CN103121744A - Method for treating azo dye wastewater - Google Patents
Method for treating azo dye wastewater Download PDFInfo
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- CN103121744A CN103121744A CN2013100363443A CN201310036344A CN103121744A CN 103121744 A CN103121744 A CN 103121744A CN 2013100363443 A CN2013100363443 A CN 2013100363443A CN 201310036344 A CN201310036344 A CN 201310036344A CN 103121744 A CN103121744 A CN 103121744A
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- Prior art keywords
- azo dye
- dye wastewater
- potassium hydrogen
- carbon fiber
- hydrogen peroxymonosulfate
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Abstract
The invention relates to a treatment method of azo dye wastewater, and the treatment method particularly comprises the following steps of: simultaneously adding active carbon fibers and oxidizing agent potassium hydrogen peroxymonosulfate in proportion under the reaction condition of normal temperature and pressure, stirring and treating the azo dye wastewater, wherein the mole ratio of pollutants/potassium hydrogen peroxymonosulfate is 1/10-1/40, and the adding amount of the active carbon fibers is 0.2-1.0 g/L. The treatment method disclosed by the invention is carried out at normal temperature and pressure, is moderate in reaction condition and easy to operate and has a better treatment effect on the azo dye wastewater with various colority.
Description
Technical field
The invention belongs to technical field of sewage, be specifically related to the method that activated carbon fiber catalysis potassium hydrogen peroxymonosulfate is processed azo dye wastewater.
Background technology
Dyestuff is to make fiber and the painted material of other materials, be widely used in the fields such as weaving, printing and dyeing, papermaking, plastics, leather, rubber, coating, printing ink, makeup, sensitive materials, the processing of consequent various waste water from dyestuff is a great problems: waste water from dyestuff has the advantages that organic content is high, colourity is high (can reach 500-500000 doubly), recalcitrant substance is many.Azoic dyestuff account in dyestuff more than 80%, use the most general.Therefore, the processing of azo dyes waste water has very high practical value.
Summary of the invention
The treatment process that the purpose of this invention is to provide a kind of azo dye wastewater, namely a kind of reaction conditions is gentle, and is simple to operate, and the advanced oxidation processes that processing efficiency is high is processed the method for azo dye wastewater.
Method of the present invention is characterized in that, is to add active carbon fibre peacekeeping potassium hydrogen peroxymonosulfate to process Wastewater Dyes class organic pollutant in the waste water that contains the dye class organic pollutant.
When pollutent/potassium hydrogen peroxymonosulfate mol ratio is 1/10~1/40, when the dosage of activated carbon fiber is 0.2g/L~1.0g/L, can guarantee the efficient removal to dyestuff contaminant.
Advantage of the present invention is simple to operate, carries out under normal temperature and pressure, and reaction conditions is gentle; In addition, the present invention also has an outstanding advantages, namely the azo dye wastewater of various colourities is all had good treatment effect.
Embodiment:
Waste water from dyestuff is the bio-refractory waste water of a quasi-representative, consider it is wherein azoic dyestuff more than 80%, the present invention selects gold orange II as the representative of azoic dyestuff pollutent, the degraded of research gold orange II solution can represent the degraded of difficult biochemical organic waste water to a certain extent, selects the waste water from dyestuff that contains gold orange II in therefore following embodiment.
Concrete operations are first to add potassium hydrogen peroxymonosulfate in gold orange II waste water from dyestuff, after mixing, (putting into distilled water boiled 30 minutes to add immediately the viscose-based active carbon fiber felt of anticipating, then oven dry) degrading, is wherein 1/10~1/40 to add potassium hydrogen peroxymonosulfate according to pollutent/potassium hydrogen peroxymonosulfate mol ratio.Temperature is made as 25 ℃, and stirs, and stirs and adopts mechanical stirring.
Embodiment 1:
The processing example of low concentration gold orange II waste water from dyestuff (colourity is less than 2000 times).
Specific as follows: as to get gold orange II waste water from dyestuff 250mL, starting point concentration is 20mg/L, active carbon fibre peacekeeping potassium hydrogen peroxymonosulfate is rendered in the reaction vessel that fills gold orange II solution, gold orange II/ potassium hydrogen peroxymonosulfate mol ratio is respectively 1/20,1/30,1/40, the activated carbon fiber dosage is 0.2g/L, mix to be placed on vibrator and vibrate, adjusting temperature is 25 ℃.
Experimental result:
Embodiment 2:
The processing example of intermediate concentration gold orange II waste water from dyestuff (chromaticity range is 5000-10000 times).
Specific as follows: as to get gold orange II waste water from dyestuff 250mL, starting point concentration is 100mg/L, active carbon fibre peacekeeping potassium hydrogen peroxymonosulfate is rendered in the reaction vessel that fills gold orange II solution, gold orange II/ potassium hydrogen peroxymonosulfate mol ratio is respectively 1/10,1/20,1/30, the activated carbon fiber dosage is 0.3g/L, mix to be placed on vibrator and vibrate, adjusting temperature is 25 ℃.
Experimental result:
Embodiment 3:
The processing example of higher concentration gold orange II waste water from dyestuff (colourity is greater than 20000 times).
