CN108249510A - A kind of method based on light conversion material processing water body organic contamination - Google Patents

A kind of method based on light conversion material processing water body organic contamination Download PDF

Info

Publication number
CN108249510A
CN108249510A CN201711259325.1A CN201711259325A CN108249510A CN 108249510 A CN108249510 A CN 108249510A CN 201711259325 A CN201711259325 A CN 201711259325A CN 108249510 A CN108249510 A CN 108249510A
Authority
CN
China
Prior art keywords
light
water body
conversion material
organic contamination
energy
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
CN201711259325.1A
Other languages
Chinese (zh)
Inventor
林青
李玲玲
陈文远
张爽
张丁雨
邱佳琳
王磊
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.)
Jinling Institute of Technology
Original Assignee
Jinling Institute of Technology
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 Jinling Institute of Technology filed Critical Jinling Institute of Technology
Priority to CN201711259325.1A priority Critical patent/CN108249510A/en
Publication of CN108249510A publication Critical patent/CN108249510A/en
Pending legal-status Critical Current

Links

Classifications

    • 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
    • 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

Abstract

The invention discloses a kind of methods based on light conversion material processing water body organic contamination:Solar energy is converted by electric energy by photoelectric conversion material, driving electroluminescent material shines, and so as to generate the light of specific wavelength, irradiates catalysis material, and photocatalytic effect occurs, and degradable organic pollutant purifies water source.The present invention is directed to photocatalysis oxidation technique, efficiently use light source of solar energy, dexterously photovoltaic material, electroluminescent material and catalysis material are organically combined and used, realize the purpose that high efficiency of energy recycles, and all energy are all from sunlight, the efficiency of photocatalysis treatment organic contamination is improved, it is environmentally protective.

