CN102806082A - Method for preparing visible light catalyst for degrading sulphide ore dressing organic wastewater - Google Patents

Method for preparing visible light catalyst for degrading sulphide ore dressing organic wastewater Download PDF

Info

Publication number
CN102806082A
CN102806082A CN2012102438774A CN201210243877A CN102806082A CN 102806082 A CN102806082 A CN 102806082A CN 2012102438774 A CN2012102438774 A CN 2012102438774A CN 201210243877 A CN201210243877 A CN 201210243877A CN 102806082 A CN102806082 A CN 102806082A
Authority
CN
China
Prior art keywords
visible light
water
sulphide ore
preparation
light catalyst
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
CN2012102438774A
Other languages
Chinese (zh)
Inventor
周国华
张春燕
刘红
曹琴琴
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.)
Hubei University of Technology
Original Assignee
Hubei University 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 Hubei University of Technology filed Critical Hubei University of Technology
Priority to CN2012102438774A priority Critical patent/CN102806082A/en
Publication of CN102806082A publication Critical patent/CN102806082A/en
Pending legal-status Critical Current

Links

Images

Classifications

    • 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 preparing a visible light catalyst for degrading sulphide ore dressing organic wastewater. The method takes ferric nitrate, malonic acid and water as raw materials which are uniformly mixed, the mixture is vaporized in a water bath of 80 DEG C to be pasty, is dried at the condition of 105 DEG C-120 DEG C, and is calcinated at 200 DEG C-500 DEG C, and nanocrystalline iron oxide powder is obtained. An iron oxide photocatalyst can effectively degrade the organic ingredients of the sulphide ore dressing organic wastewater under the irradiation of visible lights. The method has the advantages of simple and quick catalyst preparation, quick organic pollutant degradation, obvious pollutant removing effect and low cost, and does not cause secondary pollution.

