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CN1327039C - Technology for treating electroplating effluent by biochemical process - Google Patents

Technology for treating electroplating effluent by biochemical process Download PDF

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CN1327039C
CN1327039C CNB2004100217715A CN200410021771A CN1327039C CN 1327039 C CN1327039 C CN 1327039C CN B2004100217715 A CNB2004100217715 A CN B2004100217715A CN 200410021771 A CN200410021771 A CN 200410021771A CN 1327039 C CN1327039 C CN 1327039C
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electroplating wastewater
electroplating
wastewater
static mixer
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CN1557999A (en
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赵开方
覃涛
杨明云
吴基生
孙玉琴
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Qin Tao
Wu Ji
Yang Mingyun
Zhao Kaifang
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Abstract

本生化法治理电镀废水工艺是利用由脱硫弧菌、脱硫球菌、脱硫带环菌组成的BM功能菌处理电镀综合废水,将电镀废水引入调节池,调节其水量、均化水质;将调节池内的电镀废水经过第一级静态混合器,向第一级静态合混合器内加入BM功能菌,加入量为第一级静态混合器内电镀废水流量的1/50-200,进入BM反应器或池,进行一级生物反应,停留1-2.5小时,将进行一级生物反应后的电镀废水经过第二静态混合器,加入含量为30%氢氧化钠溶液,调整PH值到7.0-8.5,或同时加入BM功能菌,其加入量为电镀废水流量的1-3‰,进行二级反应沉淀过滤,停留2.5-4小时;将经过二级生化反应沉淀过滤后的电镀废水即达到国家污水综合排放标准GB8978-1996中的一级标准。

Figure 200410021771

The process of treating electroplating wastewater by this biochemical method is to use BM functional bacteria composed of Desulfovibrio, Desulfurococcus and Desulfuria annulus to treat electroplating comprehensive wastewater, introduce electroplating wastewater into the regulating pool, adjust its water volume, and homogenize the water quality; The electroplating wastewater passes through the first-stage static mixer, and BM functional bacteria are added to the first-stage static mixer. , carry out the primary biological reaction, stay for 1-2.5 hours, pass the electroplating wastewater after the primary biological reaction through the second static mixer, add 30% sodium hydroxide solution, adjust the pH value to 7.0-8.5, or at the same time Add BM functional bacteria, the amount of which is 1-3‰ of the electroplating wastewater flow rate, carry out secondary reaction precipitation filtration, and stay for 2.5-4 hours; the electroplating wastewater after secondary biochemical reaction precipitation filtration will meet the national sewage comprehensive discharge standard The primary standard in GB8978-1996.

Figure 200410021771

Description

生化法治理电镀废水工艺Treatment of electroplating wastewater by biochemical method

技术领域technical field

本发明涉及一种利用BM功能菌团对电镀污水进行处理的工艺。The invention relates to a process for treating electroplating sewage by using BM functional bacteria group.

背景技术Background technique

环境治理工程是一件利国利民的大事。重金属废水未经处理直接排入水体,会造成水体污染,影响水体生态平衡。Environmental governance engineering is a major event that benefits the country and the people. Heavy metal wastewater is directly discharged into water bodies without treatment, which will cause water pollution and affect the ecological balance of water bodies.

目前,国内采用最多的处理电镀污水的方法是化学处理法,通过沉淀、絮凝作用去除各种重金属,使废水达标。排放含铬废水须单独分开处理,还需投入大量化学药剂,不仅运行成本高,而且产生大量污泥,易造成二次污染;At present, the most widely used method to treat electroplating wastewater in China is chemical treatment, which removes various heavy metals through precipitation and flocculation to make wastewater meet the standard. The discharge of chromium-containing wastewater must be treated separately, and a large amount of chemical agents need to be invested, which not only has high operating costs, but also produces a large amount of sludge, which is likely to cause secondary pollution;

电解法处理电镀污水,是利用氧化还原的原理,将Cr6+还原成Cr3+,去除废水中的Cr3+。但不能处理混合废水,对单一重金属的浓度和水量均有一定限制;Electrolytic treatment of electroplating sewage is to use the principle of redox to reduce Cr 6+ to Cr 3+ and remove Cr 3+ in wastewater. However, mixed wastewater cannot be treated, and there are certain restrictions on the concentration and water volume of a single heavy metal;

