the removal of organic pollutants at the same time. The whole process of the treatment process does not require external addition of chemicals, does not increase the ion concentration in the wastewater, and finally achieves standard discharge or reuse as supplementary water for enterprise production to achieve wastewater purification or resource utilization.

为了达到上述目的,本发明采用以下技术方案实现:In order to achieve the above object, the present invention adopts the following technical solutions to realize:

一种高浓度COD含铬电镀清洗废水的组合生物处理方法,所述电镀清洗废水中的COD浓度≥2000mg/L,六价铬浓度≤10mg/L;处理方法包括如下步骤:A combined biological treatment method for high-concentration COD-containing chromium-containing electroplating cleaning wastewater, wherein the COD concentration in the electroplating cleaning wastewater is greater than or equal to 2000 mg/L, and the hexavalent chromium concentration is less than or equal to 10 mg/L; the treatment method comprises the following steps:

(1)废水首先送入调节池,进行均质均量;(1) The waste water is first sent to the regulating tank for homogenization;

(2)调节池出水送入初级过滤单元,去除废水中的大颗粒不溶杂质;(2) The effluent of the conditioning tank is sent to the primary filtration unit to remove large particles of insoluble impurities in the wastewater;

(3)初级过滤单元出水送入氧化单元;所述氧化单元采用非均相催化氧化,在常温常压及催化剂的作用下,对废水中的复杂有机污染物进行断链,同时改善废水的可生化性,同时调节废水性质,使其满足后续工艺要求;(3) The effluent of the primary filtration unit is sent to the oxidation unit; the oxidation unit adopts heterogeneous catalytic oxidation, and under the action of normal temperature and pressure and a catalyst, the complex organic pollutants in the wastewater are chain-severed, and the efficiency of the wastewater is improved at the same time. Biochemical properties, while adjusting the properties of wastewater to meet the requirements of subsequent processes;

(4)氧化单元出水送入生物降解单元;将废水中经氧化单元初步降解得到的大碳链有机物进一步降解为小碳链、单碳链有机物,最终转化为水、二氧化碳及其它小分子无机物;生物降解单元中氧化与还原的生化反应交替反复发生,废水所含六价铬被还原为三价铬的沉淀物,并沉积在生物降解单元的底部,定期外排;(4) The effluent of the oxidation unit is sent to the biodegradation unit; the large carbon chain organic matter obtained by the preliminary degradation of the oxidation unit in the wastewater is further degraded into small carbon chain and single carbon chain organic matter, and finally converted into water, carbon dioxide and other small molecular inorganic substances ; The biochemical reactions of oxidation and reduction in the biodegradation unit occur alternately and repeatedly, and the hexavalent chromium contained in the wastewater is reduced to the precipitate of trivalent chromium, which is deposited at the bottom of the biodegradation unit and discharged regularly;

(5)生物降解单元出水送入后过滤单元,去除废水中的多余杂质,然后达标排放、直接回用或经深度处理后回用。(5) The effluent of the biodegradation unit is sent to the post-filtration unit to remove excess impurities in the wastewater, and then discharged up to the standard, directly reused or reused after advanced treatment.

所述初级过滤单元中过滤介质为多孔过滤介质、颗粒状过滤介质、合金筛网中的一种或多种组合;其中多孔过滤介质为陶瓷或尼龙,过滤孔径为30~50μm;颗粒状过滤介质为锰砂或石英砂中的一种或两种。The filter medium in the primary filter unit is one or more combinations of porous filter medium, granular filter medium, and alloy screen; the porous filter medium is ceramic or nylon, and the filter pore size is 30-50 μm; the granular filter medium It is one or both of manganese sand or quartz sand.

所述氧化单元中的非均相催化氧化过程,催化剂采用铂、铅、镍、铜的氧化物中的一种或多种,并经高温烧结为网状或颗粒状结构;氧化剂选用空气或臭氧。In the heterogeneous catalytic oxidation process in the oxidation unit, the catalyst adopts one or more of oxides of platinum, lead, nickel and copper, and is sintered at high temperature into a network or granular structure; the oxidant is selected from air or ozone .