Description

A kind of method based on light conversion material processing water body organic contamination
Technical field
The present invention relates to a kind of methods for handling water body organic contamination, particularly relate to efficiently sharp based on light conversion material The method that water body organic contamination is handled with solar energy source, suitable for the purified treatment of industrial wastewater and city domestic sewage.
Background technology
China's water resource quality constantly declines, and water environment is continuous worsening, and the water shortage and accident caused by pollution are continuous Occur, plant downtime, the agriculture underproduction is not only made even to have no harvest, but also cause undesirable social influence and larger economic damage It loses, has seriously threatened the sustainable development of society, threatened the existence of the mankind." blue montains and green waters is exactly Kingsoft Yin Shan ", energetically Carry out sewage treatment works, build good ecological environment, strengthen the improvement of water pollution, strengthen the protection of ecological environment, be both Meet the current needs of people's survival and development and realize the key of Sustainable Development in Future.
The method of processing water body organic contamination has Physical, ordinary chemical method, bioanalysis etc., but there are costs for these methods Height, effect unobvious, technical difficulty are big, secondary pollution problems.
Physical is the dirt that state, colloidal attitude and super colloidal attitude can be settled with the physical principles processing such as precipitation, filtering, absorption Object is contaminated, and is difficult to remove the organic pollution of solubilised state.Such as patent CN 881000597, using quartz sand, zeolite or haydite For equigranular inert material as sorbing material, these sorbing materials have the treatment effect identical with activated carbon, but this method It is unsatisfactory for the treatment effect of toxic, bio-refractory micro quantity organic pollutant.Patent CN 105366759 is utilized X-ray or gamma-radiation, preferably rhodamine B degradation sample, but there is ray preparation difficulty, Radiation On Human body are harmful It is insufficient.
Ordinary chemical method is by reacting decomposing organic pollutant between compound, so needing in addition to system additionization Reagent is learned, for micro, trace contamination system, introduces new pollution sources instead.
The structure of bioanalysis, that is, model ecosystem, to the method that the biology in food chain carries out reasonable disposition, but because of it Engineering is complicated, technical strong, it is difficult to implement.
Photocatalysis oxidation technique is the new technology for handling water body organic contamination, has huge research in field of sewage treatment And application value.Photocatalysis oxidation technique be to generate based on oxyradical, it made to be reacted with larger molecular organics, so as to Organic molecular structure is destroyed, until being decomposed into carbon dioxide and water.Promote photocatalytic effect, it is necessary first to specific purple Outer light irradiation., can be directly using the ultraviolet light in sunlight from the point of view of tradition is using energy mode, but wherein contain specific purple Outer light is less, and is vulnerable to the influence of climatic environment, causes catalytic efficiency very low;It is directly irradiated, produced using ultraviolet lamp Raw electric energy consuming is very big, and cost is very high.
Patent CN 105084514, directly by the use of mercury lamp or ultraviolet radiator as photocatalysis light source, though it can effectively obtain institute Ultraviolet light is needed, but capacity usage ratio is low, high energy consumption is of high cost, is unfavorable for extensive use.Patent CN 104923072, passes through gas Liquid-solid mixture hits ultraviolet lamp, though the ultraviolet light of effective wavelength can be obtained, its effect easily can be by mixture concentration, temperature Influence, operation it is more complicated, be also relatively difficult to apply.
It is well known that solar energy is the energy of most original, nearly all energy is all directly or indirectly from too on the earth It is positive can, and solar energy contain it is abundant will not be exhausted, safety will not totally threaten the mankind and welding.Such as patent CN 103097284, photochemical catalyst is irradiated by conductive isolation layer using sunlight, photocatalytic effect occurs, although the device can reach To the purpose for efficiently using solar energy, but it obtains the approach complexity of solar energy, and the sun loss of energy is larger.
Enough sunlights are converted into electric energy first with photovoltaic material and stored by the present invention, reuse electrical energy drive electricity Electroluminescent material generates the light source of the specific wavelength needed for catalysis material, organic using the driving catalysis material degradation of this light source Pollutant.
Photovoltaic material, electroluminescent material and catalysis material used in the method for the present invention belong to light conversion material, energy It realizes the efficient utilization of the energy, improves the efficiency of photocatalysis treatment organic contamination, be that a kind of light conversion material that is based on handles water body The method of organic contamination, environmental protection easy to operate.
Invention content
The purpose of the present invention is providing clean energy resource for photocatalysis oxidation technique, the energy profit of photocatalysis oxidation technique is improved With rate, the efficiency of photocatalysis treatment organic contamination is improved.In order to realize goal of the invention, converted the present invention provides one kind based on light The method of material processing water body organic contamination, includes the following steps:
Step 1:Solar energy is converted by electric energy by photoelectric conversion material;
Step 2:Electrical energy drive electroluminescent material generates the light of specific wavelength;
Step 3:The light irradiation catalysis material of specific wavelength, occurs photocatalytic effect, degradable organic pollutant.
Wherein, the photoelectric conversion material be photovoltaic material, including crystal silicon solar batteries, polysilicon solar cell, Non-crystal silicon solar cell and multi-element compounds solar cell material.
The electroluminescent material is Light-emitting diode LED, main two poles included using gallium nitride GaN based semiconductors Pipe.
The catalysis material is titanium dioxide, zinc oxide, zirconium dioxide, cadmium sulfide, including doped metal ion, non-gold Belong to ion.
The present invention is applied to the organic pollution in processing water body.
Electroluminescent material selects light emitting diode (LED), and compared to general light emitting device, the light sent out is certain wave Long light acts required special wavelength light closer to catalysis material.
Advantageous effect acquired by the present invention:
(1) compared with prior art, the present invention efficiently uses light source of solar energy, dexterously for photocatalysis oxidation technique Photovoltaic material, electroluminescent material and catalysis material are organically combined and used, realizes the mesh that high efficiency of energy recycles 's;
(2) all energy are all from sunlight, improve the efficiency of photocatalysis treatment organic contamination, environmentally protective.
Description of the drawings
Fig. 1 is the degradation curve of the lower rhodamine B of different light sources irradiation of equal-wattage:(a) LED source;(b) General ultraviolet lamp source.
Specific embodiment
The present invention will be further described with reference to embodiments, but following embodiments have no protection scope of the present invention Clearly limit.
Embodiment 1
The water body of the rhodamine B solution simulation organic contamination of two parts of a concentration of 20mg/L of 50ml is taken respectively, is respectively put into The catalysis material (Zinc oxide powder, ZnO) of 50mg, a light emitting diode using launch wavelength as 370nm are light source (work( Rate is 60W) irradiation sewage, another irradiates sewage by light source (power 60W) of common uv lamp.In reaction process uniformly RB solution is stirred, is sampled every 30min, finally measures rhodamine B concentration in solution, meter using ultra-violet and visible spectrophotometer It calculates and to draw rhodamine B degradation rate curve graph as shown in Figure 1.
Rhodamine B in the lower solution of LED source (a) and general ultraviolet lamp source (b) irradiation of Fig. 1 equal-wattages Degradation curve, as can be seen from the figure under the irradiation of the LED source of specific wavelength, rhodamine B concentration in solution It is remarkably decreased.Therefore, it can effectively be improved using the light source (370nm) of catalysis material (Zinc oxide powder) specific absorption wavelength Light-catalysed efficiency has higher efficiency of energy utilization.
Embodiment 2
The water body of the rhodamine B solution simulation organic contamination of two parts of a concentration of 20mg/L of 50ml is taken respectively, is respectively put into Catalysis material (titanium dioxide powder, the TiO of 50mg2).By 1m2Sunlight is converged in the container equipped with rhodamine B solution and (is opened Mouth diameter 4cm), portion irradiates 2 hours under this illumination, another first uses area 1m2Photovoltaic material (mono-crystalline silicon solar Solar panel) constant absorption sunlight 2 hours, it converts light into as electricity, then drive the light emitting diode that launch wavelength is 380nm (60W) irradiates.Uniform stirring rhodamine B solution in reaction process, after, it is tested using ultra-violet and visible spectrophotometer molten Liquid remnants rhodamine B percentage compositions.
The result shows that the residual content of sunlight direct irradiation rhodamine B after 2 hours is 80.5%;Illumination in 2 hours is converted into Electric energy, then drive lumination of light emitting diode irradiate sample in rhodamine B residual content be 68.5%.The result shows that utilize light Converting material can effectively improve the efficiency that light-catalyzed reaction utilizes sunlight.
Embodiment 3
The methyl orange solution of a concentration of 20mg/L of a 50ml is taken to simulate the water body of organic contamination, is put into 100mg photocatalysis Material (Zinc oxide powder, ZnO).Using area 1m2Photovoltaic material absorb sunlight, convert light into as electricity, then drive transmitting Light emitting diode (60W) of the wavelength for 365nm, prolonged exposure water body.Methyl orange solution is at the uniform velocity stirred in reaction process, urges light Change the pollutant that material comes into full contact with simulation, photocatalytic effect occurs, sewage of degrading.
The result shows that the degradation rate of methyl orange solution is 95.28% after 4 hours.
Embodiment is only the description of the invention, and the application realized using the thinking of the present invention belongs to the protection of the present invention Range.

