CN105936560A - Method for degrading sewage based on dye photooxidation and visible light catalytic oxidation - Google Patents

Method for degrading sewage based on dye photooxidation and visible light catalytic oxidation Download PDF

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Publication number
CN105936560A
CN105936560A CN201610349824.9A CN201610349824A CN105936560A CN 105936560 A CN105936560 A CN 105936560A CN 201610349824 A CN201610349824 A CN 201610349824A CN 105936560 A CN105936560 A CN 105936560A
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CN
China
Prior art keywords
sewage
photooxidation
visible light
dye
catalytic oxidation
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.)
Pending
Application number
CN201610349824.9A
Other languages
Chinese (zh)
Inventor
张宁迁
鲍习舟
石凯元
石磊
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Anhui Pu Shi Ecological Environment Engineering Co Ltd
Original Assignee
Anhui Pu Shi Ecological Environment Engineering Co Ltd
Priority date (The priority date 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 date listed.)
Filing date
Publication date
Application filed by Anhui Pu Shi Ecological Environment Engineering Co Ltd filed Critical Anhui Pu Shi Ecological Environment Engineering Co Ltd
Priority to CN201610349824.9A priority Critical patent/CN105936560A/en
Publication of CN105936560A publication Critical patent/CN105936560A/en
Pending legal-status Critical Current

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Classifications

    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F9/00Multistage treatment of water, waste water or sewage
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/001Processes for the treatment of water whereby the filtration technique is of importance
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/30Treatment of water, waste water, or sewage by irradiation
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/72Treatment of water, waste water, or sewage by oxidation
    • C02F1/725Treatment of water, waste water, or sewage by oxidation by catalytic oxidation
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/30Organic compounds
    • C02F2101/308Dyes; Colorants; Fluorescent agents
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2305/00Use of specific compounds during water treatment
    • C02F2305/02Specific form of oxidant
    • C02F2305/023Reactive oxygen species, singlet oxygen, OH radical
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2305/00Use of specific compounds during water treatment
    • C02F2305/10Photocatalysts
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W10/00Technologies for wastewater treatment
    • Y02W10/30Wastewater or sewage treatment systems using renewable energies
    • Y02W10/37Wastewater or sewage treatment systems using renewable energies using solar energy

Abstract

The invention discloses a method for degrading sewage based on dye photooxidation and visible light catalytic oxidation. The method comprises the following steps: 1, pumping sewage to a sewage treatment pool, and mechanically stirring the sewage to uniformly disperse all phases in the sewage; 2, adding 0.1g of a dye photooxidation catalyst to every liter of the sewage; 3, using visible light to irritate the sewage treatment pool, and stirring and reacting the sewage for 5h; and 4, standing the sewage after the reaction ends, and filtering the sewage through a filtering device. Compared with the prior art, the method disclosed in the invention has the following advantages: 1, the treated sewage can be directly discharged or biologically purified; and 2, the filtered dye photooxidation catalyst can be recycled after being recovered.