所述生物降解单元为全流程的厌氧生物降解过程,包含水解酸化段和厌氧消化段2个工艺段;所述水解酸化段中,废水所含的大碳链有机物转化为小碳链的碳氢化合物,产物中有多种有机酸;在酸性环境中下废水中的六价铬作为电子受体,生物菌种以小碳链分子为电子供体,实现六价铬还原为三价铬;所述厌氧生物段中,依靠厌氧生物菌种的新陈代谢,在弱碱环境中,水解酸化段反应生成的低价态铬离子与废水中OH-结合,形成低价态铬沉淀物,从废水中逐渐分离;同时,小碳链有机污染物依靠生物菌种新陈代谢,最终转化为水、二氧化碳及其他无机物;同时,氨氮、总磷也得以去除。The biodegradation unit is a full-process anaerobic biodegradation process, including two process sections, a hydrolysis acidification section and an anaerobic digestion section; in the hydrolysis acidification section, the large carbon chain organic matter contained in the wastewater is converted into small carbon chain organic matter. Hydrocarbons, there are a variety of organic acids in the product; in an acidic environment, hexavalent chromium in wastewater is used as an electron acceptor, and biological bacteria use small carbon chain molecules as electron donors to achieve the reduction of hexavalent chromium to trivalent chromium In the anaerobic biological section, relying on the metabolism of anaerobic biological bacteria, in a weak alkaline environment, the low-valent chromium ions generated by the hydrolysis and acidification section are combined with OH- in the wastewater to form low-valent chromium precipitates, Gradually separated from wastewater; at the same time, small carbon chain organic pollutants rely on the metabolism of biological bacteria, and finally converted into water, carbon dioxide and other inorganic substances; at the same time, ammonia nitrogen and total phosphorus are also removed.

所述低价态铬沉淀物单独收集后作为金属铬冶炼原料。The low-valent chromium precipitate is collected separately and used as a raw material for metal chromium smelting.

所述后过滤单元中的过滤介质为石英砂、无烟煤、活性炭、磁铁矿、锰砂、陶粒、多孔陶瓷中的一种或多种,过滤介质的粒径为0.5~5mm。The filter medium in the post-filter unit is one or more of quartz sand, anthracite, activated carbon, magnetite, manganese sand, ceramsite, and porous ceramics, and the particle size of the filter medium is 0.5-5 mm.

与现有技术相比,本发明的有益效果是:Compared with the prior art, the beneficial effects of the present invention are:

1)本发明采用“组合生物技术处理方法”,有针对性地处理具有特定污染物特性的高浓度COD含铬电镀清洗废水,既能克服常规生化处理厌氧菌种对六价铬毒性耐受能力差的问题,同时也能解决现有厌氧处理含铬废水对低浓度六价铬处理效率低,且功能单一、无法同时脱除有机污染物的缺陷。对工艺流程进行优化组合,通过化学氧化段对难降解有机物进行断链,改善废水的可生化性,同时调节废水性质,为后续生物处理特定菌种的生长创造优势环境条件,从而经过生物降解单元的水解酸化和厌氧工艺段的协同作用,得以同时完成六价铬的去毒性化与有机污染物脱除。两种工艺的有机结合,使原本毒性大、难降解污染物浓度高、可生化性差的废水得以被高效、稳定地净化。1) The present invention adopts a "combined biotechnology treatment method" to treat high-concentration COD chromium-containing electroplating cleaning wastewater with specific pollutant characteristics in a targeted manner, which can overcome the toxicity tolerance of anaerobic bacteria in conventional biochemical treatment to hexavalent chromium. At the same time, it can also solve the problem that the existing anaerobic treatment of chromium-containing wastewater has low treatment efficiency for low-concentration hexavalent chromium, and has a single function and cannot remove organic pollutants at the same time. The optimized combination of the process flow, the chain scission of the refractory organic matter through the chemical oxidation section, to improve the biodegradability of the wastewater, and to adjust the properties of the wastewater at the same time, to create favorable environmental conditions for the growth of specific bacterial species in the subsequent biological treatment, so as to pass through the biodegradation unit. The synergistic effect of hydrolysis acidification and anaerobic process section can complete the detoxification of hexavalent chromium and the removal of organic pollutants at the same time. The organic combination of the two processes enables the wastewater with high toxicity, high concentration of refractory pollutants and poor biodegradability to be efficiently and stably purified.

