CN106045151A - Method for degrading rhodamine B through nanometer Fe3O4/H2O2 synergistically - Google Patents
Method for degrading rhodamine B through nanometer Fe3O4/H2O2 synergistically Download PDFInfo
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- CN106045151A CN106045151A CN201610536523.7A CN201610536523A CN106045151A CN 106045151 A CN106045151 A CN 106045151A CN 201610536523 A CN201610536523 A CN 201610536523A CN 106045151 A CN106045151 A CN 106045151A
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- rhodamine
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- waste water
- hydrogen peroxide
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F9/00—Multistage treatment of water, waste water or sewage
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/34—Treatment of water, waste water, or sewage with mechanical oscillations
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/66—Treatment of water, waste water, or sewage by neutralisation; pH adjustment
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/72—Treatment of water, waste water, or sewage by oxidation
- C02F1/722—Oxidation by peroxides
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/72—Treatment of water, waste water, or sewage by oxidation
- C02F1/725—Treatment of water, waste water, or sewage by oxidation by catalytic oxidation
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2305/00—Use of specific compounds during water treatment
- C02F2305/02—Specific form of oxidant
- C02F2305/023—Reactive oxygen species, singlet oxygen, OH radical
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2305/00—Use of specific compounds during water treatment
- C02F2305/02—Specific form of oxidant
- C02F2305/026—Fenton's reagent
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- 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
The invention belongs to the field of advanced oxidation wastewater treatment engineering, and discloses a method for degrading rhodamine B through a Fe3O4/H2O2 heterogeneous fenton reaction system. The method includes the steps that under the certain pH condition, H2O2 and nanometer Fe3O4 are added into rhodamine B wastewater, reaction is carried out at the normal temperature, and the recycling is achieved through the magnetism of the nanometer Fe3O4. The decolorization ratio of the rhodamine B treated with the method reaches 90% or above. The method has the advantages that the technology condition is simple, the operation requirement is low, catalytic materials can be recycled, and the method can be widely applied to dyeing and textile wastewater treatment.
Description
Technical field
The invention belongs to advanced oxidation waste water treatment engineering field, be specifically related to one and utilize nanometer Fe3O4Associating H2O2Association
Method with rhodamine B degradation.
Background technology
Rhodamine B (Rhodamine B, RhB), also known as rose-red, is that one is widely used in weaving, printing and organic glass
The dyestuff of the industries such as glass, under this waste water from dyestuff low concentration, its colourity is the highest, if without processing directly discharge, then can contaminant water
Body environment, endangers mankind's drinking water safety.
At present conventional inside dye industry processing method specifically includes that ozone high grade oxidation, anaerobic treatment, anaerobism-good
Oxygen process and biomembrance process etc., these method techniques are complex, the shortcoming such as long processing period and instability.Fenton's reaction
It is hydrogen peroxide and known organic compound (carboxylic acid, alcohol and esters) is oxidized to inorganic states by the mixed solution of ferrous ion,
Treatment of dyeing wastewater is commonly employed.But traditional homogeneous Fenton's reaction is after having processed waste water, due to ferrum from
Son makes solution present certain color, causes secondary pollution;Additionally, the source of iron of catalytic reaction is difficult to recycle the most substantially, improve
Processing cost.Based on problem above, many researchers propose employing nano zero valence iron and hydrogen peroxide composition in recent years
Heterogeneous class Fenton's reaction system carry out degradation of dye waste water, the most effective, be one be worth research direction.
The present invention, on the basis of applicant studies for many years, discloses one and utilizes Fe3O4/H2O2Heterogeneous class Fenton is anti-
The method answering system rhodamine B degradation, it is achieved that convenient, efficient degradation waste water from dyestuff.
Summary of the invention
The invention provides one and utilize Fe3O4/H2O2The method of heterogeneous class Fenton's reaction system rhodamine B degradation, solves
Long processing period, secondary pollution and be difficult to problems such as recycling in traditional handicraft of having determined, have that process conditions are simple, operation
Require the features such as lowstand and catalysis material can be recycled.Can be widely applied to printing, textile waste processes.
The present invention is that one utilizes Fe3O4/H2O2The method of heterogeneous class Fenton's reaction system rhodamine B degradation, concrete skill
Art scheme is as follows: by controlling pH under certain condition, add hydrogen peroxide and nanometer four aoxidizes three in rhodamine B
Ferrum, vibrates under room temperature in constant temperature oscillator, and the rhodamine B percent of decolourization after process reaches more than 90%.Utilize nanometer four oxidation
The magnetic of three-iron is by its recycle and reuse.