离子交换法处理电镀污水,操作复杂,树脂饱和快,再生需消耗大量酸、碱,运行费太高;The ion exchange method is used to treat electroplating sewage, the operation is complicated, the resin is saturated quickly, the regeneration needs to consume a lot of acid and alkali, and the operating cost is too high;

铁屑法处理电镀污水,其稳定运行时间短。随着时间的推移,出水水质差、净化率低;The iron filing method treats electroplating sewage, and its stable operation time is short. As time goes by, the effluent water quality is poor and the purification rate is low;

微生物处理电镀污水较前述处理方法效果较好,如专利CN1096769A提供的微生物法治理电镀废水新技术,对Cr6+去除明显,但对综合电镀废水处理不能完全达标,尤其是废水中的镍和锌。由于其技术的局限性和不稳定性,对大水量、高浓度电镀废水目前还无法推广应用。Microbial treatment of electroplating wastewater is more effective than the aforementioned treatment methods. For example, the new technology of microbial treatment of electroplating wastewater provided by patent CN1096769A can significantly remove Cr 6+ , but it cannot fully meet the standards for comprehensive electroplating wastewater treatment, especially nickel and zinc in wastewater. . Due to the limitations and instability of its technology, it cannot be popularized and applied to large-volume, high-concentration electroplating wastewater.

发明目的purpose of invention

鉴于目前各种治理电镀废水的现状,本发明的目的是研制一种利用微生物治理电镀废水,提供一种高效率、技术稳定、抗冲击负荷和运行成本低、适用于大水量、高浓度情况下的生化法治理电镀废水的工艺。In view of the current status of various treatment of electroplating wastewater, the purpose of the present invention is to develop a treatment of electroplating wastewater using microorganisms to provide a high-efficiency, technically stable, impact-resistant load and low operating cost, suitable for large water volumes and high concentrations. The process of treating electroplating wastewater by biochemical method.

本生化法治理电镀废水工艺特征在于利用BM功能菌团对电镀废水进行处理,处理步骤如下:The biochemical method for treating electroplating wastewater is characterized in that the electroplating wastewater is treated by using BM functional bacteria group, and the processing steps are as follows:

1)、将电镀废水引入调节池,调节其水量、均化水质;1) Introduce the electroplating wastewater into the regulating tank to adjust the water volume and homogenize the water quality;

2)、将调节池内的电镀废水经过第一级静态混合器,同时向第一级静态混合器内加入BM功能菌,加入量为第一级静态混合器内电镀废水流量的1/50-200,进入BM反应器或池,进行一级生物反应,停留1-2.5小时;2) Pass the electroplating wastewater in the regulating tank through the first-stage static mixer, and add BM functional bacteria into the first-stage static mixer at the same time, the amount added is 1/50-200 of the flow rate of the electroplating wastewater in the first-stage static mixer , enter the BM reactor or pool, carry out the first-order biological reaction, and stay for 1-2.5 hours;

3)、将进行一级生物反应后的电镀废水经过第二静态混合器,加入含量为30%氢氧化钠溶液,加入量视电镀废水酸度而定,调整PH值到7.0-8.5,或同时加入BM功能菌,其加入量为电镀废水流量的1-3‰,进行二级生化反应沉淀过滤,停留2.5-4小时;3) Pass the electroplating wastewater after the primary biological reaction through the second static mixer, add 30% sodium hydroxide solution, the amount depends on the acidity of the electroplating wastewater, adjust the pH value to 7.0-8.5, or add at the same time BM functional bacteria, the amount added is 1-3‰ of the electroplating wastewater flow rate, and the secondary biochemical reaction is precipitated and filtered, and the residence time is 2.5-4 hours;

4)、将经过二级生化反应沉淀过滤后的电镀废水即达到国家污水综合排放标准GB8978-1996中的一级标准;4) The electroplating wastewater after secondary biochemical reaction sedimentation and filtration reaches the first-level standard in the national sewage comprehensive discharge standard GB8978-1996;

5)、将两级生化反应的沉淀物收集至污泥干化池干化或经浓缩后压滤,可回收重金属。5) Collect the sediment from the two-stage biochemical reaction to the sludge drying tank for drying or pressure filtration after concentration to recover heavy metals.