Description

The visible light catalyst preparation method of degraded sulphide ore ore dressing organic wastewater
Technical field
The present invention relates to a kind of method of Beneficiation Wastewater, particularly to a kind of visible light catalyst preparation method of the sulphide ore ore dressing organic wastewater of degrading.
Background technology
Along with the development of mining industry, the consumption of the floating agent that uses in the ore dressing process is increasing, and the environmental pollution that the while floating agent brings is also more and more serious.Because the floating agent consumption is big, efficient is low, high poison and high pollution; Medicament residual volume in the beneficiation wastewater is bigger; Cause many mining area ecological environments constantly to worsen, water body and soil receive severe contamination, and health of human body, agricultural production and fishery have all been caused very big harm.The technology of therefore, how to seek a kind of improvement beneficiation wastewater effectively and reasonably is the great difficult problem that people need to be resolved hurrily.
At present, the method for organic principle has bioanalysis, chemical method, physisorphtion and mine tailing storehouse self-purification method etc. in the processing beneficiation wastewater of sulphide ore.Bioanalysis is poor to the organic principle degradation property in some sulfide flotation waste water.Chinese patent CN101875960A tests the biological degradability of the organic principle hydrocarbyl xanthate in the sulfide flotation waste water; The result shows that ethyl xanthate is biodegradable, but isopropyl xanthate, normal-butyl xanthate, Isobutylxanthic acid and n-pentyl xanthate all belong to difficult for biological degradation.Chinese patent CN101279804A discloses the method with ozone method degraded sulphide ore ore dressing organic wastewater.This method reaction speed is fast, and it is remarkable to remove the pollutant effect.But ozone is prone to decompose, and can not recycle.The absorption method reproducing adsorbent is more loaded down with trivial details.Mine tailing storehouse self-purification method degradation speed is slow.
In recent years, utilize the poisonous and hazardous pollutant of semi-conducting material photocatalytic degradation to become one of popular research topic of comparison.Not only energy consumption is low, easy and simple to handle, reaction condition is gentle, non-secondary pollution for photocatalysis technology, and can effectively organic pollution be converted into inorganic molecules, reaches the purpose of complete inorganicization.Using more photochemical catalyst at present is TiO 2, it has the advantage of photocatalytic activity height, good stability.Yet TiO 2Greater band gap, can only absorb the ultraviolet light of λ≤387nm, the utilization rate of luminous energy is low.Therefore, people transfer to sight gradually has the low energy gap width, can utilize the semiconductor light-catalyst of visible light, to improve the utilization ratio to solar energy.Chinese patent CN101830537A discloses the method for organic principle in a kind of visible light photocatalytic degradation beneficiation wastewater of sulphide ore.This method prepares photochemical catalyst Bi with coprecipitation 2O 3Powder.Its preparation process comprises: the 1. preparation of presoma: with five water bismuth nitrates, red fuming nitric acid (RFNA) and deionized water mixing in polytetrafluoroethylcontainer container according to a certain percentage; Slowly drip KOH solution then and be neutral to pH; Stir while dripping, obtain the solid deposition behind the reaction 1h; With sedimentation and filtration and washing, dry (120 ℃) then, grind, obtain precursor powder; 2. photochemical catalyst Bi 2O 3Preparation: precursor powder is calcined 6h in 303 ℃~800 ℃, obtains Bi 2O 3Powder.Though it is fast that this method has technological reaction speed, remove pollutant obvious results advantage, its semiconductor light-catalyst that relates to preparation is complicated, and cost is high.
Summary of the invention
In view of the deficiency of prior art, the objective of the invention is to the fast simple and low Fe of cost with preparation technology 2O 3The photochemical catalyst beneficiation wastewater of sulphide ore organic principle that is used for degrading, thus the complicated and high problem of cost of existing visible light catalyst preparation solved.
The objective of the invention is to realize like this:
The visible light catalyst preparation method of organic principle in a kind of beneficiation wastewater of sulphide ore of degrading is a raw material with ferric nitrate, malonic acid and water, adopts wet chemistry method to be prepared into alpha-iron oxide nano-powder, promptly gets visible light catalyst.
Preferably, the preparation method of said visible light catalyst comprises the steps:
(1) is raw material with ferric nitrate, malonic acid and water, mixes, be evaporated to pasty state 80 ℃ of water-baths; Wherein, ferric nitrate, the mol ratio of malonic acid and water is: 1:2-8:45-180;
(2) pastel is dry under 105 ℃ of-120 ℃ of conditions;
(3) dry pastel is put into kiln calcining under 200 ℃-500 ℃ and got alpha-iron oxide nano-powder in 2-6 hour.
Further preferably, the preparation method of said visible light catalyst, ferric nitrate wherein, the mol ratio of malonic acid and water is: 1:2-4:47-84.
Further preferably, the preparation method of said visible light catalyst, wherein the calcining heat in the step (3) is 250 ℃-350 ℃, calcination time is 2-3 hour.
Again further preferably, the preparation method of said visible light catalyst, wherein the water of step (1) employing is deionized water or distilled water.
The method of organic principle in a kind of beneficiation wastewater of sulphide ore of degrading comprises alpha-iron oxide nano-powder with method for preparing as visible light catalyst, outstandingly turbidly in beneficiation wastewater of sulphide ore, carries out illumination and penetrates.
Preferably, the method for organic principle in the said degraded beneficiation wastewater of sulphide ore, wherein the ratio in 0.3~2.0g/L waste water adds alpha-iron oxide nano-powder, and irradiation is 150~240 minutes under visible light.
