CN107902744A - A kind of composite oxidant and preparation method thereof - Google Patents
A kind of composite oxidant and preparation method thereof Download PDFInfo
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- CN107902744A CN107902744A CN201711084893.2A CN201711084893A CN107902744A CN 107902744 A CN107902744 A CN 107902744A CN 201711084893 A CN201711084893 A CN 201711084893A CN 107902744 A CN107902744 A CN 107902744A
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- composite oxidant
- ferrate
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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
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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
- C02F1/42—Treatment of water, waste water, or sewage by ion-exchange
-
- 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
-
- 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
- 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
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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)
- Removal Of Specific Substances (AREA)
- Separation Of Suspended Particles By Flocculating Agents (AREA)
- Treatment Of Water By Oxidation Or Reduction (AREA)
Abstract
The invention discloses a kind of composite oxidant, including following component by weight:5 10 parts of metal chloride, 3 25 parts of silicate, 20 35 parts of ferrate, 12 25 parts of organic solvent, 10 20 parts of chelating agent, 15 25 parts of potassium permanganate, 30 50 parts of deionized water.Composite oxidant produced by the present invention can effectively remove the organic matter for being difficult to remove in dyeing waste water by a variety of effects such as ion exchange;In addition the oxidant is easy to dissolve, and performance is stablized, and odorlessness during dissolving, will not produce toxic gas, the experiment proved that:Processing of the composite oxidant produced by the present invention to dyeing waste water has excellent effect, and COD removal rates are more than 90%, and chroma removal rate is more than 96%.
Description
Technical field
The present invention relates to technical field of waste water processing, more particularly to a kind of composite oxidant and preparation method thereof.
Background technology
With deepening continuously for process of industrialization, global environmental pollution increasingly destroys global biosphere institute over several hundred million years
The ecological balance of formation, and constitute a threat to the living environment of mankind itself.It is dirty to China's water environment according to State Environmental Protection Administration
The statistics and investigation, rivers, lake and the coastal waters basin in China for contaminating present situation are generally subject to different degrees of pollution, are generally in
The trend now aggravated, the principal element for polluting exacerbation are industrial wastewater and sanitary sewage.
Textile and dyeing industry discharges substantial amounts of waste water and waste residue in process of production to produce pollution to environment, wherein with print
Pollution of the waste water discharged during dye industry production to environment is the most serious.According to incompletely statistics, national dyeing waste water is daily
Discharge capacity is (3-4) × 106m3, the 35% of national industrial wastewater total release is accounted for, and increase year by year with 1% speed.Discharge
Entrainment in waste water containing fibrous raw material in itself, and process slurry, finish, dyestuff and chemical assistant for using etc.,
There is biochemical oxygen demand (BOD) height, colourity height, pH value height, difficult for biological degradation, diverse " a three high hardly possiblies one become ".It is residual in waste water
The dye component deposited, even if concentration is very low, is discharged into the reduction that water body will also result in gas solubility in water body light transmittance and water body,
Various biological growths in water can be influenced, so as to destroy the food chain of water body purity and aquatile, most cause water body to be given birth at last
The destruction of state system.Therefore, the governing problem of printing and dyeing industrial waste water, it has also become Now Domestic external environment engineering circles are badly in need of what is solved
A great problem.
Dyeing produces a large amount of dyeing waste waters every year, is extremely difficult to one of the industrial wastewater of processing.Conventional water process medicine
Agent has been unable to meet process demand, must research and develop the water treatment agent of new high-efficiency for this.
The content of the invention
Based on technical problem existing for background technology, the present invention, which proposes, provides a kind of composite oxidant, can effectively remove
Difficult organics removal in dyeing waste water, Product Green environmental protection, will not cause secondary pollution to environment.
A kind of composite oxidant, including following component in parts by weight:5-10 parts of metal chloride, silicate 3-25
Part, 20-35 parts of ferrate, 12-25 parts of organic solvent, 10-20 parts of chelating agent, 15-25 parts of potassium permanganate, deionized water 30-
50 parts.