上述处理电镀综合废水最佳工艺条件是:废水PH值为3.0-8.0,反应温度10~50℃。The above optimal process conditions for treating electroplating comprehensive wastewater are: the pH value of the wastewater is 3.0-8.0, and the reaction temperature is 10-50°C.

上述的生化法治理电镀废水工艺所述的是由脱硫弧菌、脱硫球菌、脱硫带环菌组成的BM功能菌,生长条件为厌氧生长,温度20-40℃,生长时间为12-24小时。The above-mentioned process of treating electroplating wastewater by biochemical method refers to the BM functional bacteria composed of Desulfovibrio, Desulfococcus, and Desulfurized Cyclobacterium. The growth conditions are anaerobic growth, the temperature is 20-40°C, and the growth time is 12-24 hours. .

BM功能菌经过长期的筛选和培育,它们之间存在着化学、物理、生物三个层次的相互协作。因此,BM菌团具有静电吸附、价态转化、络合、絮凝和缓冲PH值五大功能,将废水中的重金属离子富集于BM菌的表面,经固液分离,再进入二级生化反应沉淀过滤后,即可使电镀废水达标排放。本发明的优点在于:BM functional bacteria have undergone long-term screening and cultivation, and there are three levels of mutual cooperation among them: chemistry, physics, and biology. Therefore, the BM bacteria group has five functions of electrostatic adsorption, valence transformation, complexation, flocculation and pH buffering. It enriches the heavy metal ions in the wastewater on the surface of the BM bacteria, separates the solid and liquid, and then enters the secondary biochemical reaction precipitation. After filtering, the electroplating wastewater can be discharged up to the standard. The advantages of the present invention are:

1、废水处理工程将彻底解决企业的生产废水对环境的污染问题。1. The wastewater treatment project will completely solve the problem of environmental pollution caused by the production wastewater of the enterprise.

2、生化处理后的电镀废水完全可以回用至对水质要求十分严格的地方,回用一般不低于50%。2. The electroplating wastewater after biochemical treatment can be completely reused in places with strict water quality requirements, and the reuse is generally not less than 50%.

3、与传统处理工艺一一化学法相比,可节约大笔运行费用和维修成本。如严格按照国家一级标准排放,化学法通常处理1吨废水需3-8元,生化法仅1.2元左右,二者相差约2.0元以上。3. Compared with the traditional treatment process—chemical method, it can save a lot of operating costs and maintenance costs. If the discharge is strictly in accordance with the national first-level standard, the chemical method usually costs 3-8 yuan to treat 1 ton of wastewater, while the biochemical method only costs about 1.2 yuan, and the difference between the two is about 2.0 yuan or more.

4、泥渣量少,金属可回收,无二次污染。BM菌将电镀废水中的重金属离子通过吸附等作用形成颗粒状沉降物,其渣量很少。由于污泥中重金属含量较高,将污泥集中进行处理,能将重金属回收或化工原料。经提取后污泥剩余量更少,其重金属残存量较低,从而有效地避免了二次污染。4. The amount of sludge is small, the metal can be recycled, and there is no secondary pollution. BM bacteria will form the heavy metal ions in the electroplating wastewater through adsorption and other actions to form granular sediments, and the amount of slag is very small. Due to the high content of heavy metals in sludge, centralized treatment of sludge can recover heavy metals or chemical raw materials. After extraction, the residual amount of sludge is less, and the residual amount of heavy metals is lower, thus effectively avoiding secondary pollution.

综上所述,本发明利用BM功能菌处理电镀综合废水,克服了现有化学法、电解法、离子交换法的不足、兼有了化学法、电解法、离子交换法、微生物法等治理电镀废水的优点,具有独特的技术优势,可处理综合电镀废水,且处理能力强、效率高、用菌量少、出水水质稳定、抗冲击负荷和运行成本低、操作管理简便、适用于处理大水量、高浓度的电镀废水。In summary, the present invention uses BM functional bacteria to treat electroplating comprehensive wastewater, overcomes the deficiencies of existing chemical methods, electrolytic methods, and ion exchange methods, and combines chemical methods, electrolytic methods, ion exchange methods, and microbial methods to treat electroplating. The advantages of wastewater, with unique technical advantages, can handle comprehensive electroplating wastewater, and has strong processing capacity, high efficiency, less bacteria, stable effluent quality, impact load resistance and low operating cost, easy operation and management, and is suitable for processing large amounts of water , High concentration electroplating wastewater.

