CN103071498A - Preparation method of Cu2O compound photocatalyst - Google Patents

Preparation method of Cu2O compound photocatalyst Download PDF

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Publication number
CN103071498A
CN103071498A CN2013100124705A CN201310012470A CN103071498A CN 103071498 A CN103071498 A CN 103071498A CN 2013100124705 A CN2013100124705 A CN 2013100124705A CN 201310012470 A CN201310012470 A CN 201310012470A CN 103071498 A CN103071498 A CN 103071498A
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solution
ethyl alcohol
absolute ethyl
preparation
expanded graphite
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CN103071498B (en
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杜亚丽
祝宝林
赵强
宋少飞
刘有军
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Shanxi Yuan Technology Co Ltd
Taiyuan University of Technology
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Abstract

The invention provides a preparation method of a Cu2O compound photocatalyst. The method includes the following steps: mixing distilled water, absolute ethyl alcohol and a copper salt solution, adding EG (expanded graphite) and evenly stirring, then adding a NaOH solution and absolute ethyl alcohol, and finally adding an NH2OH*HC1 solution, stirring and standing; heating the prepared solution in a water bath and stirring, removing the supernatant after layering after the reaction is over, flushing and precipitating; and finally dissolving the precipitating in absolute ethyl alcohol, drying to prepare the Cu2O compound photocatalyst. The method takes EG and a copper compound as the raw materials to prepare an EG-loaded nano Cu2O sample, the raw material source is easy, the cost is low, the preparation technology is simple, requirements for equipment are low, and the operability is good; and nano-particles in the prepared photocatalyst are uniformly loaded on the EG surface, and the photocatalyst can degrade hazardous and noxious substances under the condition of visible light, is simple in recycling, and is quite suitable for processing organic pollutants.