2)废水处理工艺的全过程中,无需外部投加酸、碱或其它化学药剂,不增加废水处理过程中的离子浓度,因此废水处理前后的电导率不会上升,处理后的出水可满足电镀生产环节清洗回用水标准。2) In the whole process of the wastewater treatment process, there is no need to add acid, alkali or other chemicals externally, and the ion concentration in the wastewater treatment process is not increased, so the conductivity before and after wastewater treatment will not increase, and the treated effluent can meet the requirements of electroplating. Standard for cleaning and reuse water in production.

3)在非均相催化氧化工艺环节没有固体废弃物外排,生物降解单元的生物菌种生化反应过程仅产生少量生物菌种新陈代谢的生物污泥,以及低价态金属铬沉淀物;低价态金属铬沉淀物与生物污泥一同作为废水处理过程中的废弃物外排。这种废弃物因含有生物污泥及金属铬,可作为资源化回收利用的原料,并实现污染物零排放。3) There is no solid waste discharge in the process of heterogeneous catalytic oxidation, and the biochemical reaction process of biological bacteria in the biodegradation unit produces only a small amount of biological sludge metabolized by biological bacteria, and low-valent metal chromium precipitates; low-cost Metal chromium precipitates are discharged together with biological sludge as waste in the wastewater treatment process. Because this waste contains biological sludge and metallic chromium, it can be used as a raw material for resource recycling and achieve zero emission of pollutants.

4)由于高浓度COD含铬电镀清洗废水的生物处理过程中,每一段生物菌种生化反应均在缺氧条件下完成,故废水中所含的六价铬还原为三价铬后,不会再次被氧化为六价铬,从而彻底消除废水中的六价铬,保证处理效果稳定可靠。4) In the biological treatment process of high-concentration COD-containing chromium-containing electroplating cleaning wastewater, the biochemical reaction of each stage of biological bacteria is completed under anoxic conditions, so after the hexavalent chromium contained in the wastewater is reduced to trivalent chromium, it will not. It is oxidized to hexavalent chromium again, so as to completely eliminate the hexavalent chromium in the wastewater and ensure the stable and reliable treatment effect.

5)本发明与常规的化学法消除废水中六价铬离子技术相比,具有无毒、无害、无废弃物的优点;与常规的生物活性污泥技术相比,具有生物污泥产生量少、排放量少的优点。5) Compared with the conventional chemical method to eliminate hexavalent chromium ions in wastewater, the present invention has the advantages of non-toxic, harmless and waste-free; The advantages of less and less emissions.

6)本发明所述方法具有工艺稳定性好、耐冲击能力强、流程简洁、操作简单、效率高、成本低、且无二次污染的优势,适于推广应用。6) The method of the present invention has the advantages of good process stability, strong impact resistance, concise process, simple operation, high efficiency, low cost, and no secondary pollution, and is suitable for popularization and application.

附图说明Description of drawings

图1是本发明所述一种高浓度COD含铬电镀清洗废水的组合生物处理方法的工艺流程图。1 is a process flow diagram of a combined biological treatment method for high-concentration COD-containing chromium-containing electroplating cleaning wastewater according to the present invention.

具体实施方式Detailed ways

下面结合附图对本发明的具体实施方式作进一步说明:The specific embodiments of the present invention will be further described below in conjunction with the accompanying drawings:

如图1所示,本发明所述一种高浓度COD含铬电镀清洗废水的组合生物处理方法,所述电镀清洗废水中的COD浓度≥2000mg/L,六价铬浓度≤10mg/L;处理方法包括如下步骤:As shown in Figure 1, a combined biological treatment method of high-concentration COD-containing chromium-containing electroplating cleaning wastewater according to the present invention, the COD concentration in the electroplating cleaning wastewater is ≥ 2000mg/L, and the hexavalent chromium concentration is ≤ 10mg/L; The method includes the following steps:

(1)废水首先送入调节池,进行均质均量;(1) The waste water is first sent to the regulating tank for homogenization;

(2)调节池出水送入初级过滤单元,去除废水中的大颗粒不溶杂质;(2) The effluent of the conditioning tank is sent to the primary filtration unit to remove large particles of insoluble impurities in the wastewater;

