CN110482675A - A method of methylene blue waste water is handled with manganous silicate - Google Patents
A method of methylene blue waste water is handled with manganous silicate Download PDFInfo
- Publication number
- CN110482675A CN110482675A CN201910787126.0A CN201910787126A CN110482675A CN 110482675 A CN110482675 A CN 110482675A CN 201910787126 A CN201910787126 A CN 201910787126A CN 110482675 A CN110482675 A CN 110482675A
- Authority
- CN
- China
- Prior art keywords
- methylene blue
- waste water
- manganous silicate
- blue waste
- silicate
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
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Classifications
-
- 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
- C02F2101/00—Nature of the contaminant
- C02F2101/30—Organic compounds
- C02F2101/308—Dyes; Colorants; Fluorescent agents
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2101/00—Nature of the contaminant
- C02F2101/30—Organic compounds
- C02F2101/38—Organic compounds containing nitrogen
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2103/00—Nature of the water, waste water, sewage or sludge to be treated
- C02F2103/30—Nature of the water, waste water, sewage or sludge to be treated from the textile industry
-
- 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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- Chemical & Material Sciences (AREA)
- Life Sciences & Earth Sciences (AREA)
- Hydrology & Water Resources (AREA)
- Engineering & Computer Science (AREA)
- Environmental & Geological Engineering (AREA)
- Water Supply & Treatment (AREA)
- Organic Chemistry (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Treatment Of Water By Oxidation Or Reduction (AREA)
Abstract
The invention discloses a kind of methods for handling methylene blue waste water, include the following steps: at room temperature, and manganous silicate and hydrogen peroxide are added in methylene blue waste water, are catalyzed fenton-type reagent reaction by manganous silicate, realize the removal of methylene blue.The processing method of methylene blue waste water of the invention, simple process, without adjusting pH value of waste water, short processing time, materials are few, and treatment effeciency is high.It is expected to become a kind of environmental-friendly wastewater treatment method as the fenton-type reagent method of catalyst using manganous silicate.
Description
Technical field
The present invention provides a kind of method for handling methylene blue waste water, belongs to dye wastewater treatment field.
Background technique
The processing method of textile printing and dyeing wastewater has absorption method, flocculence, electrolysis method, bioanalysis and advanced oxidation processes.
The disadvantages of Fenton oxidation method is most common advanced oxidation processes, but there are reaction time length, pH narrow application range.Fenton-like
Oxidizing process has and is not controlled by pH value, and reaction product is only the advantage of clean carbon dioxide and water.The oxide of manganese is exactly one
The typical Fenton-like type catalyst of kind, catalytic activity with higher.However metal oxide preparation process is complicated, synthesis temperature
Degree is high, the period is long.
Metallosilicate material has had both the dual characteristics of the multivalent state of metal oxide and the structural stability of silicate,
Resourceful, cheap, reactivity is higher, and is easy preparation.However do not make in the prior art about by manganous silicate also
It is used to handle the report of methylene blue waste water for Fenton-like type catalyst.The present invention provides a kind of processing methylene blue waste water
Method, for silicate material further application have great importance.
Summary of the invention
The object of the present invention is to provide a kind of methods for handling methylene blue waste water, to achieve the above object, institute of the present invention
The technical scheme steps of use are as follows:
A method of processing methylene blue waste water, which is characterized in that at room temperature, in methylene blue waste water be added manganous silicate and
Hydrogen peroxide is kept for 60 minutes under stirring, is catalyzed fenton-type reagent reaction by manganous silicate, is realized methylene blue
Removal.
The methylene blue wastewater treatment method, which is characterized in that methylene blue methylene blue in waste, manganous silicate and
The content of hydrogen peroxide is respectively 0.05g/L, 0.1g/L, 16.7g/L.
Beneficial effects of the present invention:
(1) method of a kind of processing methylene blue waste water of the invention, simple process handle the time without adjusting pH value of waste water
Short, materials are few, and treatment effeciency is high.
Specific embodiment
The invention will be further described in conjunction with the embodiments, it should illustrate to be, following the description is merely to explain this hair
It is bright, its content is not defined.
The calculation method of Methylene Blue removal rate of the present invention are as follows: measure methylene with ultraviolet specrophotometer at 664nm
The absorbance of base indigo plant waste water finds out the removal of methylene blue by the variation of methylene blue waste water absorbance before and after oxidation reaction
Rate.Calculation formula are as follows: removal rate (%)=(A0- A)/A0× 100%, in formula, A0For the absorbance before methylene blue waste water reaction
Value, A are the absorbance value after reaction.
Embodiment 1
2.84g sodium metasilicate and 1.98g manganese chloride is taken to be dissolved in 50mL deionized water respectively, it is under stirring, sodium metasilicate is molten
Liquid is slowly added into metal salt solution, forms mixed solution, is persistently stirred 15 minutes at room temperature, and centrifugation is clear with deionized water
It washes 3 times, is dried at 60 DEG C, obtain taupe manganous silicate powder.
It takes 10mg manganous silicate to be dissolved in the methylene blue waste water that 95mL concentration is 50mg/L, 5mL is added under stirring
The hydrogen peroxide that mass fraction is 30% is kept for 60 minutes, and the removal rate of methylene blue is up to 96%.
