CN106045152A - Method for degrading rhodamine B through nanometer Fe3O4/Na2S2O8 jointly - Google Patents
Method for degrading rhodamine B through nanometer Fe3O4/Na2S2O8 jointly Download PDFInfo
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- CN106045152A CN106045152A CN201610539957.2A CN201610539957A CN106045152A CN 106045152 A CN106045152 A CN 106045152A CN 201610539957 A CN201610539957 A CN 201610539957A CN 106045152 A CN106045152 A CN 106045152A
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- rhodamine
- nanometer
- waste water
- na2s2o8
- nanometer fe3o4
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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
- C02F1/725—Treatment of water, waste water, or sewage by oxidation by catalytic oxidation
-
- 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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- Life Sciences & Earth Sciences (AREA)
- 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)
- Removal Of Specific Substances (AREA)
Abstract
The invention belongs to the field of advanced oxidation wastewater treatment engineering, and discloses a method for degrading rhodamine B through a nanometer Fe3O4/Na2S2O8 reaction system. The method includes the steps that under the certain pH condition, Na2S2O8 and nanometer Fe3O4 are added into rhodamine B wastewater, reaction is carried out at the normal temperature, and recycling is achieved through the magnetism of the nanometer Fe3O4. The decolorization ratio of the rhodamine B treated with the method reaches 85% to 90%. 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 dye wastewater treatment.
Description
Technical field
The invention belongs to advanced oxidation waste water treatment engineering field, be specifically related to one and utilize nano ferriferrous oxide
(Fe3O4) and sodium peroxydisulfate (Na2S2O8) method of combined degradation rhodamine B.
Background technology
In recent years, advanced oxidation technology based on persulfate is gradually applied to the process of waste water from dyestuff.With it
Its oxidant is compared, and it has a lot of advantages: in solid state under room temperature, it is easy to stores and carries;High stability, Gao Shui
Dissolubility, relative price is relatively low.But, under normal temperature condition, persulfate is more stable, needs to be penetrated by light, heat, electricity, microwave, γ
The activation methods such as physical method or transition metal such as line decompose generation persulfate free radical and carry out degradable organic pollutant.Wang Zhongming
Na is activated Deng by active carbon loading silver2S2O8Degraded acid orange 7, under acid condition, degradation rate reaches more than 95%;Bai Xiaolong etc. pass through
Thermal activation Na under acid condition2S2O8Processing methylene blue waste water, degradation rate is up to more than 90%;Zuo Chuanmei uses bivalence ironwork
Changing sodium peroxydisulfate and process reactive brilliant orange, degradation rate is up to 95.7%.
But, although the activation methods such as heat, ultraviolet light, microwave, gamma-rays can realize the activation of persulfate, but required
Energy consumption is high;Noble metal then price is the most expensive;Ferrous iron is the efficient activator of activation persulfate, efficient, nontoxic, Non-energy-consumption, but
The side reaction of ferrous iron and persulfuric acid silver will consume a large amount of persulfate, cause this system efficiency to reduce, and this reaction need to be
< carrying out under the conditions of 3, this limits its range of application to pH the most to a certain extent.Therefore, high-performance activator activation over cure is selected
Hydrochlorate, widens pH range of application, reduces the generation of generation persulfate side reaction, raising persulfate system oxidation efficiency and profit
It is activation persulfate degradable organic pollutant key to be solved by rate.
The present invention, on the basis of applicant studies for many years, discloses one and utilizes nanometer Fe3O4Activation Na2S2O8Degrade
The method of rhodamine B, it is achieved that convenient, the efficient degradation of waste water from dyestuff.
Summary of the invention
The invention provides one and utilize nanometer Fe3O4/Na2S2O8The method of system rhodamine B degradation, solves tradition work
Long processing period, secondary pollution and be difficult to problems such as recycling in skill, have that process conditions are simple, operation require lowstand with
And catalysis material such as can be recycled at the feature.Can be widely applied to printing, textile waste processes.
The present invention is that one utilizes nanometer Fe3O4/Na2S2O8The method of system rhodamine B degradation, concrete technical scheme is such as
Under: by controlling pH under certain condition, in rhodamine B, add Na2S2O8And nanometer Fe3O4, shake in constant temperature under room temperature
Swinging in device and vibrate, the rhodamine B percent of decolourization after process reaches more than 90%.Utilize nanometer Fe3O4Magnetic reclaimed circulation profit
With.
In described waste water, the concentration of rhodamine B is 20~80mg/L.
Described pH is 3~4, the control hydrochloric acid of pH and sodium hydroxide regulation.
Described Na2S2O8It is the Na of 30%2S2O8, dosage is 600~800ml/L.
Described nanometer Fe3O4Particle diameter is 20~30nm, is shaped as spherical, and iron content is 99.5%, dosage be 600~
800mg/L。
The temperature of described constant temperature oscillator is room temperature, and rotating speed is 180r/min.
Described degradation time is 3~4h.
In the present invention, Na2S2O8Main Function be for oxidation reaction provide persulfate free radical.
In the present invention, nanometer Fe3O4Main Function be as Na2S2O8Activator, due to its be nanoscale be catalyzed material
Material, has the biggest specific surface area, its surface and Na2S2O8After contact, catalysis produces a large amount of potentiometric titrations, thus improves
Oxidation efficiency.
Beneficial effects of the present invention:
Na2S2O8And nanometer Fe3O4The reaction system constituted, improves the degradation efficiency of waste water from dyestuff;Additionally, due to nanometer
Na2S2O8Itself has magnetic, can pass through Magnet recycle and reuse, significantly reduce processing cost;And relatively conventional work
The ferrous iron activation Na of skill2S2O8Reaction system, the present invention uses nanometer Fe3O4Activation Na2S2O8Effectively reduce due to iron ion
The secondary pollution existed and cause.
