CN1280105A - Electric ally caltalytic contact oxidizing technology - Google Patents
Electric ally caltalytic contact oxidizing technology Download PDFInfo
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- CN1280105A CN1280105A CN 99110084 CN99110084A CN1280105A CN 1280105 A CN1280105 A CN 1280105A CN 99110084 CN99110084 CN 99110084 CN 99110084 A CN99110084 A CN 99110084A CN 1280105 A CN1280105 A CN 1280105A
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- reactor
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- waste water
- catalyzer
- caltalytic
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- 230000001590 oxidative effect Effects 0.000 title claims abstract 5
- 238000005516 engineering process Methods 0.000 title claims description 6
- 239000002351 wastewater Substances 0.000 claims abstract description 33
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 claims abstract description 14
- 239000001301 oxygen Substances 0.000 claims abstract description 14
- 229910052760 oxygen Inorganic materials 0.000 claims abstract description 14
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 11
- GWEVSGVZZGPLCZ-UHFFFAOYSA-N Titan oxide Chemical compound O=[Ti]=O GWEVSGVZZGPLCZ-UHFFFAOYSA-N 0.000 claims abstract description 8
- 238000006243 chemical reaction Methods 0.000 claims abstract description 6
- GNTDGMZSJNCJKK-UHFFFAOYSA-N divanadium pentaoxide Chemical compound O=[V](=O)O[V](=O)=O GNTDGMZSJNCJKK-UHFFFAOYSA-N 0.000 claims abstract description 6
- 239000002808 molecular sieve Substances 0.000 claims abstract description 4
- URGAHOPLAPQHLN-UHFFFAOYSA-N sodium aluminosilicate Chemical compound [Na+].[Al+3].[O-][Si]([O-])=O.[O-][Si]([O-])=O URGAHOPLAPQHLN-UHFFFAOYSA-N 0.000 claims abstract description 4
- 229910021536 Zeolite Inorganic materials 0.000 claims abstract description 3
- HNPSIPDUKPIQMN-UHFFFAOYSA-N dioxosilane;oxo(oxoalumanyloxy)alumane Chemical compound O=[Si]=O.O=[Al]O[Al]=O HNPSIPDUKPIQMN-UHFFFAOYSA-N 0.000 claims abstract description 3
- 239000004576 sand Substances 0.000 claims abstract description 3
- 239000010457 zeolite Substances 0.000 claims abstract description 3
- 239000000945 filler Substances 0.000 claims description 10
- 239000004408 titanium dioxide Substances 0.000 claims description 3
- 239000000203 mixture Substances 0.000 claims description 2
- -1 gac Substances 0.000 claims 1
- JEGUKCSWCFPDGT-UHFFFAOYSA-N h2o hydrate Chemical compound O.O JEGUKCSWCFPDGT-UHFFFAOYSA-N 0.000 claims 1
- 238000000034 method Methods 0.000 abstract description 15
- 239000003054 catalyst Substances 0.000 abstract description 14
- 239000005416 organic matter Substances 0.000 abstract description 10
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 abstract description 3
- VYPSYNLAJGMNEJ-UHFFFAOYSA-N Silicium dioxide Chemical compound O=[Si]=O VYPSYNLAJGMNEJ-UHFFFAOYSA-N 0.000 abstract description 2
- 230000003197 catalytic effect Effects 0.000 abstract description 2
- 229910052799 carbon Inorganic materials 0.000 abstract 1
- 239000010865 sewage Substances 0.000 abstract 1
- 238000004043 dyeing Methods 0.000 description 9
- 238000007254 oxidation reaction Methods 0.000 description 8
- 230000003647 oxidation Effects 0.000 description 5
- 239000000126 substance Substances 0.000 description 5
- 238000004042 decolorization Methods 0.000 description 4
- 230000015556 catabolic process Effects 0.000 description 3
- 238000006731 degradation reaction Methods 0.000 description 3
- 208000028659 discharge Diseases 0.000 description 3
- 239000000975 dye Substances 0.000 description 3
- 238000001179 sorption measurement Methods 0.000 description 3
- XEEYBQQBJWHFJM-UHFFFAOYSA-N Iron Chemical compound [Fe] XEEYBQQBJWHFJM-UHFFFAOYSA-N 0.000 description 2
- 238000005273 aeration Methods 0.000 description 2
- 239000006185 dispersion Substances 0.000 description 2
- 238000011160 research Methods 0.000 description 2
- 238000002306 biochemical method Methods 0.000 description 1
- 230000015271 coagulation Effects 0.000 description 1
- 238000005345 coagulation Methods 0.000 description 1
- 230000000694 effects Effects 0.000 description 1
- 230000007613 environmental effect Effects 0.000 description 1
- 239000003344 environmental pollutant Substances 0.000 description 1
- 238000001914 filtration Methods 0.000 description 1
- 238000011835 investigation Methods 0.000 description 1
- 229910052742 iron Inorganic materials 0.000 description 1
- 238000012856 packing Methods 0.000 description 1
- 239000002957 persistent organic pollutant Substances 0.000 description 1
- 230000010287 polarization Effects 0.000 description 1
- 231100000719 pollutant Toxicity 0.000 description 1
- 239000000843 powder Substances 0.000 description 1
- 239000000376 reactant Substances 0.000 description 1
- 239000000979 synthetic dye Substances 0.000 description 1
- 238000012360 testing method Methods 0.000 description 1
- 238000010977 unit operation Methods 0.000 description 1
- 238000004065 wastewater treatment Methods 0.000 description 1
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- Treatment Of Water By Oxidation Or Reduction (AREA)
- Catalysts (AREA)
- Water Treatment By Electricity Or Magnetism (AREA)
Abstract
Description
电催化接触氧化工艺是用于处理印染废水及含有难降解有机物的废水治理技术。The electrocatalytic contact oxidation process is used to treat printing and dyeing wastewater and wastewater containing refractory organic matter.