Preferably, the metal chloride is copper chloride, iron chloride or zinc chloride.
Preferably, the metal chloride is copper chloride.
Preferably, the silicate is sodium metasilicate.
Preferably, the ferrate is potassium ferrate or Na2Fe04.
Preferably, the organic solvent is ethylene glycol.
Preferably, the chelating agent is ethylenediamine tetra-acetic acid.
A kind of preparation method of composite oxidant, method and step are as follows:S1:Deionized water is added in reaction kettle, stirring
And 42-48 DEG C is warming up to, metal chloride and silicate are added, stirs 20min;S2:The solution of S1 is cooled to 30 DEG C, is added
Ferrate, stirs 20min;S3:Organic solvent is added into S2, stirs 10min;S4:The solution of S3 is warming up to 57-63
DEG C, chelating agent is added, stirs 30min;S5:The solution of S4 is cooled to 27-33 DEG C, adds potassium permanganate, stirs 20min, i.e.,
.
A kind of composite oxidant proposed by the present invention is applied to the processing of dyeing waste water.
Compared with prior art, the device have the advantages that being:
In the present invention, the stability of ferrate, second two can be improved under the collective effect of metal chloride and silicate
Amine tetraacethyl can form stable iron ion chelate as chelating agent, then can form oxidisability with potassium permanganate collective effect
Stronger composite oxidant.Composite oxidant produced by the present invention can effectively remove print by a variety of effects such as ion exchange
It is difficult to the organic matter removed in dye waste water;In addition the oxidant is easy to dissolve, and performance is stablized, and odorlessness during dissolving, will not produce
Toxic gas, the experiment proved that:Processing of the composite oxidant produced by the present invention to dyeing waste water has excellent effect, COD
Removal rate is more than 90%, and chroma removal rate is more than 96%.
Embodiment
The present invention is made with reference to specific embodiment further to explain.
Embodiment 1
A kind of composite oxidant, including following component in parts by weight:5 parts of copper chloride, 3 parts of sodium metasilicate, ferric acid
20 parts of potassium, 12 parts of ethylene glycol, 10 parts of ethylenediamine tetra-acetic acid, 15 parts of potassium permanganate, 30 parts of deionized water.
A kind of preparation method of composite oxidant, method and step are as follows:
S1:Deionized water is added in reaction kettle, stirs and is warming up to 42 DEG C, adds copper chloride and sodium metasilicate, stirring
20min;S2:The solution of S1 is cooled to 30 DEG C, adds potassium ferrate, stirs 20min;S3:Ethylene glycol is added into S2, is stirred
10min;S4:The solution of S3 is warming up to 57 DEG C, adds ethylenediamine tetra-acetic acid, stirs 30min;S5:The solution of S4 is cooled to
27 DEG C, add potassium permanganate, stir 20min, to obtain the final product.
Embodiment 2
A kind of composite oxidant, including following component in parts by weight:8 parts of copper chloride, 5 parts of sodium metasilicate, ferric acid
28 parts of sodium, 20 parts of ethylene glycol, 15 parts of ethylenediamine tetra-acetic acid, 20 parts of potassium permanganate, 40 parts of deionized water.
A kind of preparation method of composite oxidant, method and step are as follows:
S1:Deionized water is added in reaction kettle, stirs and is warming up to 45 DEG C, adds copper chloride and sodium metasilicate, stirring
20min;S2:The solution of S1 is cooled to 30 DEG C, adds Na2Fe04, stirs 20min;S3:Ethylene glycol is added into S2, is stirred
10min;S4:The solution of S3 is warming up to 60 DEG C, adds ethylenediamine tetra-acetic acid, stirs 30min;S5:The solution of S4 is cooled to
30 DEG C, add potassium permanganate, stir 20min, to obtain the final product.
Embodiment 3
A kind of composite oxidant, including following component in parts by weight:10 parts of copper chloride, 25 parts of sodium metasilicate, high ferro
Sour 35 parts of potassium, 25 parts of ethylene glycol, 20 parts of ethylenediamine tetra-acetic acid, 25 parts of potassium permanganate, 50 parts of deionized water.