Claims (4)

1. a kind of method based on light conversion material processing water body organic contamination, includes the following steps:
Step 1:Solar energy is converted by electric energy by photoelectric conversion material;
Step 2:Electrical energy drive electroluminescent material generates the light of specific wavelength;
Step 3:The light irradiation catalysis material of specific wavelength, occurs photocatalytic effect, degradable organic pollutant.
2. a kind of method based on light conversion material processing water body organic contamination according to claim 1, it is characterised in that:Institute Photoelectric conversion material is stated as photovoltaic material, including crystal silicon solar batteries, polysilicon solar cell, non-crystal silicon solar cell And multi-element compounds solar cell material.
3. a kind of method based on light conversion material processing water body organic contamination according to claim 1, it is characterised in that:Institute Electroluminescent material is stated as Light-emitting diode LED, the main diode included using gallium nitride GaN based semiconductors.
A kind of 4. method based on light conversion material processing water body organic contamination according to claim 1, it is characterised in that institute Catalysis material is stated as titanium dioxide, zinc oxide, zirconium dioxide, cadmium sulfide, including doped metal ion, nonmetallic ion.
CN201711259325.1A 2017-12-04 2017-12-04 A kind of method based on light conversion material processing water body organic contamination Pending CN108249510A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201711259325.1A CN108249510A (en) 2017-12-04 2017-12-04 A kind of method based on light conversion material processing water body organic contamination

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201711259325.1A CN108249510A (en) 2017-12-04 2017-12-04 A kind of method based on light conversion material processing water body organic contamination

Publications (1)

Publication Number Publication Date
CN108249510A true CN108249510A (en) 2018-07-06

Family

ID=62722385

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201711259325.1A Pending CN108249510A (en) 2017-12-04 2017-12-04 A kind of method based on light conversion material processing water body organic contamination

Country Status (1)

Country Link
CN (1) CN108249510A (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN108996600A (en) * 2018-07-26 2018-12-14 中原工学院 Utilize the method for solar battery waste material regulation creek black and odorous water

Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO1992008768A1 (en) * 1989-09-25 1992-05-29 Board Of Regents, The University Of Texas System Materials and methods for photocatalyzing oxidation of organic compounds on water
CN1506155A (en) * 2002-12-06 2004-06-23 中国科学院化学研究所 Photocatalytic method to titania with LED as light source
CN2649577Y (en) * 2003-06-27 2004-10-20 长春环能科技有限公司 Solar photocatalytic organic waste water treating device
CN102603037A (en) * 2012-04-01 2012-07-25 南京工业大学 Organic wastewater treatment film reactor utilizing sunlight-assisted electro-catalysis

Patent Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO1992008768A1 (en) * 1989-09-25 1992-05-29 Board Of Regents, The University Of Texas System Materials and methods for photocatalyzing oxidation of organic compounds on water
CN1506155A (en) * 2002-12-06 2004-06-23 中国科学院化学研究所 Photocatalytic method to titania with LED as light source
CN2649577Y (en) * 2003-06-27 2004-10-20 长春环能科技有限公司 Solar photocatalytic organic waste water treating device
CN102603037A (en) * 2012-04-01 2012-07-25 南京工业大学 Organic wastewater treatment film reactor utilizing sunlight-assisted electro-catalysis

Non-Patent Citations (2)

* Cited by examiner, † Cited by third party
Title
刘华忠: "《第一性原理计算 TiO2表面》", 31 May 2017, 西安交通大学出版社 *
张媛: "《低频电子电路》", 31 August 2017, 西安电子科技大学出版社 *

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN108996600A (en) * 2018-07-26 2018-12-14 中原工学院 Utilize the method for solar battery waste material regulation creek black and odorous water
CN108996600B (en) * 2018-07-26 2021-07-02 中原工学院 Method for remedying river black and odorous water body by using solar cell waste

Similar Documents

Publication Publication Date Title
Marcelino et al. Solar energy for wastewater treatment: review of international technologies and their applicability in Brazil
CN106140242B (en) A kind of visible-light response type boron nitride modification carbon nitride photocatalyst and its preparation method and application
CN102274739B (en) Copper-nitrogen double-doped titanium dioxide photocatalytic material
CN101653728A (en) Preparation method and application thereof for zinc ferrite/titanium dioxide nano compounded visible light photocatalyst
CN107029771B (en) Silver carbonate/silver/tungstic acid tri compound Z-type photochemical catalyst and its preparation method and application
CN101773841A (en) Photocatalyst for water treatment
CN106299418A (en) The photocatalysis wastewater fuel cell, manufacture of strengthening radical reaction and preparation method and application
Zhang et al. Photocatalytic removal organic matter and bacteria simultaneously from real WWTP effluent with power generation concomitantly: Using an ErAlZnO photo-anode
CN106902803B (en) Compound photocatalytic system CQDS-KNbO3 and preparation method and application thereof
CN103785422B (en) The preparation method of cauliflower-shaped CdS Nano microsphere photochemical catalyst and application thereof
CN207619091U (en) A kind of photocatalysis oxidation reaction apparatus
Ruiz-Aguirre et al. Assessment of pilot-plant scale solar photocatalytic hydrogen generation with multiple approaches: Valorization, water decontamination and disinfection
CN110783111A (en) Titanium dioxide film electrode and preparation method and application thereof
CN106395998A (en) Salt-containing wastewater resourceful treatment method
Wang et al. Upconversion Tm3+: CeO2/palygorskite as direct Z-scheme heterostructure for photocatalytic degradation of bisphenol A
CN108249510A (en) A kind of method based on light conversion material processing water body organic contamination
CN108889289B (en) Preparation and application of nano-micron silicon particle composite titanium dioxide photocatalyst
CA2929997A1 (en) Hollow optical fibre photo-catalytic reactor utilizing solar energy and uv rays
EP3990395B1 (en) Modular photocatalytic system
Zhai et al. Applications of Cu2O octahedral particles on ITO glass in photocatalytic degradation of dye pollutants under a halogen tungsten lamp
CN101704598A (en) Method for degrading polychlorinated biphenyl in water body by irradiation
CN104368324A (en) Preparation method and application of mesoporous graphene/titanium dioxide nano composite material
CN209052544U (en) A kind of coupling device of microbiological fuel cell and photo-electrocatalytic technology
CN103086563B (en) Multistage sunlight photocatalytic landfill leachate treatment technology
CN106380027A (en) Sewage deep treatment method

Legal Events

Date Code Title Description
PB01 Publication
PB01 Publication
SE01 Entry into force of request for substantive examination
SE01 Entry into force of request for substantive examination
RJ01 Rejection of invention patent application after publication

Application publication date: 20180706

RJ01 Rejection of invention patent application after publication