The present invention introduces beneficiation wastewater in the cylindrical quartz photo catalysis reactor, adds the photochemical catalyst Fe of preparation as stated above in the ratio of 0.3~2.0 g/L waste water 2O 3, open magnetic stirring apparatus again and stir, make Fe 2O 3Be suspended state, connect xenon source then, shone 150~240 minutes, utilize Fe 2O 3Organic principle in the photocatalytic degradation waste water.Said xenon lamp places in the quartzy cold-trap, and this cold-trap is fixed on cylindrical quartz reactor central authorities, is connected with cooling water in the interlayer in the cold-trap, eliminates the fuel factor of xenon lamp through the flow of regulating cooling water.Said light source adopts xenon lamp, the following wave spectrum of optical filter elimination 420 nm.This xenon lamp is used for simulated solar spectrum.Also can use solar light irradiation in the present invention.
The visible light catalyst preparation method of the degraded sulphide ore ore dressing organic wastewater that compared with prior art, the present invention relates to has following main advantage and progress:
Figure 2012102438774100002DEST_PATH_IMAGE002
Photochemical catalyst Fe 2O 3Manufacturing process is simply quick, and cost is low; Photochemical catalyst Fe 2O 3Avirulence.
Figure 2012102438774100002DEST_PATH_IMAGE004
Photochemical catalyst Fe 2O 3Good photocatalytic activity is arranged under visible light, improved utilization ratio the sunshine energy.
3. it is remarkable to remove the pollutant effect, and degradation speed is fast,
Figure 2012102438774100002DEST_PATH_IMAGE006
becomes the inorganic molecules material with the pollutant final degradation, thereby avoided the generation of secondary pollution.
Description of drawings
Fig. 1 is the XRD figure spectrum of the ferric oxide powder of the embodiment of the invention 1 preparation;
Fig. 2 is the SEM photo of the ferric oxide powder of the embodiment of the invention 1 preparation.
The specific embodiment
Below through the embodiment form foregoing of the present invention is remake further detailed description; But should this be interpreted as that the scope of the above-mentioned theme of the present invention only limits to following embodiment, all technology that realizes based on foregoing of the present invention all belong to scope of the present invention.
Embodiment 1:
10.0g nine water ferric nitrates (about 0.03 mol) and 6.3 g malonic acid (about 0.06 mol) are added in 25 mL (the about 1.4 mol) distilled water successively, mix, be evaporated to pasty state 80 ℃ of water-baths.Pastel is dry under 105 ℃ of conditions; Dry pastel is put into kiln calcining under 250 ℃ got ferric oxide powder in 3 hours.The XRD figure spectrum of gained powder is as shown in Figure 1.Can know from Fig. 1, all characteristic peak positions and standard powder diffraction card (
Figure 2012102438774100002DEST_PATH_IMAGE007
-Fe 2O 3PDF 39-1346) diffraction maximum is consistent, can confirm that the gained powder does -Fe 2O 3The SEM photo of gained powder is as shown in Figure 2, and this figure shows that the size of gained powder is about 50 nm~100 nm.
Be in the butyl xanthate flotation waste water adding cylindrical quartz photo catalysis reactor of 40.0 mg/L with 40 mL concentration then, add the Fe of embodiment 1 preparation 2O 340 mg, magnetic agitation makes photochemical catalyst be in suspended state always, shines with 300 W xenon lamps then.The following wave spectrum of optical filter elimination 420 nm.At wavelength>after the illumination of 420 nm penetrated 150 min, butyl xanthate concentration changes with time situation was as shown in table 1.Can know that by table 1 behind illumination 150 min, the degradation rate of butyl xanthate is 94.0%.
The Fe of 250 ℃ of preparations of table 1 2O 3Visible light photocatalytic degradation contains butyl xanthate beneficiation wastewater result
Figure DEST_PATH_IMAGE009
Embodiment 2:
10.0g nine water ferric nitrates (about 0.03 mol) and 9.4 g malonic acid (about 0.09 mol) are added in 35 mL (the about 1.9 mol) distilled water successively, mix, be evaporated to pasty state 80 ℃ of water-baths.Pastel is dry under 105 ℃ of conditions; Dry pastel is put into kiln calcining under 300 ℃ got ferric oxide powder in 2 hours.
Be in the butyl xanthate flotation waste water adding cylindrical quartz reactor of 40.0 mg/L with 40 mL concentration then, add the Fe of 40 mg embodiment, 2 preparations 2O 3, magnetic agitation makes photochemical catalyst be in suspended state always, shines with 300 W xenon lamps then.The following wave spectrum of optical filter elimination 420 nm.At wavelength>behind illumination 180 min of 420 nm, the butyl xanthate concentration changes with time is as shown in table 2.Can know that by table 2 behind illumination 180 min, the degradation rate of butyl xanthate is 96.0%.
The Fe of 300 ℃ of preparations of table 2 2O 3Visible light photocatalytic degradation contains butyl xanthate beneficiation wastewater result
Embodiment 3:
10.0g nine water ferric nitrates (about 0.03 mol) and 12.5g malonic acid (about 0.12 mol) are added in the 45 mL distilled water (about 2.5 mol) successively, mix, be evaporated to pasty state 80 ℃ of water-baths.Pastel is dry under 105 ℃ of conditions; Dry pastel is put into kiln calcining under 350 ℃ got ferric oxide powder in 2 hours.
Be in the butyl xanthate flotation waste water adding cylindrical quartz reactor of 40.0 mg/L with 40 ml concentration then, add the Fe of 40 mg embodiment, 3 preparations respectively 2O 3, magnetic agitation makes photochemical catalyst be in suspended state always, shines with the 300W xenon lamp then.The following wave spectrum of optical filter elimination 420 nm.At wavelength>behind illumination 240 min of 420 nm, the butyl xanthate concentration changes with time is as shown in table 3.Can know that by table 3 behind illumination 240 min, the degradation rate of butyl xanthate is 90.0%.
The Fe of 350 ℃ of preparations of table 3 2O 3Visible light photocatalytic degradation contains butyl xanthate beneficiation wastewater result
Figure DEST_PATH_IMAGE013