(3)初级过滤单元出水送入氧化单元;所述氧化单元采用非均相催化氧化,在常温常压及催化剂的作用下,对废水中的复杂有机污染物进行断链,同时改善废水的可生化性,同时调节废水性质,使其满足后续工艺要求;(3) The effluent of the primary filtration unit is sent to the oxidation unit; the oxidation unit adopts heterogeneous catalytic oxidation, and under the action of normal temperature and pressure and a catalyst, the complex organic pollutants in the wastewater are chain-severed, and the efficiency of the wastewater is improved at the same time. Biochemical properties, while adjusting the properties of wastewater to meet the requirements of subsequent processes;

(4)氧化单元出水送入生物降解单元;将废水中经氧化单元初步降解得到的大碳链有机物进一步降解为小碳链、单碳链有机物,最终转化为水、二氧化碳及其它小分子无机物;生物降解单元中氧化与还原的生化反应交替反复发生,废水所含六价铬被还原为三价铬的沉淀物,并沉积在生物降解单元的底部,定期外排;(4) The effluent of the oxidation unit is sent to the biodegradation unit; the large carbon chain organic matter obtained by the preliminary degradation of the oxidation unit in the wastewater is further degraded into small carbon chain and single carbon chain organic matter, and finally converted into water, carbon dioxide and other small molecular inorganic substances ; The biochemical reactions of oxidation and reduction in the biodegradation unit occur alternately and repeatedly, and the hexavalent chromium contained in the wastewater is reduced to the precipitate of trivalent chromium, which is deposited at the bottom of the biodegradation unit and discharged regularly;

(5)生物降解单元出水送入后过滤单元,去除废水中的多余杂质,然后达标排放、直接回用或经深度处理后回用。(5) The effluent of the biodegradation unit is sent to the post-filtration unit to remove excess impurities in the wastewater, and then discharged up to the standard, directly reused or reused after advanced treatment.

所述初级过滤单元中过滤介质为多孔过滤介质、颗粒状过滤介质、合金筛网中的一种或多种组合;其中多孔过滤介质为陶瓷或尼龙,过滤孔径为30~50μm;颗粒状过滤介质为锰砂或石英砂中的一种或两种。The filter medium in the primary filter unit is one or more combinations of porous filter medium, granular filter medium, and alloy screen; the porous filter medium is ceramic or nylon, and the filter pore size is 30-50 μm; the granular filter medium It is one or both of manganese sand or quartz sand.

所述氧化单元中的非均相催化氧化过程,催化剂采用铂、铅、镍、铜的氧化物中的一种或多种,并经高温烧结为网状或颗粒状结构;氧化剂选用空气或臭氧。In the heterogeneous catalytic oxidation process in the oxidation unit, the catalyst adopts one or more of oxides of platinum, lead, nickel and copper, and is sintered at high temperature into a network or granular structure; the oxidant is selected from air or ozone .

所述生物降解单元为全流程的厌氧生物降解过程,包含水解酸化段和厌氧消化段2个工艺段;所述水解酸化段中,废水所含的大碳链有机物转化为小碳链的碳氢化合物,产物中有多种有机酸;在酸性环境中下废水中的六价铬作为电子受体,生物菌种以小碳链分子为电子供体,实现六价铬还原为三价铬;所述厌氧生物段中,依靠厌氧生物菌种的新陈代谢,在弱碱环境中,水解酸化段反应生成的低价态铬离子与废水中OH-结合,形成低价态铬沉淀物,从废水中逐渐分离;同时,小碳链有机污染物依靠生物菌种新陈代谢,最终转化为水、二氧化碳及其他无机物;同时,氨氮、总磷也得以去除。The biodegradation unit is a full-process anaerobic biodegradation process, including two process sections, a hydrolysis acidification section and an anaerobic digestion section; in the hydrolysis acidification section, the large carbon chain organic matter contained in the wastewater is converted into small carbon chain organic matter. Hydrocarbons, there are various organic acids in the product; in an acidic environment, hexavalent chromium in wastewater is used as electron acceptor, and biological bacteria use small carbon chain molecules as electron donors to achieve the reduction of hexavalent chromium to trivalent chromium In the anaerobic biological section, relying on the metabolism of anaerobic biological bacteria, in a weak alkaline environment, the low-valent chromium ions generated by the hydrolysis and acidification section are combined with OH- in the wastewater to form low-valent chromium precipitates, It is gradually separated from the wastewater; at the same time, the small carbon chain organic pollutants rely on the metabolism of biological bacteria, and are finally converted into water, carbon dioxide and other inorganic substances; at the same time, ammonia nitrogen and total phosphorus are also removed.