印染行业所用的染料基本上都是人工合成的化学染料,由于化学染料具有品种多,结构复杂,脱色困难、可生化性较差等特点,一直是国内外没有得到很好解决的问题,印染废水的色度对废水处理回用带来了很大的困难,成为实现废水资源化的障碍,是环境科学研究领域急待解决的问题。The dyes used in the printing and dyeing industry are basically artificially synthesized chemical dyes. Due to the characteristics of many types of chemical dyes, complex structures, difficult decolorization, and poor biodegradability, they have not been well resolved at home and abroad. Printing and dyeing wastewater The chromaticity has brought great difficulties to wastewater treatment and reuse, and has become an obstacle to the realization of wastewater resource utilization. It is an urgent problem to be solved in the field of environmental science research.
含有难降解有机物废水由于其可生化性较差,给环境带来很大污染,也是研究领域多年关注和要解决的技术问题。Due to its poor biodegradability, wastewater containing refractory organic matter has brought great pollution to the environment. It is also a technical problem that has been concerned and solved in the research field for many years.
上述两种有机污染物在治理上均有一定难度,处理成本也高。传统的治理方法有化学混凝法、化学氧化法、吸附法、铁屑过滤及生化等方法,在实际工程中,单一用一种处理手段很难取得满意效果,因而实际工程中都是采用多个单元组合工艺,结果是处理工艺路线即长又复杂,处理费用偏高,而且处理后污染物指标仍然达不到国家控制要求的排放标准,这一标准主要指色度和COD值。The above two organic pollutants are difficult to control and the treatment cost is high. Traditional treatment methods include chemical coagulation, chemical oxidation, adsorption, iron filings filtration, and biochemical methods. In actual engineering, it is difficult to achieve satisfactory results with a single treatment method. Therefore, multiple methods are used in actual engineering. The result is that the treatment process route is long and complicated, the treatment cost is high, and the pollutant indicators after treatment still cannot meet the emission standards required by the national control. This standard mainly refers to chromaticity and COD value.
电催化接触氧化工艺的目的是解决印染废水和难降解有机废水达标排放或回用问题,即要缩短工艺流程,又要从根本上解决原有传统技术解决不了的脱色和有机物降解的难点。The purpose of the electrocatalytic contact oxidation process is to solve the problem of standard discharge or reuse of printing and dyeing wastewater and refractory organic wastewater, that is, to shorten the process flow, and fundamentally solve the difficulties of decolorization and organic degradation that cannot be solved by the original traditional technology.