说明附图Explanatory drawings

图1本发明工艺流程图Fig. 1 process flow chart of the present invention

具体实施方式Detailed ways

实施例1:Example 1:

重庆某电镀厂日排放电镀综合废水400吨,原水指标:(当地环保局监测验收数据)An electroplating factory in Chongqing discharges 400 tons of comprehensive electroplating wastewater per day, and the raw water index: (monitoring and acceptance data of the local environmental protection bureau)

    PH PH     Cr6+ Cr6 +     TCr TCr     Ni2+ Ni 2+     CODcr CODcr     石油类 Petro     3.05 3.05     77.1 77.1     127 127     4.89 4.89     124 124     5.68 5.68

废水流量为20吨/小时,温度25℃,加入400升/小时的BM功能菌经第一级静态混合器进入BM反应器进行一级生物反应1.0小时后,加入30%氢氧化钠溶液,将PH值调整到7.0,经第二级静态混合器,进行二级生化反应沉淀过滤停留2.5小时,出水结果为:Wastewater flow rate is 20 tons/hour, temperature 25 ℃, add the BM functional bacteria of 400 liters/hour and enter BM reactor through the first stage static mixer to carry out the first stage biological reaction after 1.0 hour, add 30% sodium hydroxide solution, will Adjust the pH value to 7.0, and carry out the second-stage biochemical reaction, sedimentation and filtration for 2.5 hours through the second-stage static mixer. The result of the effluent is:

(当地环保局监测验收数据)(Monitoring and acceptance data of the local environmental protection bureau)

    PH PH     Cr6+ Cr6 +     TCr TCr     Ni2+ Ni 2+     CODcr CODcr     石油类 Petro     7.72 7.72     0.102 0.102     0.296 0.296     0.108 0.108     38.5 38.5     1.04 1.04

国家污水综合排放标准(G88978-1996)中的一级标准:The first-level standard in the National Comprehensive Wastewater Discharge Standard (G88978-1996):

    PH PH     Cr6+ Cr6 +     TCr TCr     Ni2+ Ni 2+     CODcr CODcr     石油类 Petro     6--9 6--9     0.5 0.5     1.5 1.5     1.0 1.0     100 100      5 5

出水完全达到国家污水综合排放标准。The effluent fully meets the national sewage comprehensive discharge standard.

实施例2:Example 2:

东莞某电镀厂日排放电镀综合废水1000吨,原水指标:(当地环保局监测验收数据)An electroplating factory in Dongguan discharges 1,000 tons of comprehensive electroplating wastewater per day, and the raw water index: (monitoring and acceptance data of the local environmental protection bureau)

    PH PH     Cr6+ Cr6 +     Cu2+ Cu 2+     Ni2+ Ni 2+     CODcr CODcr     石油类 Petro     3.0 3.0     58.06 58.06     2.51 2.51     5.7 5.7     51.1 51.1     1.3 1.3

废水流量为50吨/小时,温度50℃,加入250升/小时的BM功能菌,经第一级静态混合器进入BM反应器进行一级生物反应2.5小时后,加入30%氢氧化钠溶液,将PH值调整到8.0,经第二级静态混合器,进行二级生化反应沉淀过滤停留4.0小时,出水结果为:The wastewater flow rate is 50 tons/hour, the temperature is 50°C, add 250 liters/hour of BM functional bacteria, and enter the BM reactor through the first-stage static mixer for 2.5 hours of primary biological reaction, then add 30% sodium hydroxide solution, Adjust the pH value to 8.0, and carry out the secondary biochemical reaction, precipitation and filtration for 4.0 hours through the second-stage static mixer, and the result of the effluent is:

(当地环保局监测验收数据)(Monitoring and acceptance data of the local environmental protection bureau)

    PH PH     Cr6+ Cr6 +   Cu2+ Cu 2+     Ni2+ Ni 2+     CODcr CODcr     石油类 Petro     7.0 7.0     0.05 0.05   未测出 not detected     0.1 0.1     49.5 49.5     0.4 0.4

国家污水综合排放标准(GB8978-1996)中的一级标准:The first-level standard in the National Comprehensive Wastewater Discharge Standard (GB8978-1996):

    PH PH     Cr6+ Cr6 +     Cu2+ Cu 2+     Ni2+ Ni 2+     CODcr CODcr     石油类 Petro     6-9 6-9     0.5 0.5     0.5 0.5     1.0 1.0     100 100     5 5

出水完全达到国家污水综合排放标准。The effluent fully meets the national sewage comprehensive discharge standard.