所述低价态铬沉淀物单独收集后作为金属铬冶炼原料。The low-valent chromium precipitate is collected separately and used as a raw material for metal chromium smelting.

所述后过滤单元中的过滤介质为石英砂、无烟煤、活性炭、磁铁矿、锰砂、陶粒、多孔陶瓷中的一种或多种,过滤介质的粒径为0.5~5mm。The filter medium in the post-filter unit is one or more of quartz sand, anthracite, activated carbon, magnetite, manganese sand, ceramsite, and porous ceramics, and the particle size of the filter medium is 0.5-5 mm.

以下实施例在以本发明技术方案为前提下进行实施,给出了详细的实施方式和具体的操作过程,但本发明的保护范围不限于下述的实施例。下述实施例中所用方法如无特别说明均为常规方法。The following examples are implemented on the premise of the technical solutions of the present invention, and provide detailed embodiments and specific operation processes, but the protection scope of the present invention is not limited to the following examples. The methods used in the following examples are conventional methods unless otherwise specified.

【实施例】【Example】

本实施例中,一种高浓度COD含铬电镀清洗废水是来自某企业进行待电镀轧辊表面清洗除油产生的清洗废水,废水中含油3500mg/L,COD 3000mg/L,氨氮16.1mg/L,总磷53.9mg/L,六价铬0.96mg/L,总铬1.77mg/L,pH值为9.73,同时废水中含有大量铁离子。In this embodiment, a high-concentration COD-containing chromium-containing electroplating cleaning wastewater is the cleaning wastewater generated by cleaning and degreasing the surface of the roll to be plated in a certain enterprise. The total phosphorus was 53.9mg/L, the hexavalent chromium was 0.96mg/L, the total chromium was 1.77mg/L, and the pH value was 9.73. At the same time, the wastewater contained a large amount of iron ions.

废水首先送入调节池进行均质均量,之后送入初级过滤单元,以去除废水中的大颗粒不溶杂质。初级过滤单元中的过滤介质为硅酸铝陶瓷,过滤孔径为30μm。过滤操作中滤速不变,废水快速通过滤层。The wastewater is first sent to the conditioning tank for homogenization, and then sent to the primary filtration unit to remove large particles of insoluble impurities in the wastewater. The filter medium in the primary filter unit is aluminosilicate ceramics, and the filter pore size is 30 μm. During the filtration operation, the filtration rate remains unchanged, and the waste water quickly passes through the filter layer.

初级过滤单元出水送入氧化单元,氧化单元内部设置由尼龙66、PE、鹅卵石、陶土粒等多种非金属材料构成的固态填料,催化剂是铂、铅、镍、铜的合金氧化物,以空气中的氧作为氧化剂。在常温常压环境条件下,废水与氧充分接触反应,油分子的大碳链断链,形成大小不一的有机碳链。The effluent from the primary filter unit is sent to the oxidation unit. The solid fillers made of nylon 66, PE, pebbles, clay particles and other non-metallic materials are arranged inside the oxidation unit. The catalyst is an alloy oxide of platinum, lead, nickel and copper. Oxygen in the oxidant. Under the environmental conditions of normal temperature and pressure, the wastewater is fully contacted and reacted with oxygen, and the large carbon chain of the oil molecule is broken, forming organic carbon chains of different sizes.

经过断链后的废水进入后续的生物降解单元,废水中有机物的碳链进一步降解,直至最终形成H2O和CO2。废水依次通过水解酸化段与厌氧硝化段后,出水送入后过滤单元。The wastewater after chain scission enters the subsequent biodegradation unit, and the carbon chain of the organic matter in the wastewater is further degraded until H 2 O and CO 2 are finally formed. After the wastewater passes through the hydrolysis and acidification section and the anaerobic nitrification section in sequence, the effluent is sent to the post-filtration unit.