A kind of preparation method of composite oxidant, method and step are as follows:
S1:Deionized water is added in reaction kettle, stirs and is warming up to 48 DEG C, adds copper chloride and sodium metasilicate, stirring
20min;S2:The solution of S1 is cooled to 30 DEG C, adds potassium ferrate, stirs 20min;S3:Ethylene glycol is added into S2, is stirred
10min;S4:The solution of S3 is warming up to 63 DEG C, adds ethylenediamine tetra-acetic acid, stirs 30min;S5:The solution of S4 is cooled to
33 DEG C, add potassium permanganate, stir 20min, to obtain the final product.
Embodiment 4
A kind of composite oxidant, including following component in parts by weight:7 parts of iron chloride, 10 parts of sodium metasilicate, ferric acid
32 parts of potassium, 22 parts of ethylene glycol, 13 parts of ethylenediamine tetra-acetic acid, 17 parts of potassium permanganate, 45 parts of deionized water.
A kind of preparation method of composite oxidant, method and step are as follows:
S1:Deionized water is added in reaction kettle, stirs and is warming up to 46 DEG C, adds iron chloride and sodium metasilicate, stirring
20min;S2:The solution of S1 is cooled to 30 DEG C, adds potassium ferrate, stirs 20min;S3:Ethylene glycol is added into S2, is stirred
10min;S4:The solution of S3 is warming up to 62 DEG C, adds ethylenediamine tetra-acetic acid, stirs 30min;S5:The solution of S4 is cooled to
31 DEG C, add potassium permanganate, stir 20min, to obtain the final product.
Embodiment 5
A kind of composite oxidant, including following component in parts by weight:6 parts of zinc chloride, 20 parts of sodium metasilicate, ferric acid
25 parts of potassium, 16 parts of ethylene glycol, 18 parts of ethylenediamine tetra-acetic acid, 23 parts of potassium permanganate, 35 parts of deionized water.
A kind of preparation method of composite oxidant, method and step are as follows:
S1:Deionized water is added in reaction kettle, stirs and is warming up to 43 DEG C, adds zinc chloride and sodium metasilicate, stirring
20min;S2:The solution of S1 is cooled to 30 DEG C, adds potassium ferrate, stirs 20min;S3:Ethylene glycol is added into S2, is stirred
10min;S4:The solution of S3 is warming up to 58 DEG C, adds ethylenediamine tetra-acetic acid, stirs 30min;S5:The solution of S4 is cooled to
29 DEG C, add potassium permanganate, stir 20min, to obtain the final product.
Properties of product detect
Certain printing and dyeing mill's dyeing waste water is dark brown, belongs to serious pollution sewage, and smell is pungent, and has stink, pH 6.7, COD are
15320mg/L, colourity are 1600 times;Product field test results are as follows:
1 test result of table
Product | Color | COD(mg/L) | Colourity (again) | COD removal rates (%) | Chroma removal rate (%) |
Dyeing waste water | Dark brown is opaque | 15320 | 1600 | / | / |
Embodiment 1 | It is transparent | 1360 | 60 | 91.12 | 96.25 |
Embodiment 2 | It is transparent | 1280 | 50 | 91.64 | 96.88 |
Embodiment 3 | It is transparent | 1420 | 60 | 90.73 | 96.15 |
Embodiment 4 | It is transparent | 1320 | 60 | 91.22 | 96.37 |
Embodiment 5 | It is transparent | 1310 | 50 | 90.89 | 96.61 |
It the experiment proved that, processing of the composite oxidant produced by the present invention to dyeing waste water has excellent effect, and COD is gone
Except rate is more than 90%, chroma removal rate is more than 96%.