The above is only a preferred embodiment of the present invention, it is noted that for the ordinary skill people of the art
Member, under the premise of not departing from the method for the present invention, can also make several improvements and modifications, these improvements and modifications also should be regarded as
Protection scope of the present invention.
Claims (2)
1. a kind of method for handling methylene blue waste water, which comprises the steps of: at room temperature, useless in methylene blue
Manganous silicate and hydrogen peroxide are added in water, under stirring, is kept for 60 minutes.
2. methylene blue wastewater treatment method as described in claim 1, which is characterized in that methylene blue waste water methylene
The content of blue, manganous silicate and hydrogen peroxide is respectively 0.05g/L, 0.1g/L, 16.7g/L.
Priority Applications (1)
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CN201910787126.0A CN110482675A (en) | 2019-08-25 | 2019-08-25 | A method of methylene blue waste water is handled with manganous silicate |
Applications Claiming Priority (1)
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CN201910787126.0A CN110482675A (en) | 2019-08-25 | 2019-08-25 | A method of methylene blue waste water is handled with manganous silicate |
Publications (1)
Publication Number | Publication Date |
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CN110482675A true CN110482675A (en) | 2019-11-22 |
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CN201910787126.0A Withdrawn CN110482675A (en) | 2019-08-25 | 2019-08-25 | A method of methylene blue waste water is handled with manganous silicate |
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Cited By (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN111579514A (en) * | 2020-05-26 | 2020-08-25 | 山东理工大学 | Method for catalyzing and oxidizing TMB by using manganese silicate to simulate oxidase |
CN116889857A (en) * | 2023-07-11 | 2023-10-17 | 四川农业大学 | Film gradient diffusion method for in-situ selective monitoring lead effective state |
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CN103702936A (en) * | 2011-07-22 | 2014-04-02 | 株式会社半导体能源研究所 | Graphite oxide, graphene oxide or graphene, electric device using same and method of manufacturing same, and electrodialysis apparatus |
WO2014118750A1 (en) * | 2013-01-31 | 2014-08-07 | L'air Liquide, Societe Anonyme Pour L'etude Et L'exploitation Des Procedes Georges Claude | Manganese-containing compounds, their synthesis, and use in manganese-containing film deposition |
WO2014118751A1 (en) * | 2013-01-31 | 2014-08-07 | L'air Liquide, Societe Anonyme Pour L'etude Et L'exploitation Des Procedes Georges Claude | Manganese-containing compounds, their synthesis, and use in manganese-containing film deposition |
CN108273516A (en) * | 2017-10-12 | 2018-07-13 | 北京森泉伟业科技有限公司 | A kind of method that electrolytic manganese residues prepare effective catalyst and catalyzing hydrogen peroxide oxidative degradation methylene blue |
CN108516535A (en) * | 2018-03-15 | 2018-09-11 | 山东理工大学 | A kind of method of extensive preparation carbon nanotube |
CN108786810A (en) * | 2018-05-18 | 2018-11-13 | 东南大学 | A kind of magnetism cupric silicate and its application in catalytic degradation methylene blue waste water |
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2019
- 2019-08-25 CN CN201910787126.0A patent/CN110482675A/en not_active Withdrawn
Patent Citations (6)
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CN103702936A (en) * | 2011-07-22 | 2014-04-02 | 株式会社半导体能源研究所 | Graphite oxide, graphene oxide or graphene, electric device using same and method of manufacturing same, and electrodialysis apparatus |
WO2014118750A1 (en) * | 2013-01-31 | 2014-08-07 | L'air Liquide, Societe Anonyme Pour L'etude Et L'exploitation Des Procedes Georges Claude | Manganese-containing compounds, their synthesis, and use in manganese-containing film deposition |
WO2014118751A1 (en) * | 2013-01-31 | 2014-08-07 | L'air Liquide, Societe Anonyme Pour L'etude Et L'exploitation Des Procedes Georges Claude | Manganese-containing compounds, their synthesis, and use in manganese-containing film deposition |
CN108273516A (en) * | 2017-10-12 | 2018-07-13 | 北京森泉伟业科技有限公司 | A kind of method that electrolytic manganese residues prepare effective catalyst and catalyzing hydrogen peroxide oxidative degradation methylene blue |
CN108516535A (en) * | 2018-03-15 | 2018-09-11 | 山东理工大学 | A kind of method of extensive preparation carbon nanotube |
CN108786810A (en) * | 2018-05-18 | 2018-11-13 | 东南大学 | A kind of magnetism cupric silicate and its application in catalytic degradation methylene blue waste water |
Non-Patent Citations (1)
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Cited By (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN111579514A (en) * | 2020-05-26 | 2020-08-25 | 山东理工大学 | Method for catalyzing and oxidizing TMB by using manganese silicate to simulate oxidase |
CN116889857A (en) * | 2023-07-11 | 2023-10-17 | 四川农业大学 | Film gradient diffusion method for in-situ selective monitoring lead effective state |
CN116889857B (en) * | 2023-07-11 | 2024-04-02 | 四川农业大学 | Film gradient diffusion method for in-situ selective monitoring lead effective state |
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