后过滤单元用于去除废水中多余的杂质,过滤介质选择粒径为0.5~4mm的锰砂、粒径为0.5~1.2mm的石英砂及粒径为0.8~1.8mm的活性炭,锰砂、石英砂及活性碳依次由下至上铺设。The post-filtration unit is used to remove excess impurities in the wastewater. The filter media select manganese sand with a particle size of 0.5-4mm, quartz sand with a particle size of 0.5-1.2mm, activated carbon with a particle size of 0.8-1.8mm, manganese sand, quartz sand Sand and activated carbon are laid sequentially from bottom to top.

本实施例中,处理后出水COD≤30mg/L,氨氮≤2mg/L,总磷≤1mg/L,六价铬≤0.02mg/L,总铬≤0.03mg/L,pH值为7.80,满足回用水水质标准,可作为清洗槽的补充水回用。In this embodiment, the treated effluent COD≤30mg/L, ammonia nitrogen≤2mg/L, total phosphorus≤1mg/L, hexavalent chromium≤0.02mg/L, total chromium≤0.03mg/L, pH value of 7.80, satisfying The water quality standard for reused water can be reused as supplementary water for cleaning tanks.

以上所述,仅为本发明较佳的具体实施方式,但本发明的保护范围并不局限于此,任何熟悉本技术领域的技术人员在本发明揭露的技术范围内,根据本发明的技术方案及其发明构思加以等同替换或改变,都应涵盖在本发明的保护范围之内。The above description is only a preferred embodiment of the present invention, but the protection scope of the present invention is not limited to this. The equivalent replacement or change of the inventive concept thereof shall be included within the protection scope of the present invention.

Claims (6)

1. A combined biological treatment method of high-concentration COD chromium-containing electroplating cleaning wastewater is characterized in that the COD concentration in the electroplating cleaning wastewater is more than or equal to 2000mg/L, and the concentration of hexavalent chromium is less than or equal to 10 mg/L; the processing method comprises the following steps:
(1) firstly, feeding the wastewater into a regulating tank, and homogenizing;
(2) the effluent of the regulating reservoir is sent into a primary filtering unit to remove large-particle insoluble impurities in the wastewater;
(3) the effluent of the primary filtering unit is sent into an oxidizing unit; the oxidation unit adopts heterogeneous catalytic oxidation, carries out chain scission on complex organic pollutants in the wastewater under the action of a catalyst at normal temperature and normal pressure, improves the biodegradability of the wastewater, and simultaneously adjusts the property of the wastewater to ensure that the wastewater meets the requirements of the subsequent process;
(4) the effluent of the oxidation unit is sent to a biodegradation unit; the large carbon chain organic matter obtained by the preliminary degradation of the wastewater through the oxidation unit is further degraded into small carbon chain and single carbon chain organic matter, and finally converted into water, carbon dioxide and other small molecular inorganic matters; the biochemical reactions of oxidation and reduction in the biodegradation unit are alternately and repeatedly carried out, hexavalent chromium contained in the wastewater is reduced into precipitate of trivalent chromium, the precipitate is deposited at the bottom of the biodegradation unit, and the precipitate is periodically discharged;
(5) and (3) sending the effluent of the biodegradation unit into a post-filtering unit, removing redundant impurities in the wastewater, and then discharging the wastewater after reaching the standard and directly recycling the wastewater or recycling the wastewater after advanced treatment.
2. The combined biological treatment method for the high-concentration COD chromium-containing electroplating cleaning wastewater according to claim 1, characterized in that the filter medium in the primary filter unit is one or more of porous filter medium, granular filter medium and alloy screen; wherein the porous filter medium is ceramic or nylon, and the filter aperture is 30-50 μm; the granular filter medium is one or two of manganese sand or quartz sand.
3. The combined biological treatment method for the high-concentration COD chromium-containing electroplating cleaning wastewater according to claim 1, characterized in that in the heterogeneous catalytic oxidation process in the oxidation unit, the catalyst adopts one or more oxides of platinum, lead, nickel and copper, and is sintered into a net-shaped or granular structure at high temperature; the oxidant is air or ozone.
4. The combined biological treatment method for the high-concentration COD chromium-containing electroplating cleaning wastewater according to claim 1, characterized in that the biodegradation unit is a full-flow anaerobic biodegradation process comprising 2 process sections of a hydrolytic acidification section and an anaerobic digestion section;
in the hydrolysis acidification section, large carbon chain organic matters contained in the wastewater are converted into small carbon chain hydrocarbon compounds, and a plurality of organic acids are contained in the products; in an acidic environment, hexavalent chromium in the wastewater is used as an electron acceptor, and the biological strain takes small carbon chain molecules as an electron donor to reduce the hexavalent chromium into trivalent chromium;
in the anaerobic biological section, low-valence chromium ions generated by the reaction of the hydrolytic acidification section are combined with OH < - > in the wastewater in a weak alkali environment by means of metabolism of anaerobic biological strains to form low-valence chromium precipitates which are gradually separated from the wastewater; meanwhile, the small carbon chain organic pollutants are metabolized by the biological strains and finally converted into water, carbon dioxide and other inorganic substances; ammonia nitrogen and total phosphorus are also removed.
5. The combined biological treatment method of high concentration COD chromium containing electroplating cleaning waste water according to claim 4, characterized in that the low valence state chromium precipitate is collected separately and used as metallic chromium smelting raw material.
6. The combined biological treatment method of high concentration COD chromium containing electroplating cleaning wastewater according to claim 1, characterized in that the filtering medium in the post-filtering unit is one or more of quartz sand, anthracite, activated carbon, magnetite, manganese sand, ceramsite and porous ceramic, and the particle size of the filtering medium is 0.5-5 mm.
CN202010364734.3A 2020-04-30 2020-04-30 A combined biological treatment method for high-concentration COD-containing chromium-containing electroplating cleaning wastewater Pending CN111573969A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN202010364734.3A CN111573969A (en) 2020-04-30 2020-04-30 A combined biological treatment method for high-concentration COD-containing chromium-containing electroplating cleaning wastewater