In described waste water, the concentration of rhodamine B is 20~60mg/L.
Described pH is 2~3, the control hydrochloric acid of pH and sodium hydroxide regulation.
Described hydrogen peroxide is the hydrogen peroxide of 30%, and dosage is 300~400ml/L.
Described nano ferriferrous oxide particle diameter is 20~30nm, is shaped as spherical, and ferroso-ferric oxide content is 99.5%,
Dosage is 300~400mg/L.
The temperature of described constant temperature oscillator is room temperature, and rotating speed is 180r/min.
Described degradation time is 2~3h.
In the present invention, the Main Function of hydrogen peroxide is to provide superoxide radical and hydroxyl radical free radical for oxidation reaction.
In the present invention, the Main Function of nano ferriferrous oxide is the catalyst as heterogeneous class Fenton's reaction, due to
It is Nanometer grade catalysis material, has the biggest specific surface area, and after its surface contacts with hydrogen peroxide, catalysis produces great amount of hydroxy group
Free radical, thus improve oxidation efficiency.
Beneficial effects of the present invention:
The heterogeneous class Fenton's reaction that hydrogen peroxide and nano ferriferrous oxide are constituted, significantly improves the fall of waste water from dyestuff
Solve efficiency;Additionally, due to nano ferriferrous oxide itself has magnetic, Magnet recycle and reuse can be passed through, greatly drop
Low processing cost;And the homogeneous Fenton's reaction of relatively conventional technique, this heterogeneous Fenton's reaction of the present invention effectively subtracts
Lack the secondary pollution caused owing to iron ion exists.
Detailed description of the invention
Below in conjunction with instantiation, the present invention is further illustrated, but embodiments of the present invention are not limited to this.
Embodiment 1 and example 2 utilize processing method of the present invention to process rhodamine B solution.Wherein, in waste water solution
The rhodamine B of residual utilizes UV-VIS spectrophotometry quantitative analysis under 552nm wavelength.
Embodiment 1:
Configuration 100mL rhodamine B (20mg/L, containing 350ml/L 30% hydrogen peroxide), with salt acid for adjusting pH to 3,
Adding 400mg/L nano ferriferrous oxide in waste water, vibrate under room temperature in the constant temperature oscillator of 180r/min 2h, waste water
The percent of decolourization of middle rhodamine B has reached 96.11%.After reaction terminates, Magnetic Isolation nano ferriferrous oxide, ultrasonic clearly in 400W
Wash in device use after ultrasonic 10min, recycle with desiccant dryness.
Embodiment 2:
Configuration 100mL rhodamine B (20mg/L, containing 350ml/L 30% hydrogen peroxide), with salt acid for adjusting pH to 2,
Adding 300mg/L nano ferriferrous oxide in waste water, vibrate under room temperature in the constant temperature oscillator of 180r/min 2h, waste water
The percent of decolourization of middle rhodamine B has reached 91.18%.After reaction terminates, Magnetic Isolation nano ferriferrous oxide, ultrasonic clearly in 400W
Wash in device use after ultrasonic 10min, recycle with desiccant dryness.
Interpretation of result: test finds, under conditions of control pH is 2, individually adds hydrogen peroxide, and after reaction 2h, it takes off
Color rate is only 59.53%;And individually adding nano ferriferrous oxide, after reaction 2h, its percent of decolourization is only 51.22%;Peroxidating
After hydrogen and nano ferriferrous oxide compound reaction 2h, its percent of decolourization is up to 91.18%, and this shows hydrogen peroxide and nanometer four oxidation
Significant coupling is had between three-iron.
To sum up, this example is implemented to show, hydrogen peroxide and nano ferriferrous oxide have well for degradation of dye waste water
Coupling, simultaneously because the magnetic that nano ferriferrous oxide itself is had, it is achieved that the recycling of catalysis material, also
Avoid due to the existence of iron ion and the secondary pollution that brings in waste water, it is achieved that convenient, low-cost environment-friendly processes technique.
Claims (7)
1. a nanometer Fe3O4/H2O2The method of Synergistic degradation rhodamine B, it is characterised in that comprise the following steps: first use hydrochloric acid
Control the pH of waste water under certain condition with sodium hydroxide, in rhodamine B, add hydrogen peroxide and nanometer four aoxidizes three
Ferrum, carries out decoloring reaction in constant temperature oscillator, utilizes the magnetic of nano ferriferrous oxide itself to recycle it.