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), with salt acid for adjusting pH to 3, adds 600mg/L nanometer in waste water
Fe3O4And 600mg/LNa2S2O8, vibrate under room temperature in the constant temperature oscillator of 180r/min 5h, and in waste water, rhodamine B is de-
Color rate has reached 85.89%.After reaction terminates, Magnetic Isolation nanometer Fe3O4, in 400W ultrasonic cleaner after ultrasonic 10min
With, recycle with desiccant dryness.
Embodiment 2:
Configuration 100mL rhodamine B (20mg/L), with salt acid for adjusting pH to 4, adds 600mg/L nanometer in waste water
Fe3O4And 800mg/LNa2S2O8, vibrate under room temperature in the constant temperature oscillator of 180r/min 5h, and in waste water, rhodamine B is de-
Color rate has reached 90.15%.After reaction terminates, Magnetic Isolation nanometer Fe3O4, in 400W ultrasonic cleaner after ultrasonic 10min
With, recycle with desiccant dryness.
Interpretation of result: test finds, under conditions of control pH is 4, individually adds 800mg/L Na2S2O8, react 5h
After, its percent of decolourization is only 76.18%;And individually add 600mg/L nanometer Fe3O4, after reaction 5h, its percent of decolourization is only
49.56%;Na2S2O8With nanometer Fe3O4After compound reaction 5h, its percent of decolourization is up to 90.15%, and this shows Na2S2O8With nanometer
Fe3O4Between have significant synergism.
To sum up, this example is implemented to show, Na2S2O8With nanometer Fe3O4For degradation of dye waste water, there is good collaborative work
With, simultaneously because nanometer Fe3O4The magnetic being had, it is achieved that the recycling of catalysis material itself, it also avoid due to waste water
The existence of middle iron ion and the secondary pollution that brings, it is achieved that convenient, low-cost environment-friendly processes technique.
Claims (7)
1. a nanometer Fe3O4/Na2S2O8The method of combined degradation rhodamine B, it is characterised in that comprise the following steps: first use
Hydrochloric acid and sodium hydroxide control the pH of waste water under certain condition, add sodium peroxydisulfate and nanometer four oxygen in rhodamine B
Change three-iron, in constant temperature oscillator, carry out decoloring reaction, utilize the magnetic of nano ferriferrous oxide itself that it is recycled.
Method the most according to claim 1, it is characterised in that in described waste water, the concentration of rhodamine B is 20~80mg/L.
Method the most according to claim 1, it is characterised in that described pH is 3~4.
Method the most according to claim 1, it is characterised in that described sodium peroxydisulfate dosage is 600~800mg/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 600~800mg/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 |
---|---|---|---|---|
CN106745650A (en) * | 2016-12-13 | 2017-05-31 | 浙江工业大学 | A kind of method of organic dyestuff in utilization ferriferrous oxide nano cage activation sodium peroxydisulfate degradation water |
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 |
CN107089735A (en) * | 2017-05-08 | 2017-08-25 | 上海城市污染控制工程研究中心有限公司 | A kind of aquaculture wastewater discoloration method |
CN109928482A (en) * | 2019-04-26 | 2019-06-25 | 常州大学 | A kind of method of persulfate activation |
CN113287633A (en) * | 2021-06-02 | 2021-08-24 | 天津大学 | Red tide algae algaecide based on ferroferric oxide activated persulfate and application thereof |
CN113321340A (en) * | 2021-05-18 | 2021-08-31 | 哈尔滨工业大学(深圳) | Method for treating oily ink wastewater by using advanced oxidation coupling degreaser |
Citations (3)
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CN101704600A (en) * | 2009-11-19 | 2010-05-12 | 同济大学 | Segmented treatment method of high-concentration high-chromaticity dye wastewater |
JP2010179272A (en) * | 2009-02-09 | 2010-08-19 | Iwasaki Electric Co Ltd | Wastewater treatment apparatus and wastewater treatment method |
CN103739056A (en) * | 2013-11-20 | 2014-04-23 | 上海大学 | Method for degrading organic dye wastewater by utilizing Fe3O4 to activate potassium persulphate |
-
2016
- 2016-07-08 CN CN201610539957.2A patent/CN106045152A/en active Pending
Patent Citations (3)
Publication number | Priority date | Publication date | Assignee | Title |
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JP2010179272A (en) * | 2009-02-09 | 2010-08-19 | Iwasaki Electric Co Ltd | Wastewater treatment apparatus and wastewater treatment method |
CN101704600A (en) * | 2009-11-19 | 2010-05-12 | 同济大学 | Segmented treatment method of high-concentration high-chromaticity dye wastewater |
CN103739056A (en) * | 2013-11-20 | 2014-04-23 | 上海大学 | Method for degrading organic dye wastewater by utilizing Fe3O4 to activate potassium persulphate |
Cited By (6)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN106745650A (en) * | 2016-12-13 | 2017-05-31 | 浙江工业大学 | A kind of method of organic dyestuff in utilization ferriferrous oxide nano cage activation sodium peroxydisulfate degradation water |
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 |
CN107089735A (en) * | 2017-05-08 | 2017-08-25 | 上海城市污染控制工程研究中心有限公司 | A kind of aquaculture wastewater discoloration method |
CN109928482A (en) * | 2019-04-26 | 2019-06-25 | 常州大学 | A kind of method of persulfate activation |
CN113321340A (en) * | 2021-05-18 | 2021-08-31 | 哈尔滨工业大学(深圳) | Method for treating oily ink wastewater by using advanced oxidation coupling degreaser |
CN113287633A (en) * | 2021-06-02 | 2021-08-24 | 天津大学 | Red tide algae algaecide based on ferroferric oxide activated persulfate and application thereof |
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