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN202010364734.3A CN111573969A (en) 2020-04-30 2020-04-30 A combined biological treatment method for high-concentration COD-containing chromium-containing electroplating cleaning wastewater

Publications (1)

Publication Number Publication Date
CN111573969A true CN111573969A (en) 2020-08-25

Family

ID=72113318

Family Applications (1)

Application Number Title Priority Date Filing Date
CN202010364734.3A Pending CN111573969A (en) 2020-04-30 2020-04-30 A combined biological treatment method for high-concentration COD-containing chromium-containing electroplating cleaning wastewater

Country Status (1)

Country Link
CN (1) CN111573969A (en)

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN111606519A (en) * 2020-06-09 2020-09-01 闫娟 Advanced treatment method for electroplating wastewater
CN113135642A (en) * 2021-05-25 2021-07-20 西安泰瑞环保技术有限公司 Copper foil passivation solution wastewater treatment process
CN115432890A (en) * 2022-09-21 2022-12-06 无锡市道格环保科技有限公司 Treatment device and method for reducing pollutant discharge in chromium-containing metal ion wastewater

Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1096769A (en) * 1993-06-11 1994-12-28 中国科学院成都生物研究所 New technology for treating electroplating waste water with micro-organism
CN1559937A (en) * 2004-02-13 2005-01-05 成都科泰技术有限公司 Method for treating high-concentration hazardous waste chromium waste liquid by using efficient functional bacteria
PT103332A (en) * 2005-08-12 2007-02-28 Univ Do Minho BIOSAFETY SYSTEM PRODUCED FROM BIOFILMS SUPPORTED IN FAUJASITE ZEÓLITO (FAU), PROCESS FOR OBTAINING AND USING IT IN THE REMOVAL OF HEXAVALENT CHROMIUM (CR (VI))
CN104671391A (en) * 2015-01-27 2015-06-03 北京中科圣泰环境科技有限公司 Ozone heterogeneous catalysis oxidization treatment device and technology for hardly degradable organic wastewater
CN109052848A (en) * 2018-09-01 2018-12-21 王斯靖 A kind of oxidation and biochemical coupling integrated method for treating water