Method the most according to claim 1, it is characterised in that in described waste water, the concentration of rhodamine B is 20~60mg/L.
Method the most according to claim 1, it is characterised in that described pH is 2~3.
Method the most according to claim 1, it is characterised in that described 30% hydrogen peroxide dosage is 300~400ml/
L。
Method the most according to claim 1, it is characterised in that described nano ferriferrous oxide particle diameter is 20~30nm, shape
Shape is spherical, and ferroso-ferric oxide content is 99.5%, and dosage is 300~400mg/L.
Method the most according to claim 1, it is characterised in that the temperature of described constant temperature oscillator is room temperature, rotating speed is
180r/min。
Method the most according to claim 1, it is characterised in that the magnetic nano ferroferric oxide for catalysis can circulate
Utilize, can be applicable to printing and dyeing, textile waste process.
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Cited By (6)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN106966484A (en) * | 2017-03-31 | 2017-07-21 | 常州大学 | A kind of nanometer Fe3O4/CaO2The method for repairing the pollution of underground water benzene homologues |
CN106976947A (en) * | 2017-03-31 | 2017-07-25 | 常州大学 | A kind of nanometer Fe3O4/Na2CO4The method of benzene homologues in co-treating wastewater |
CN107055740A (en) * | 2017-04-13 | 2017-08-18 | 河海大学 | A kind of method that hydroquinones promotes ferriferous oxide catalyzing hydrogen peroxide degraded orange G waste water |
CN107089718A (en) * | 2017-06-02 | 2017-08-25 | 常州大学 | A kind of nanometer Fe3O4/CaO2The method for repairing PAEs polluted underground waters |
CN108176401A (en) * | 2018-01-10 | 2018-06-19 | 扬州工业职业技术学院 | A kind of preparation method of the nano ferriferrous oxide Fenton catalyst of selenium doping |
CN108246317A (en) * | 2018-01-10 | 2018-07-06 | 扬州工业职业技术学院 | A kind of recyclable ferroselenium composite nano materials and its application in rhodamine B degradation waste water |
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CN101549294A (en) * | 2008-04-02 | 2009-10-07 | 中国科学院生物物理研究所 | Magnetic nanometer material for processing organic pollutants |
JP2010179272A (en) * | 2009-02-09 | 2010-08-19 | Iwasaki Electric Co Ltd | Wastewater treatment apparatus and wastewater treatment method |
CN105174411A (en) * | 2015-09-17 | 2015-12-23 | 广州天赐高新材料股份有限公司 | Fenton-reaction-based improved industrial organic wastewater treatment method |
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2016
- 2016-07-08 CN CN201610536523.7A patent/CN106045151A/en active Pending
Patent Citations (3)
Publication number | Priority date | Publication date | Assignee | Title |
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CN101549294A (en) * | 2008-04-02 | 2009-10-07 | 中国科学院生物物理研究所 | Magnetic nanometer material for processing organic pollutants |
JP2010179272A (en) * | 2009-02-09 | 2010-08-19 | Iwasaki Electric Co Ltd | Wastewater treatment apparatus and wastewater treatment method |
CN105174411A (en) * | 2015-09-17 | 2015-12-23 | 广州天赐高新材料股份有限公司 | Fenton-reaction-based improved industrial organic wastewater treatment method |
Cited By (6)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN106966484A (en) * | 2017-03-31 | 2017-07-21 | 常州大学 | A kind of nanometer Fe3O4/CaO2The method for repairing the pollution of underground water benzene homologues |
CN106976947A (en) * | 2017-03-31 | 2017-07-25 | 常州大学 | A kind of nanometer Fe3O4/Na2CO4The method of benzene homologues in co-treating wastewater |
CN107055740A (en) * | 2017-04-13 | 2017-08-18 | 河海大学 | A kind of method that hydroquinones promotes ferriferous oxide catalyzing hydrogen peroxide degraded orange G waste water |
CN107089718A (en) * | 2017-06-02 | 2017-08-25 | 常州大学 | A kind of nanometer Fe3O4/CaO2The method for repairing PAEs polluted underground waters |
CN108176401A (en) * | 2018-01-10 | 2018-06-19 | 扬州工业职业技术学院 | A kind of preparation method of the nano ferriferrous oxide Fenton catalyst of selenium doping |
CN108246317A (en) * | 2018-01-10 | 2018-07-06 | 扬州工业职业技术学院 | A kind of recyclable ferroselenium composite nano materials and its application in rhodamine B degradation waste water |
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