The foregoing is only a preferred embodiment of the present invention, but protection scope of the present invention be not limited thereto,
Any one skilled in the art the invention discloses technical scope in, technique according to the invention scheme and its
Inventive concept is subject to equivalent substitution or change, should be covered by the protection scope of the present invention.
Claims (9)
1. a kind of composite oxidant, it is characterised in that including following component by weight:5-10 parts of metal chloride, silicon
3-25 parts of hydrochlorate, 20-35 parts of ferrate, 12-25 parts of organic solvent, 10-20 parts of chelating agent, 15-25 parts of potassium permanganate, go from
Sub- water 30-50 parts.
2. a kind of composite oxidant according to claim 1, it is characterised in that the metal chloride is copper chloride, chlorine
Change iron or zinc chloride.
3. a kind of composite oxidant according to claim 2, it is characterised in that the metal chloride is copper chloride.
4. a kind of composite oxidant according to claim 1, it is characterised in that the silicate is sodium metasilicate.
5. a kind of composite oxidant according to claim 1, it is characterised in that the ferrate is potassium ferrate or height
Sodium ferrite.
6. a kind of composite oxidant according to claim 1, it is characterised in that the organic solvent is ethylene glycol.
7. a kind of composite oxidant according to claim 1, it is characterised in that the chelating agent is ethylenediamine tetra-acetic acid.
8. according to a kind of preparation method of composite oxidant of claim 1-7 any one of them, it is characterised in that method and step
It is as follows:S1:Deionized water is added in reaction kettle, stirs and is warming up to 42-48 DEG C, metal chloride and silicate is added, stirs
Mix 20min;S2:The solution of S1 is cooled to 30 DEG C, adds ferrate, stirs 20min;S3:Organic solvent is added into S2,
Stir 10min;S4:The solution of S3 is warming up to 57-63 DEG C, adds chelating agent, stirs 30min;S5:The solution of S4 is cooled to
27-33 DEG C, add potassium permanganate, stir 20min, to obtain the final product.
9. it is applied to the processing of dyeing waste water according to a kind of composite oxidant of claim 1-7 any one of them.
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CN201711084893.2A CN107902744A (en) | 2017-11-07 | 2017-11-07 | A kind of composite oxidant and preparation method thereof |
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CN201711084893.2A CN107902744A (en) | 2017-11-07 | 2017-11-07 | A kind of composite oxidant and preparation method thereof |
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Citations (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPS4869359A (en) * | 1971-12-23 | 1973-09-20 | ||
CN102515327A (en) * | 2011-12-28 | 2012-06-27 | 樊继健 | Composite water treatment agent, and preparation method thereof |
CN103449528A (en) * | 2013-08-09 | 2013-12-18 | 华南理工大学 | Method for preparing ferrate through ultrasonic activation |
-
2017
- 2017-11-07 CN CN201711084893.2A patent/CN107902744A/en active Pending
Patent Citations (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPS4869359A (en) * | 1971-12-23 | 1973-09-20 | ||
CN102515327A (en) * | 2011-12-28 | 2012-06-27 | 樊继健 | Composite water treatment agent, and preparation method thereof |
CN103449528A (en) * | 2013-08-09 | 2013-12-18 | 华南理工大学 | Method for preparing ferrate through ultrasonic activation |
Non-Patent Citations (1)
Title |
---|
金士威等: ""腐殖酸与EDTA 对高铁酸钾降解水中孔雀石绿影响的研究"", 《湖北农业科学》 * |
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Address after: 1202, Dachong building, No. 2009, Shahe West Road, Dachong community, Yuehai street, Nanshan District, Shenzhen City, Guangdong Province Applicant after: Shenzhen Delan ecological environment Co.,Ltd. Address before: The 830002 the Xinjiang Uygur Autonomous Region Urumqi high tech Industrial Development Zone (new city) north Dongrong Street No. 567 building eleven floor, South Tower of high-tech talent Applicant before: XINJIANG ENVIRONMENTAL ENGINEERING TECHNOLOGY Co.,Ltd. |
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Application publication date: 20180413 |