Claims (8)

1. the visible light catalyst preparation method of organic principle in the beneficiation wastewater of sulphide ore of degrading, it is characterized in that: with ferric nitrate, malonic acid and water is raw material, adopts wet chemistry method to be prepared into alpha-iron oxide nano-powder.
2. according to the preparation method of the said visible light catalyst of claim 1, it is characterized in that comprising the steps:
(1) is raw material with ferric nitrate, malonic acid and water, mixes, be evaporated to pasty state 80 ℃ of water-baths; Wherein, ferric nitrate, the mol ratio of malonic acid and water is: 1:2-8:45-180;
(2) pastel is dry under 105 ℃ of-120 ℃ of conditions;
(3) dry pastel is put into kiln calcining under 200 ℃-500 ℃ and got alpha-iron oxide nano-powder in 2-6 hour.
3. according to the preparation method of the said visible light catalyst of claim 2, it is characterized in that: ferric nitrate, the mol ratio of malonic acid and water is: 1:2-4:47-84.
4. according to the preparation method of the said visible light catalyst of claim 2, it is characterized in that: the calcining heat in the step (3) is 250 ℃-350 ℃, and calcination time is 2-3 hour.
5. according to the preparation method of each said visible light catalyst of claim 1-4, it is characterized in that: the water that step (1) adopts is deionized water or distilled water.
6. the method for organic principle in the beneficiation wastewater of sulphide ore of degrading is characterized in that: comprise alpha-iron oxide nano-powder with each preparation of claim 1-4 as visible light catalyst, outstandingly turbidly in beneficiation wastewater of sulphide ore, carry out illumination and penetrate.
7. according to the method for organic principle in the said degraded beneficiation wastewater of sulphide ore of claim 6, it is characterized in that: the ratio in 0.3 ~ 2.0g/L waste water adds alpha-iron oxide nano-powder, and irradiation is 150~240 minutes under visible light.
8. according to the method for organic principle in the said degraded beneficiation wastewater of sulphide ore of claim 7, it is characterized in that: the light source of said visible light is xenon lamp or sunshine.
CN2012102438774A 2012-07-16 2012-07-16 Method for preparing visible light catalyst for degrading sulphide ore dressing organic wastewater Pending CN102806082A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN2012102438774A CN102806082A (en) 2012-07-16 2012-07-16 Method for preparing visible light catalyst for degrading sulphide ore dressing organic wastewater

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN2012102438774A CN102806082A (en) 2012-07-16 2012-07-16 Method for preparing visible light catalyst for degrading sulphide ore dressing organic wastewater

Publications (1)

Publication Number Publication Date
CN102806082A true CN102806082A (en) 2012-12-05

Family

ID=47230056

Family Applications (1)

Application Number Title Priority Date Filing Date
CN2012102438774A Pending CN102806082A (en) 2012-07-16 2012-07-16 Method for preparing visible light catalyst for degrading sulphide ore dressing organic wastewater

Country Status (1)

Country Link
CN (1) CN102806082A (en)