实例3:Example 3:

苏州某电镀厂日排放电镀综合废水100吨,原水指标:An electroplating factory in Suzhou discharges 100 tons of comprehensive electroplating wastewater per day, and the raw water indicators are:

(当地环保局监测验收数据)(Monitoring and acceptance data of the local environmental protection bureau)

    PH PH     Cu2+ Cu 2+     Ni2+ Ni 2+     CODcr CODcr     8.0 8.0     11.25 11.25     12.351 12.351     69 69

废水流量为10吨/小时,温度10℃,加入100升/小时的BM功能菌经第一级静态混合器进入BM反应器进行一级生物反应1.5小时后,加入30升/小时BM功能菌及30%氢氧化钠溶液,将PH值调整到8.5,经第二级静态混合器,进行二级生化反应沉淀过滤停留2.5小时,出水结果为:The wastewater flow rate is 10 tons/hour, the temperature is 10°C, 100 liters/hour of BM functional bacteria is added into the BM reactor through the first-stage static mixer for 1.5 hours of primary biological reaction, and 30 liters/hour of BM functional bacteria and 30% sodium hydroxide solution, adjust the pH value to 8.5, carry out the secondary biochemical reaction, precipitate and filter for 2.5 hours through the second-stage static mixer, and the result of the effluent is:

(当地环保局监测验收数据)(Monitoring and acceptance data of the local environmental protection bureau)

    PH PH     Cu2+ Cu 2+     Ni2+ Ni 2+     CODcr CODcr     7.0 7.0     0.017 0.017     0.248 0.248     20.0 20.0

国家污水综合排放标准(GB8978-1996)中的一级标准:The first-level standard in the National Comprehensive Wastewater Discharge Standard (GB8978-1996):

    PH PH     Cu2+ Cu 2+     Ni2+ Ni 2+     CODcr CODcr     6-9 6-9     0.5 0.5     1.0 1.0     100 100

出水完全达到国家污水综合排放标准。The effluent fully meets the national sewage comprehensive discharge standard.

实施例4:Example 4:

重庆某电镀厂日排放电镀综合废水700吨,原水指标:An electroplating factory in Chongqing discharges 700 tons of comprehensive electroplating wastewater per day, and the raw water indicators are:

(当地环保局监测验收数据)(Monitoring and acceptance data of the local environmental protection bureau)

    PH PH     Cr6+ Cr6 +     Ni2+ Ni 2+     CODcr CODcr     3.5 3.5     65.5 65.5     30.0 30.0     102.0 102.0

废水流量为30吨/小时,温度15℃,加入300升/小时的功能菌经第一级静态混合器进入BM反应器进行一级生物反应1.5小时后,加入90升/小时BM功能菌及30%氢氧化钠溶液,将PH值调整到8.5,经第二级静态混合器,进行二级生化反应沉淀过滤停留2.5小时,出水结果为:The wastewater flow rate is 30 tons/hour, the temperature is 15°C, 300 liters/hour of functional bacteria are added into the BM reactor through the first-stage static mixer for 1.5 hours of primary biological reaction, and 90 liters/hour of BM functional bacteria and 30 % sodium hydroxide solution, adjust the pH value to 8.5, carry out the secondary biochemical reaction, precipitate and filter for 2.5 hours through the second-stage static mixer, and the result of the effluent is:

(当地环保局监测验收数据)(Monitoring and acceptance data of the local environmental protection bureau)

    PH PH     Cr6+ Cr6 +     Ni2+ Ni 2+     CODcr CODcr     7.0 7.0     0.012 0.012     0.045 0.045     76.0 76.0

国家污水综合排放标准(GB8978-1996)中的一级标准:The first-level standard in the National Comprehensive Wastewater Discharge Standard (GB8978-1996):

    PH PH     Cr8+ Cr 8+     Ni2+ Ni 2+     CODcr CODcr     6-9 6-9     0.5 0.5     1.0 1.0     100 100

出水完全达到国家污水综合排放标准。The effluent fully meets the national sewage comprehensive discharge standard.