本发明机理是,废水中的有机物在常温下很难被氧化,即使有催化剂存在时也难氧化,但当外加电压时,本发明所用的催化剂表面吸附的氧气可形成含氧自由基,催化剂具有稳定含氧自由基,增大存在寿命,含氧自由基对有机物的氧化无选择性,本发明所用的填料起电极化、吸附及分散作用,因此,当有足够的氧气提供时,废水中的有机物可被不断氧化分解。催化一氧化反应过程在一个反应器中完成,只用一个单元操作,就彻底解决了印染废水的脱色和有机物降解的技术难点问题,用反应式表达为: The mechanism of the present invention is that the organic matter in the wastewater is difficult to be oxidized at normal temperature, even when there is a catalyst, it is also difficult to oxidize, but when an external voltage is applied, the oxygen adsorbed on the surface of the catalyst used in the present invention can form oxygen-containing free radicals, and the catalyst has Oxygen-containing free radicals are stabilized, and the life span is increased. Oxygen-containing free radicals are non-selective to the oxidation of organic matter. The fillers used in the present invention play the role of electric polarization, adsorption and dispersion. Therefore, when enough oxygen is provided, the waste water Organic matter can be continuously oxidized and decomposed. The catalytic oxidation reaction process is completed in one reactor, and only one unit operation is used to completely solve the technical difficulties in the decolorization of printing and dyeing wastewater and the degradation of organic matter. The reaction formula is expressed as:
电催化接触氧化工艺的组成包括催化剂、填料和氧气,催化剂为:二氧化钛或五氧化二钒,催化剂的形状可是粉末状,也可是颗粒状,填料为:分子筛、活性炭、沸石或砂粒,填料是起电极化和吸附、分散作用,增加反应物与催化剂之间的碰撞几率,反应条件是:废水水温为0~40℃,最佳温度15~25℃,大气压为0.8~1.2个大气压,废水的PH值为1~14,最佳为6~8,废水的有机物浓度COD在2000mg/L以下,将催化剂和填料以1∶9至9∶1的比例均匀混合,也可以以同样的比例将催化剂固定在填料上,然后一起放在反应器中,将废水引入反应器,催化剂和欲处理的废水的比例是,催化剂量是欲处理废水量的10%~90%,在反应器的电极的两端施加5~50V的电压,加快催化--氧化的速度,通过曝气管连续通入空气,以保证反应过程中有足够的氧气,废水在反应器内的停留时间为20分钟~10小时,将处理后的水引出反应器。The composition of the electrocatalytic contact oxidation process includes catalyst, filler and oxygen. The catalyst is titanium dioxide or vanadium pentoxide. The shape of the catalyst can be powder or granular. The filler is molecular sieve, activated carbon, zeolite or sand. The filler is Electropolarization, adsorption, and dispersion increase the probability of collision between the reactant and the catalyst. The reaction conditions are: the temperature of the wastewater is 0-40°C, the optimum temperature is 15-25°C, the atmospheric pressure is 0.8-1.2 atmospheres, and the pH of the wastewater The value is 1 to 14, the best is 6 to 8, the organic matter concentration COD of the wastewater is below 2000mg/L, the catalyst and the filler are evenly mixed in a ratio of 1:9 to 9:1, and the catalyst can also be fixed in the same ratio On the packing, then put them together in the reactor, introduce the wastewater into the reactor, the ratio of the catalyst to the wastewater to be treated is, the amount of catalyst is 10% to 90% of the amount of wastewater to be treated, at both ends of the electrodes of the reactor Apply a voltage of 5-50V to speed up the speed of catalysis-oxidation, and continuously feed air through the aeration tube to ensure sufficient oxygen during the reaction process. The residence time of wastewater in the reactor is 20 minutes to 10 hours. The treated water is led out of the reactor.
本发明从效果看,在有催化剂、电压和足够氧存在条件下,印染废水中的人工合成染料这类难降解有机物质可以被氧化得很完全,处理后的水质指标完全达到国家排放标准,该技术是处理印染废水和含难降解性有机物废水的极佳方法。本发明的优点是工艺路线短,设备简单、占地面积小等优势,不但降低了吨水处理成本,而且完全解决了印染废水的脱色和有机物充分降解的问题。From the effect of the present invention, in the presence of catalyst, voltage and sufficient oxygen, refractory organic substances such as synthetic dyes in printing and dyeing wastewater can be completely oxidized, and the water quality index after treatment can fully meet the national discharge standard. Technology is an excellent method to treat printing and dyeing wastewater and wastewater containing refractory organic matter. The invention has the advantages of short process route, simple equipment and small floor space, which not only reduces the cost per ton of water treatment, but also completely solves the problems of decolorization of printing and dyeing wastewater and sufficient degradation of organic matter.
本发明的具体实施如下:The concrete implementation of the present invention is as follows:
用本发明方法在常温、常压下处理某厂印染废水,其步骤是:Process the printing and dyeing wastewater of a certain factory under normal temperature and normal pressure with the inventive method, and its steps are:
第一步:水质调查:The first step: water quality investigation:
有机物浓度COD:1190mg/LOrganic concentration COD: 1190mg/L
废水色度: 450倍Wastewater chromaticity: 450 times
废水PH: 3Wastewater pH: 3
废水温度: 20℃Wastewater temperature: 20°C
第二步:将20克二氧化钛固定在180克分子筛上,放在反应器中,加入1公升废水,在反应器的电极两端施加20V的电压,加快催化--氧化的速度,通过曝气管连续通入空气,以保证反应中有足够的氧气,整个反应器如同一沸腾床,废水在反应器内停留30分钟充分反应,最后将处理后的水引出反应器。The second step: fix 20 grams of titanium dioxide on 180 grams of molecular sieve, put it in the reactor, add 1 liter of waste water, apply a voltage of 20V across the electrodes of the reactor to speed up the speed of catalysis-oxidation, and pass through the aeration tube Air is fed continuously to ensure sufficient oxygen in the reaction. The whole reactor is like a fluidized bed. The wastewater stays in the reactor for 30 minutes to fully react, and finally the treated water is led out of the reactor.