Citations (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101830537A (en) * 2010-03-23 2010-09-15 武汉理工大学 Method for degrading organic components in ore-dressing wastewater of sulphide ores by catalysis under visible light

Patent Citations (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101830537A (en) * 2010-03-23 2010-09-15 武汉理工大学 Method for degrading organic components in ore-dressing wastewater of sulphide ores by catalysis under visible light

Non-Patent Citations (1)

* Cited by examiner, † Cited by third party
Title
邓庚凤等: "溶胶-凝胶法制备超细氧化铁的工艺研究", 《江西理工大学学报》 *

Similar Documents

Publication Publication Date Title
Li et al. Roles of Cr3+ doping and oxygen vacancies in SrTiO3 photocatalysts with high visible light activity for NO removal
Amini et al. Photocatalytic degradation of some organic dyes under solar light irradiation using TiO2 and ZnO nanoparticles
Zhang et al. Novel La-doped Bi 2 WO 6 photocatalysts with enhanced visible-light photocatalytic activity
CN109395761B (en) Nitrogen-doped BiOIO3Preparation method and application of photocatalyst
Sadia et al. Metal doped titania nanoparticles as efficient photocatalyst for dyes degradation
CN105056981A (en) Preparation and application of composite photocatalyst g-C3N4-BiFeO3 for efficiently removing persistent organic pollutants
CN109550500A (en) It is a kind of can Magnetic Isolation graphene-based zinc-iron mixing bimetallic oxide photochemical catalyst preparation method and applications
Palas et al. Bioinspired metal oxide particles as efficient wet air oxidation and photocatalytic oxidation catalysts for the degradation of acetaminophen in aqueous phase
CN103230802B (en) Preparation method of composite photocatalyst with visible light response and arsenic removing method
CN104941667B (en) A kind of petal-shaped magnetic iron oxide molybdenum sulfide complex and preparation method thereof
CN104828902A (en) Method for treating chrome-containing wastewater by catalytic reduction of petaloid magnetic iron oxide/molybdenum sulfide composite
CN101830537B (en) Method for degrading organic components in ore-dressing wastewater of sulphide ores by catalysis under visible light
Wang et al. Upconversion Tm3+: CeO2/palygorskite as direct Z-scheme heterostructure for photocatalytic degradation of bisphenol A
CN101491769A (en) Strontium carbonate with visible photoresponse and preparation method thereof
Mandal et al. Solar light sensitive samarium-doped ceria photocatalysts: microwave synthesis, characterization and photodegradation of Acid Orange 7 at atmospheric conditions and in the absence of any oxidizing agents
CN105289577A (en) Vanadium tantalum/niobate photocatalyst and preparation method and application of vanadium tantalum/niobate photocatalyst
CN109364924B (en) Magnetic nano ozone catalyst CoFe2O4And preparation method and application thereof
CN104549385A (en) Graphene oxide composite FePO4 heterogeneous visible light Fenton catalyst and preparation method thereof
CN104368369B (en) A kind of preparation method of silver phosphate-cadmium sulfide compounded visible light photocatalyst
Zeid et al. A comparative study of single and bi-doped Co3O4 nanocatalysts for the photodegradation of methyl orange dye
CN108940349A (en) The method of carbonitride Z-type photochemical catalyst removal dyestuff contaminant is mixed using siliver chromate/sulphur
Yu et al. Synergistic effects of oxygen vacancies and the chelation of tetracycline with metallic ions for enhanced degradation of tetracycline over photocatalysts La 2− x K x NiMnO 6
CN113262792B (en) CoO-CeO 2 Photocatalyst and preparation method and application thereof
CN102806082A (en) Method for preparing visible light catalyst for degrading sulphide ore dressing organic wastewater
CN113457704B (en) Fe (Fe) 2 O 3 -ZnO/g-C 3 N 4 Composite material, preparation method and application thereof

Legal Events

Date Code Title Description
C06 Publication
PB01 Publication
C10 Entry into substantive examination
SE01 Entry into force of request for substantive examination
C02 Deemed withdrawal of patent application after publication (patent law 2001)
WD01 Invention patent application deemed withdrawn after publication

Application publication date: 20121205