Claims (2)

1, a kind of biochemical process is administered electroplating wastewater technology, it is characterized in that utilizing the BM function cenobium of being made up of desulfovibrio, desulfurization coccus, desulfurization band bacterium that electroplating sewerage is carried out Two-Stage Biochemical and handles, and treatment step is as follows:
1), electroplating wastewater is introduced equalizing tank, regulates its water yield, homogenizing water quality;
2), with the process of the electroplating wastewater in equalizing tank first step static mixer, in first step static mixer, add the BM function yeast simultaneously, add-on is the 1/50-200 of electroplating wastewater flow in the first step static mixer, enter BM reactor or pond, carry out the one-level biological respinse, stopped 1-2.5 hour;
3), will carry out electroplating wastewater behind the one-level biological respinse through second static mixer, adding content is 30% sodium hydroxide solution, add-on is decided on electroplating wastewater acidity, adjust pH value to 7.0-8.5, or add the BM function yeast simultaneously, its add-on is the 1-3 ‰ of electroplating wastewater flow, carries out the secondary biochemical reaction precipitation and filters, and stops 2.5-4 hour;
4), the electroplating wastewater after will filtering through the secondary biochemical reaction precipitation promptly reach the primary standard among the national sewage comprehensive emission standard GB8978-1996;
5), the throw out with two-stage reaction is collected into mummification of sludge drying pond or press filtration after concentrating, recyclable heavy metal; The optimum process condition of above-mentioned steps is: the waste water pH value is 3.0-8.0,10~50 ℃ of temperature of reaction.
2, administer electroplating wastewater technology according to the described biochemical process of claim 1, it is characterized in that the BM function yeast be made up of desulfovibrio, desulfurization coccus, desulfurization band bacterium, growth conditions is an anaerobic growth, 20~40 ℃ of temperature, and growth time is 12-24 hour.
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CN101560041B (en) * 2009-05-21 2011-08-17 浙江工商大学 Combined treatment method of electroplating wastewater by biochemical method and decomplexation
CN101830600B (en) * 2010-03-23 2012-02-22 天津大学 Treatment method of comprehensive electroplating wastewater
CN102010102B (en) * 2010-11-08 2012-06-13 兰溪市卓越电子有限公司 Method for treating electroplating wastewater
CN102115295B (en) * 2010-12-25 2012-10-24 浙江平湖绿色环保技术发展有限公司 Electroplating waste water high-efficiency combined biochemical treatment technique
CN108251644B (en) * 2016-12-29 2019-12-06 财团法人工业技术研究院 Electrode for selectively adsorbing precious metals and method for selectively recovering precious metals
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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
CN1160026A (en) * 1995-11-07 1997-09-24 古河电气工业株式会社 Apparatus for manufacturing optical fiber preform
EP0880475A1 (en) * 1996-02-06 1998-12-02 Thiopaq Sulfur Systems B.V. Process for the treatment of water containing heavy metal ions
DE10009887A1 (en) * 2000-03-01 2001-09-06 Taelim Industry Co Ltd On-site removal of nitrogen from dirty water using apparatus with one microbially-operated denitrifying deaeration vessels and two bacterially-operated nitrifying aeration vessels in each unit
CN1382651A (en) * 2001-04-20 2002-12-04 上海金迪生物技术工程有限公司 Process for comprehensively treating sewage

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
CN1160026A (en) * 1995-11-07 1997-09-24 古河电气工业株式会社 Apparatus for manufacturing optical fiber preform
EP0880475A1 (en) * 1996-02-06 1998-12-02 Thiopaq Sulfur Systems B.V. Process for the treatment of water containing heavy metal ions
DE10009887A1 (en) * 2000-03-01 2001-09-06 Taelim Industry Co Ltd On-site removal of nitrogen from dirty water using apparatus with one microbially-operated denitrifying deaeration vessels and two bacterially-operated nitrifying aeration vessels in each unit
CN1382651A (en) * 2001-04-20 2002-12-04 上海金迪生物技术工程有限公司 Process for comprehensively treating sewage

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