Patent Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1096769A (en) * 1993-06-11 1994-12-28 中国科学院成都生物研究所 New technology for treating electroplating waste water with micro-organism
CN1559937A (en) * 2004-02-13 2005-01-05 成都科泰技术有限公司 Method for treating high-concentration hazardous waste chromium waste liquid by using efficient functional bacteria
PT103332A (en) * 2005-08-12 2007-02-28 Univ Do Minho BIOSAFETY SYSTEM PRODUCED FROM BIOFILMS SUPPORTED IN FAUJASITE ZEÓLITO (FAU), PROCESS FOR OBTAINING AND USING IT IN THE REMOVAL OF HEXAVALENT CHROMIUM (CR (VI))
CN104671391A (en) * 2015-01-27 2015-06-03 北京中科圣泰环境科技有限公司 Ozone heterogeneous catalysis oxidization treatment device and technology for hardly degradable organic wastewater
CN109052848A (en) * 2018-09-01 2018-12-21 王斯靖 A kind of oxidation and biochemical coupling integrated method for treating water

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN111606519A (en) * 2020-06-09 2020-09-01 闫娟 Advanced treatment method for electroplating wastewater
CN113135642A (en) * 2021-05-25 2021-07-20 西安泰瑞环保技术有限公司 Copper foil passivation solution wastewater treatment process
CN115432890A (en) * 2022-09-21 2022-12-06 无锡市道格环保科技有限公司 Treatment device and method for reducing pollutant discharge in chromium-containing metal ion wastewater
CN115432890B (en) * 2022-09-21 2024-01-23 无锡市道格环保科技有限公司 Treatment device and method for reducing pollutant emission in chromium-containing metal ion wastewater

Similar Documents

Publication Publication Date Title
CN103288309B (en) Coal gasification wastewater zero-emission treatment method, and application thereof
CN106554126B (en) Deep standard-reaching treatment method and system for reverse osmosis concentrated water
CN111573991B (en) Chemical plating comprehensive wastewater treatment method
CN101434445A (en) Processing system and operation method for phosphor-containing organic wastewater
CN105693019A (en) System and method for treating wastewater containing nitrobenzene, aniline and cyclohexylamine
CN206736028U (en) An advanced treatment system for electroplating wastewater
CN111573969A (en) A combined biological treatment method for high-concentration COD-containing chromium-containing electroplating cleaning wastewater
CN110894125A (en) Sewage treatment process for recycling N-methyl pyrrolidone
CN111499120A (en) Treatment system and method for denitration catalyst regeneration wastewater
CN116495934A (en) Sewage low-carbon treatment method
CN112174440B (en) Heavy metal wastewater treatment process
CN112939352A (en) Treatment method of comprehensive sewage of industrial park
CN210176671U (en) High-salt high-concentration degradation-resistant organic wastewater treatment equipment
CN111847764A (en) Method for treating printing and dyeing wastewater based on catalytic oxidation of ozone
CN111170587A (en) Spraying wastewater treatment process
CN222476371U (en) MVR concentrate processing apparatus
CN103663844B (en) Treatment method of ethylene waste alkali
CN1935680A (en) Method for treating sewage by catalytic iron internal electrogravimetry and its filler
CN112142259B (en) Comprehensive treatment method of PTA-containing wastewater
CN109502900A (en) A kind of Pb-Zn deposits beneficiation wastewater treatment for reuse Processes and apparatus
CN1327039C (en) Technology for treating electroplating effluent by biochemical process
CN213012449U (en) Denitration catalyst regeneration wastewater&#39;s processing apparatus
CN114506967A (en) Method for biologically and intensively treating high-salinity high-nitrate-nitrogen wastewater
CN114212946A (en) A kind of RO concentrated water treatment system and treatment method
CN101973661A (en) Treatment method of processing wastewater of Chinese galls

Legal Events

Date Code Title Description
PB01 Publication
PB01 Publication
SE01 Entry into force of request for substantive examination
SE01 Entry into force of request for substantive examination
TA01 Transfer of patent application right

Effective date of registration: 20210204

Address after: 114000 46 Heping Road, Tiedong District, Anshan City, Liaoning Province

Applicant after: Angang Zhongyuan Industrial Development Co.,Ltd.

Address before: 114000 46 Heping Road, Tiedong District, Anshan City, Liaoning Province

Applicant before: Angang Zhongyuan (Anshan) environmental protection Co.,Ltd.

TA01 Transfer of patent application right
RJ01 Rejection of invention patent application after publication

Application publication date: 20200825

RJ01 Rejection of invention patent application after publication