Specific as follows: as to get gold orange II waste water from dyestuff 250mL, starting point concentration is 500mg/L, active carbon fibre peacekeeping potassium hydrogen peroxymonosulfate is rendered in the reaction vessel that fills gold orange II waste water from dyestuff, gold orange II/ potassium hydrogen peroxymonosulfate mol ratio is 1/20, the activated carbon fiber dosage is respectively 0.5g/L, 0.8g/L, 1.0g/L, mix to be placed on vibrator and vibrate, adjusting temperature is 25 ℃.
Experimental result:
Claims (5)
1. a method of processing azo dye wastewater, is characterized in that first adding potassium hydrogen peroxymonosulfate, adds immediately activated carbon fiber after mixing, then reacts 25 ℃ of lower mechanical stirring.
2. treatment process as claimed in claim 1, is characterized in that the azo dye wastewater of various colourities is all had good treatment effect, concrete chromaticity range be 1000-50000 doubly.
3. treatment process as claimed in claim 1, is characterized in that the activated carbon fiber that adds is that pretreatment mode is through pre-treatment viscose-based active carbon fiber felt: put into distilled water and boiled 30 minutes, then oven dry.
4. treatment process as claimed in claim 1 is characterized in that the pollutent that adds/potassium hydrogen peroxymonosulfate mol ratio 1/10~1/40.
5. treatment process as claimed in claim 1 is characterized in that the dosage of the activated carbon fiber that adds is for being 0.2g/L~1.0g/L.
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CN2013100363443A CN103121744A (en) | 2013-01-18 | 2013-01-18 | Method for treating azo dye wastewater |
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CN2013100363443A CN103121744A (en) | 2013-01-18 | 2013-01-18 | Method for treating azo dye wastewater |
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CN103121744A true CN103121744A (en) | 2013-05-29 |
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CN2013100363443A Pending CN103121744A (en) | 2013-01-18 | 2013-01-18 | Method for treating azo dye wastewater |
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Cited By (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN103303998A (en) * | 2013-06-28 | 2013-09-18 | 山东大学 | Method for purifying cationic dye wastewater based on lithocholic acid salt gel adsorption |
CN108176403A (en) * | 2018-01-24 | 2018-06-19 | 四川农业大学 | A kind of activated carbon fiber-loaded Co3O4The preparation method of catalysis material |
CN108298668A (en) * | 2018-03-31 | 2018-07-20 | 苏州科技大学 | A kind of method of azo dyes gold orange-G in degrading waste water |
CN110563116A (en) * | 2019-09-09 | 2019-12-13 | 安徽科技学院 | Method for degrading azo dye gold orange II solution by catalyzing persulfate through aluminum alloy pickling waste liquid |
Citations (3)
Publication number | Priority date | Publication date | Assignee | Title |
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JPH09271787A (en) * | 1996-04-03 | 1997-10-21 | Mitsubishi Gas Chem Co Inc | Method of decolorizing dyestuff containing water solution |
CN101525177A (en) * | 2008-12-16 | 2009-09-09 | 中国海洋大学 | Method of using active persulphate for processing difficult-biodegradability organic waste water |
CN101774674A (en) * | 2010-01-10 | 2010-07-14 | 中国海洋大学 | Method for processing organic wastewater by inorganic peroxide |
-
2013
- 2013-01-18 CN CN2013100363443A patent/CN103121744A/en active Pending
Patent Citations (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPH09271787A (en) * | 1996-04-03 | 1997-10-21 | Mitsubishi Gas Chem Co Inc | Method of decolorizing dyestuff containing water solution |
CN101525177A (en) * | 2008-12-16 | 2009-09-09 | 中国海洋大学 | Method of using active persulphate for processing difficult-biodegradability organic waste water |
CN101774674A (en) * | 2010-01-10 | 2010-07-14 | 中国海洋大学 | Method for processing organic wastewater by inorganic peroxide |
Non-Patent Citations (1)
Title |
---|
中国环境科学学会: "《中国环境科学学会学术年会论文集2010(第3卷)》", 31 August 2010, article "活性炭激活过硫酸盐水处理技术:操作方式的影响" * |
Cited By (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN103303998A (en) * | 2013-06-28 | 2013-09-18 | 山东大学 | Method for purifying cationic dye wastewater based on lithocholic acid salt gel adsorption |
CN103303998B (en) * | 2013-06-28 | 2014-07-23 | 山东大学 | Method for purifying cationic dye wastewater based on lithocholic acid salt gel adsorption |
CN108176403A (en) * | 2018-01-24 | 2018-06-19 | 四川农业大学 | A kind of activated carbon fiber-loaded Co3O4The preparation method of catalysis material |
CN108298668A (en) * | 2018-03-31 | 2018-07-20 | 苏州科技大学 | A kind of method of azo dyes gold orange-G in degrading waste water |
CN110563116A (en) * | 2019-09-09 | 2019-12-13 | 安徽科技学院 | Method for degrading azo dye gold orange II solution by catalyzing persulfate through aluminum alloy pickling waste liquid |
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Application publication date: 20130529 |