Description

A kind of method of sewage of degrading based on dyestuff photooxidation and visible light catalytic oxidation
Technical field
The present invention relates to sewage treatment area, a kind of method being specifically related to sewage of degrading based on dyestuff photooxidation and visible light catalytic oxidation.
Background technology
In Chinese Urbanization scale constantly extends the process improved constantly with industrialization degree, substantial amounts of reluctant trade effluent and sanitary sewage can be produced, the major pollutants that sewage is contained within include organic pollutants, aerobic or anaerobism pollutant, plant pollution thing, toxic pollutant and radioactive contaminant, etc., water quality is complicated, toxicity is big, ammonia nitrogen, COD (COD) comparision contents are high, therefore, how to process trade effluent, make it meet the requirement of environmental protection, be just particularly important.
Owing to above-mentioned sewage usually containing substantial amounts of organic macromolecule material, graininess or dust-like material; in prior art; when organic macromolecule material, graininess or the dust-like material processed in above-mentioned sewage; oxidant, catalyst, flocculant or flocculation aid would generally be added in sewage; by the chemical reaction within mixed material, remove organic macromolecule material, graininess or dust-like material.
The chemical reaction of mixed material is the most abundant, depends on the uniformity coefficient that mixed material mixes, and mixed material mixing is the most uniform, and chemical reaction will be the most abundant, thus scrubbing clean-up effect is the best;In prior art, generally using stirring for a long time to come combined sewage, mud and oxidant, catalyst and flocculant, but use said method, mixed material can not be made to reach molecule, being sufficiently mixed of ion level, this will affect the treatment effect of sewage.Traditional chemical physical method has the disadvantages that and generally uses substantial amounts of hydrogen peroxide as Strong oxdiative source, it is provided that active oxygen atom i.e. hydroxyl radical free radical (OH), owing to hydrogen peroxide price is higher, this will be greatly improved the cost of sewage disposal.And, sewage can not be sufficiently mixed with oxidant, catalyst or flocculant, so that the organic macromolecule material in sewage fully can not react with oxidant, catalyst or flocculant, and this effect that cannot reach thoroughly to purify sewage.By using additional light source to be irradiated being allowed to occur chemical oxidation to be referred to as photocatalytic oxidation in the presence of a catalyst to sewage.In existing photochemical catalytic oxidation system, generally individually using ultraviolet light and irradiate, but the required higher quantum yield of energy requirement of reaction is low, reaction rate is the highest.
Summary of the invention
The invention aims to overcome the deficiencies in the prior art, it is provided that a kind of method based on dyestuff photooxidation and visible light catalytic oxidation degraded sewage solves the problems referred to above.
For solving above-mentioned technical problem, the technical scheme is that
A kind of method of sewage of degrading based on dyestuff photooxidation and visible light catalytic oxidation, comprises the following steps:
A. by sewage suction treatment tank, being respectively uniformly dispersed mutually in sewage is made by mechanical agitation;
B. dyestuff photooxidation catalyst is added according to the metering of every liter of sewage 0.1g;
C. radiation of visible light treatment tank, stirring reaction treatment 5 hours are used;
D. stand after reaction terminates, filtered by filtering device.
Preferably, the visible ray described in step C is 1000WALED white light or sunlight.
Compared with prior art, the invention have the benefit that 1) process after sewage can be in line or carry out biological cleaning;2) the dyestuff photooxidation catalyst recycling Posterior circle after filtering uses.
Detailed description of the invention
By making the architectural feature to the present invention and effect of being reached have a better understanding and awareness, describe in detail in order to preferred embodiment, be described as follows:
A kind of method of sewage of degrading based on dyestuff photooxidation and visible light catalytic oxidation, comprises the following steps: A., by sewage suction treatment tank, makes being respectively uniformly dispersed mutually in sewage by mechanical agitation;B. dyestuff photooxidation catalyst is added according to the metering of every liter of sewage 0.1g;C. radiation of visible light treatment tank, stirring reaction treatment 5 hours are used;D. stand after reaction terminates, filtered by filtering device.Visible ray described in step C is 1000WALED white light or sunlight.
Dyestuff photooxidation catalyst used in the present invention is Eosin-1 dyestuff photooxidation catalyst, and this catalyst is made up of following component: mass fraction is the Kaolin of 20 ~ 30 parts, the montmorillonite of 20 ~ 40 parts, the aluminum lime-ash of 20 ~ 40 parts, the eosin W or W S of 15 ~ 40 parts, the Eosin B of 20 ~ 30 parts, the diiodocosin of 25 ~ 40 parts, the sodium silicate of 20 ~ 30 parts, the sodium aluminate of 20 ~ 30 parts.The preparation method of the Eosin-1 dyestuff photooxidation catalyst of the present invention, comprises the following steps: A. uses hydro-thermal method, each component is added to the water, and stirring forms each mutually homodisperse solution;B. by each mutually homodisperse solution heating described in step A, brilliant China postprecipitation, then calcine.
The Eosin-1 dyestuff photooxidation catalyst that the present invention uses is in visible light source such as LED, generation free radical is excited under electric filament lamp or sunlight, and then the Organic substance generation photooxidation reaction degraded in promotion sewage, relative to ultraviolet light, visible light source is more prone to obtain and operation, and the eosin in Eosin-1 dyestuff photooxidation catalyst is the organic dyestuff photosensitizer that a class is ripe, cheap and easily-available, this photooxidation system is with a wide range of applications.
The ultimate principle of the present invention, principal character and advantages of the present invention have more than been shown and described.Skilled person will appreciate that of the industry; the present invention is not restricted to the described embodiments; the principle of the simply present invention described in above-described embodiment and description; the present invention also has various changes and modifications without departing from the spirit and scope of the present invention, and these changes and improvements both fall within the range of claimed invention.The protection domain of application claims is defined by appending claims and equivalent thereof.