第三步:处理后的水质检验结果为:Step 3: The water quality test results after treatment are:
有机物浓度COD:70mg/LOrganic concentration COD: 70mg/L
色度: 30倍Chroma: 30 times
PH值: 6PH value: 6
处理后水温: 20℃Water temperature after treatment: 20°C
处理后水质达到国家二级排放标准。The water quality after treatment reaches the national secondary discharge standard.
Claims (3)
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CNB991100840A CN1133593C (en) | 1999-07-07 | 1999-07-07 | Electrocatalytic Contact Oxidation Method |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CNB991100840A CN1133593C (en) | 1999-07-07 | 1999-07-07 | Electrocatalytic Contact Oxidation Method |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| CN1280105A true CN1280105A (en) | 2001-01-17 |
| CN1133593C CN1133593C (en) | 2004-01-07 |
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Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| CNB991100840A Expired - Fee Related CN1133593C (en) | 1999-07-07 | 1999-07-07 | Electrocatalytic Contact Oxidation Method |
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| CN (1) | CN1133593C (en) |
Cited By (7)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| WO2009039325A3 (en) * | 2007-09-20 | 2009-05-14 | Catelectric Corp | Methods and apparatus for the synthesis of useful compounds |
| EP2201046A4 (en) * | 2007-09-20 | 2010-09-22 | Catelectric Corp | METHODS AND APPARATUS FOR THE SYNTHESIS OF USEFUL COMPOUNDS |
| CN102070268A (en) * | 2010-11-26 | 2011-05-25 | 方明环保科技(漳州)有限公司 | Environmentally-friendly treatment method and device for organic sewage |
| US7950221B2 (en) | 2003-04-25 | 2011-05-31 | Catelectric Corp. | Methods and apparatus for controlling catalytic processes, including catalyst regeneration and soot elimination |
| CN102101707A (en) * | 2010-11-26 | 2011-06-22 | 方明环保科技(漳州)有限公司 | Three-dimensional Electrode Electrocatalytic Oxidation Reactor for Wastewater Degradation |
| CN102826632A (en) * | 2012-07-22 | 2012-12-19 | 大连理工大学 | In-situ adsorption-microelectrolysis-catalytic oxidation sewage treatment equipment and method |
| US8414860B2 (en) | 2003-04-25 | 2013-04-09 | Catelectric Corp. | Methods for controlling catalytic processes, including the deposition of carbon based particles |
-
1999
- 1999-07-07 CN CNB991100840A patent/CN1133593C/en not_active Expired - Fee Related
Cited By (11)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| US7950221B2 (en) | 2003-04-25 | 2011-05-31 | Catelectric Corp. | Methods and apparatus for controlling catalytic processes, including catalyst regeneration and soot elimination |
| US8414860B2 (en) | 2003-04-25 | 2013-04-09 | Catelectric Corp. | Methods for controlling catalytic processes, including the deposition of carbon based particles |
| US8511064B2 (en) | 2003-04-25 | 2013-08-20 | Catelectric Corp. | Methods and apparatus for controlling catalytic processes, including catalyst regeneration and soot elimination |
| WO2009039325A3 (en) * | 2007-09-20 | 2009-05-14 | Catelectric Corp | Methods and apparatus for the synthesis of useful compounds |
| EP2201046A4 (en) * | 2007-09-20 | 2010-09-22 | Catelectric Corp | METHODS AND APPARATUS FOR THE SYNTHESIS OF USEFUL COMPOUNDS |
| US7964084B2 (en) | 2007-09-20 | 2011-06-21 | Catelectric Corp. | Methods and apparatus for the synthesis of useful compounds |
| EP2620209A1 (en) * | 2007-09-20 | 2013-07-31 | Catelectric Corp. | Methods and apparatus for the activation of a chemical compound |
| CN102070268A (en) * | 2010-11-26 | 2011-05-25 | 方明环保科技(漳州)有限公司 | Environmentally-friendly treatment method and device for organic sewage |
| CN102101707A (en) * | 2010-11-26 | 2011-06-22 | 方明环保科技(漳州)有限公司 | Three-dimensional Electrode Electrocatalytic Oxidation Reactor for Wastewater Degradation |
| CN102101707B (en) * | 2010-11-26 | 2012-10-03 | 方明环保科技(漳州)有限公司 | Three-dimensional Electrode Electrocatalytic Oxidation Reactor for Wastewater Degradation |
| CN102826632A (en) * | 2012-07-22 | 2012-12-19 | 大连理工大学 | In-situ adsorption-microelectrolysis-catalytic oxidation sewage treatment equipment and method |
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| Publication number | Publication date |
|---|---|
| CN1133593C (en) | 2004-01-07 |
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