CN1327039C - Technology for treating electroplating effluent by biochemical process - Google Patents
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- 238000009713 electroplating Methods 0.000 title claims abstract description 56
- 238000005516 engineering process Methods 0.000 title claims description 5
- 230000003851 biochemical process Effects 0.000 title claims 3
- 239000002351 wastewater Substances 0.000 claims abstract description 64
- 241000894006 Bacteria Species 0.000 claims abstract description 22
- 238000000034 method Methods 0.000 claims abstract description 22
- HEMHJVSKTPXQMS-UHFFFAOYSA-M Sodium hydroxide Chemical compound [OH-].[Na+] HEMHJVSKTPXQMS-UHFFFAOYSA-M 0.000 claims abstract description 21
- 230000003068 static effect Effects 0.000 claims abstract description 19
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 17
- 238000005842 biochemical reaction Methods 0.000 claims abstract description 11
- 238000006243 chemical reaction Methods 0.000 claims abstract description 11
- 239000010865 sewage Substances 0.000 claims abstract description 11
- 238000001914 filtration Methods 0.000 claims abstract description 8
- 230000008569 process Effects 0.000 claims abstract description 8
- 238000001556 precipitation Methods 0.000 claims abstract description 7
- 241000605716 Desulfovibrio Species 0.000 claims abstract description 4
- 229910001385 heavy metal Inorganic materials 0.000 claims description 10
- 239000010802 sludge Substances 0.000 claims description 7
- 230000012010 growth Effects 0.000 claims description 4
- 238000001035 drying Methods 0.000 claims description 3
- 230000009604 anaerobic growth Effects 0.000 claims description 2
- 238000006477 desulfuration reaction Methods 0.000 claims 4
- 230000023556 desulfurization Effects 0.000 claims 4
- 240000004808 Saccharomyces cerevisiae Species 0.000 claims 3
- 241001478240 Coccus Species 0.000 claims 2
- 238000002306 biochemical method Methods 0.000 abstract description 5
- 230000001105 regulatory effect Effects 0.000 abstract description 3
- 241000205236 Desulfurococcus Species 0.000 abstract 1
- 238000010517 secondary reaction Methods 0.000 abstract 1
- PXHVJJICTQNCMI-UHFFFAOYSA-N Nickel Chemical compound [Ni] PXHVJJICTQNCMI-UHFFFAOYSA-N 0.000 description 14
- 230000007613 environmental effect Effects 0.000 description 9
- 238000012544 monitoring process Methods 0.000 description 8
- 239000011651 chromium Substances 0.000 description 6
- 239000000126 substance Substances 0.000 description 6
- 230000008901 benefit Effects 0.000 description 4
- 238000005342 ion exchange Methods 0.000 description 3
- 230000000813 microbial effect Effects 0.000 description 3
- 238000012545 processing Methods 0.000 description 3
- XEEYBQQBJWHFJM-UHFFFAOYSA-N Iron Chemical compound [Fe] XEEYBQQBJWHFJM-UHFFFAOYSA-N 0.000 description 2
- 238000005189 flocculation Methods 0.000 description 2
- 230000016615 flocculation Effects 0.000 description 2
- 150000002500 ions Chemical class 0.000 description 2
- 239000002244 precipitate Substances 0.000 description 2
- 239000013049 sediment Substances 0.000 description 2
- 238000004062 sedimentation Methods 0.000 description 2
- 238000001179 sorption measurement Methods 0.000 description 2
- 238000004065 wastewater treatment Methods 0.000 description 2
- VYZAMTAEIAYCRO-UHFFFAOYSA-N Chromium Chemical compound [Cr] VYZAMTAEIAYCRO-UHFFFAOYSA-N 0.000 description 1
- 241000970818 Cyclobacterium Species 0.000 description 1
- 241000605829 Desulfococcus Species 0.000 description 1
- HCHKCACWOHOZIP-UHFFFAOYSA-N Zinc Chemical compound [Zn] HCHKCACWOHOZIP-UHFFFAOYSA-N 0.000 description 1
- 239000002253 acid Substances 0.000 description 1
- 239000003513 alkali Substances 0.000 description 1
- 230000003139 buffering effect Effects 0.000 description 1
- 239000013043 chemical agent Substances 0.000 description 1
- 229910052804 chromium Inorganic materials 0.000 description 1
- 238000010668 complexation reaction Methods 0.000 description 1
- 230000007812 deficiency Effects 0.000 description 1
- 238000003912 environmental pollution Methods 0.000 description 1
- 238000000605 extraction Methods 0.000 description 1
- 229910052742 iron Inorganic materials 0.000 description 1
- 239000007788 liquid Substances 0.000 description 1
- 230000007774 longterm Effects 0.000 description 1
- 238000012423 maintenance Methods 0.000 description 1
- 238000004519 manufacturing process Methods 0.000 description 1
- 229910052751 metal Inorganic materials 0.000 description 1
- 239000002184 metal Substances 0.000 description 1
- 244000005700 microbiome Species 0.000 description 1
- 229910052759 nickel Inorganic materials 0.000 description 1
- 238000011085 pressure filtration Methods 0.000 description 1
- 238000000746 purification Methods 0.000 description 1
- 239000002994 raw material Substances 0.000 description 1
- 230000008929 regeneration Effects 0.000 description 1
- 238000011069 regeneration method Methods 0.000 description 1
- 239000011347 resin Substances 0.000 description 1
- 229920005989 resin Polymers 0.000 description 1
- 229920006395 saturated elastomer Polymers 0.000 description 1
- 238000012216 screening Methods 0.000 description 1
- 239000002893 slag Substances 0.000 description 1
- 239000007787 solid Substances 0.000 description 1
- 230000009466 transformation Effects 0.000 description 1
- 238000003911 water pollution Methods 0.000 description 1
- 229910052725 zinc Inorganic materials 0.000 description 1
- 239000011701 zinc Substances 0.000 description 1
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- Water Treatment By Electricity Or Magnetism (AREA)
- Treatment Of Water By Oxidation Or Reduction (AREA)
- Purification Treatments By Anaerobic Or Anaerobic And Aerobic Bacteria Or Animals (AREA)
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。
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.
Description
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)
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)
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):
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)
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)
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):
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)
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)
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):
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)
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)
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):
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)
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CNB2004100217715A CN1327039C (en) | 2004-02-06 | 2004-02-06 | Technology for treating electroplating effluent by biochemical process |
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| CNB2004100217715A CN1327039C (en) | 2004-02-06 | 2004-02-06 | Technology for treating electroplating effluent by biochemical process |
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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 |
| US10323331B2 (en) | 2016-12-29 | 2019-06-18 | Industrial Technology Research Institute | Valuable metal selectively adsorbing electrode and method for selectively recovering valuable metals |
Citations (5)
| Publication number | Priority date | Publication date | Assignee | Title |
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| 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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Patent Citations (5)
| 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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