Claims (2)

1. the method for a sewage of degrading based on dyestuff photooxidation and visible light catalytic oxidation, it is characterised in that comprise the following steps:
A. by sewage suction treatment tank, being respectively uniformly dispersed mutually in sewage is made by mechanical agitation;
B. dyestuff photooxidation catalyst is added according to the metering of every liter of sewage 0.1g;
C. radiation of visible light treatment tank, stirring reaction treatment 5 hours are used;
D. stand after reaction terminates, filtered by filtering device.
The method of a kind of sewage of degrading based on dyestuff photooxidation and visible light catalytic oxidation the most according to claim 1, it is characterised in that the visible ray described in step C is 1000WALED white light or sunlight.
CN201610349824.9A 2016-05-24 2016-05-24 Method for degrading sewage based on dye photooxidation and visible light catalytic oxidation Pending CN105936560A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201610349824.9A CN105936560A (en) 2016-05-24 2016-05-24 Method for degrading sewage based on dye photooxidation and visible light catalytic oxidation

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201610349824.9A CN105936560A (en) 2016-05-24 2016-05-24 Method for degrading sewage based on dye photooxidation and visible light catalytic oxidation

Publications (1)

Publication Number Publication Date
CN105936560A true CN105936560A (en) 2016-09-14

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CN201610349824.9A Pending CN105936560A (en) 2016-05-24 2016-05-24 Method for degrading sewage based on dye photooxidation and visible light catalytic oxidation

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Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN106076394A (en) * 2016-06-02 2016-11-09 安徽普氏生态环境工程有限公司 A kind of zeolite-loaded dyestuff photooxidation sewage disposal catalyst Eosin 1
CN115385415A (en) * 2022-07-07 2022-11-25 江苏理工学院 Method for degrading organic wastewater by using waste to treat waste

Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1289776A (en) * 1999-09-24 2001-04-04 中国科学院化学研究所 Composite photosensing agnet of eosin-dipyridine ruthonium and its synthesis process and application
CN101519256A (en) * 2009-04-10 2009-09-02 南京大学 Application of sodium bismuthate in rapidly degrading organic dye waste water and degradation method
CN103523897A (en) * 2013-10-31 2014-01-22 哈尔滨工业大学 Water treatment compound agent for removing organic pollutants in oxidation mode with high-activity singlet oxygen and water treatment method thereof

Patent Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1289776A (en) * 1999-09-24 2001-04-04 中国科学院化学研究所 Composite photosensing agnet of eosin-dipyridine ruthonium and its synthesis process and application
CN101519256A (en) * 2009-04-10 2009-09-02 南京大学 Application of sodium bismuthate in rapidly degrading organic dye waste water and degradation method
CN103523897A (en) * 2013-10-31 2014-01-22 哈尔滨工业大学 Water treatment compound agent for removing organic pollutants in oxidation mode with high-activity singlet oxygen and water treatment method thereof

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN106076394A (en) * 2016-06-02 2016-11-09 安徽普氏生态环境工程有限公司 A kind of zeolite-loaded dyestuff photooxidation sewage disposal catalyst Eosin 1
CN115385415A (en) * 2022-07-07 2022-11-25 江苏理工学院 Method for degrading organic wastewater by using waste to treat waste
CN115385415B (en) * 2022-07-07 2023-11-10 江苏理工学院 Method for treating waste and degrading organic waste water by waste

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Application publication date: 20160914

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