Description

A kind of Cu 2The preparation method of O composite photocatalyst
Technical field
The present invention relates to the photochemical catalyst preparing technical field in the Chemical Engineering, specifically a kind of Cu 2The preparation method of O composite photocatalyst.
Background technology
In recent years, nanometer Cu 2O progressively has been subject to Environmental Studies person's attention because it has superior photocatalysis performance aspect environmental pollution improvement, be the TiO that continues 2New Generation Optical catalyst afterwards is a kind of environmental protection photochemical catalyst that has DEVELOPMENT PROSPECT.Relevant studies show that is with nanometer Cu 2O is photochemical catalyst, utilizes sunshine as the research of light source treatment of dyeing and printing, shows Cu 2O heterogeneous catalysis method may become the effective way that waste water from dyestuff is administered.
In order to improve Cu 2The photocatalysis performance of O can carry out modification to it.Relevant scholar is to Cu 2The research of the synthetic and photocatalysis performance of O internal carbon-inlaid nano pipe composite balls has illustrated Cu 2The photocatalytic activity of O composite balls p-nitrophenyl phenol solution compares Cu 2O exceeds about 10%.Yet CNT is not suitable for industrial production owing to expensive, so replace carbon nanotube loaded Cu with cheap carrier 2O just becomes researcher's research emphasis.
Expanded graphite is that native graphite obtains a kind of lamellar compound through the strong oxidizer oxidation, has the characteristics such as specific area is large, the interlayer ion exchange capacity is strong, and these characteristics are conducive to the compound of expanded graphite and inorganic material.Demonstrated many superior performances with expanded graphite as the prepared nano composite material of carrier, and its cost is more much lower than carbon nano tube compound material, thereby has potential application prospect.Present research mainly concentrates on expanded graphite/organic matter nano composite material aspect, and is relatively less about the research of expanded graphite/composite material of inorganic matter.
Based on above analysis, the present invention prepares a kind of Cu take expanded graphite and copper compound as raw material by direct precipitation method 2The O composite photocatalyst, this catalyst preparation cost is low, and preparation technology is simple, and is low for equipment requirements, and operability is good, can the efficient degradation poisonous and harmful substance under visible light, recycle simply, be highly suitable for the deep treatment of waste water from dyestuff.
Summary of the invention
The object of the present invention is to provide a kind of Cu 2The preparation method of O composite photocatalyst take expanded graphite and copper compound as raw material, prepares expanded graphite supporting nanometer Cu by direct precipitation method 2The O sample, this preparation technology is simple, and cost is low, and is low for equipment requirements, and operability is good.
Technical scheme provided by the invention is: a kind of Cu 2The preparation method of O composite photocatalyst is characterized in that comprising the steps:
(1) copper salt solution with 0.5 mol/L of the absolute ethyl alcohol of the distilled water of 83.4 unit volumes, 20 unit volumes and 5 unit volumes mixes, then adding expanded graphite stirs, then alternately add the NaOH solution of 1.0 mol/L of 9 unit volumes and the absolute ethyl alcohol of 30 unit volumes, all add at last the NH of 0.5 mol/L of 0.5 ~ 15 unit volume 2OHHCl solution left standstill after the stirring 1 ~ 6 hour;
(2) gained solution in the step 1 is carried out heating water bath also stirred in 1 ~ 30 minute, after solution reaction is finished layering, outwell supernatant liquor, mixed solution with absolute ethyl alcohol and distilled water washes precipitation, at last precipitation is dissolved in the absolute ethyl alcohol, 20 ~ 80 ℃ of lower oven dry precipitations, namely get a kind of Cu 2The O composite photocatalyst.
Copper salt solution in the described step 1 is CuCl 2Or Cu (NO 3) 2Solution, the mass ratio of mantoquita and expanded graphite are 5:1 ~ 1:1.
The load capacity of expanded graphite is 10% ~ 50% in the described step 1.
Add NH in the described step 1 2The time of OHHCl solution is 1 ~ 30 second.
Be used in the described step 2 washing in the mixed solution of precipitation, the volume ratio of absolute ethyl alcohol and distilled water is 1:1.
The invention has the beneficial effects as follows:
(1) among the present invention take expanded graphite and copper compound as raw material, prepare expanded graphite supporting nanometer Cu by direct precipitation method 2The O sample, the raw material that adopt source is easy, and price is low, and preparation technology is simple, and is low for equipment requirements, and operability is good;
(2) in the photochemical catalyst of the present invention preparation the nano particle uniform load on the expanded graphite surface, can be under the visible light condition efficient degradation poisonous and harmful substance, recycle simply, be highly suitable for the processing of organic pollution;
(3) expanded graphite has the characteristics such as specific area is large, the interlayer ion exchange capacity is strong, these characteristics are conducive to the compound of expanded graphite and inorganic material, have good synergy with expanded graphite as the prepared nano-photo catalytic composite of carrier, can greatly improve its photocatalytic degradation ability.
The specific embodiment
The present invention will be further described below in conjunction with specific embodiment, and the present invention is not limited only to these embodiment.
Embodiment 1:
A kind of Cu 2The preparation method of O composite photocatalyst is characterized in that comprising the steps:
(1) with the CuCl of 0.5 mol/L of the absolute ethyl alcohol of the distilled water of 83.4ml, 20ml and 5ml 2Solution mixes, and then adds expanded graphite and stirs, and wherein the mass ratio of mantoquita and expanded graphite is 5:1, then alternately adds the NaOH solution of 1.0 mol/L of 9ml and the absolute ethyl alcohol of 30ml, the last NH that all added 0.5 mol/L of 9.8ml in 5 seconds 2OHHCl solution left standstill after the stirring 6 hours;
(2) gained solution in the step 1 is carried out heating water bath also stirred in 10 minutes, after solution reaction is finished layering, outwell supernatant liquor, be that the absolute ethyl alcohol of 1:1 and the mixed solution of distilled water wash precipitation with volume ratio, at last precipitation is dissolved in the absolute ethyl alcohol, 75 ℃ of lower oven dry precipitations, namely get a kind of Cu 2The O composite photocatalyst.
This composite photocatalyst is carried out the photocatalytic degradation experiment according to the evaluation method of photocatalysis degradation organic contaminant, found that the degradation rate of methyl orange can reach 98%.
Embodiment 2:
A kind of Cu 2The preparation method of O composite photocatalyst is characterized in that comprising the steps:
(1) with the Cu (NO of 0.5 mol/L of the absolute ethyl alcohol of the distilled water of 83.4ml, 20ml and 5ml 3) 2Solution mixes, and then adds expanded graphite and stirs, and wherein the mass ratio of mantoquita and expanded graphite is 1:1, then alternately adds the NaOH solution of 1.0 mol/L of 9ml and the absolute ethyl alcohol of 30ml, the last NH that all added 0.5 mol/L of 15ml in 25 seconds 2OHHCl solution left standstill after the stirring 1.5 hours;
(2) gained solution in the step 1 is carried out heating water bath also stirred in 20 minutes, after solution reaction is finished layering, outwell supernatant liquor, be that the absolute ethyl alcohol of 1:1 and the mixed solution of distilled water wash precipitation with volume ratio, at last precipitation is dissolved in the absolute ethyl alcohol, 50 ℃ of lower oven dry precipitations, namely get a kind of Cu 2The O composite photocatalyst.
This composite photocatalyst is carried out the photocatalytic degradation experiment according to the evaluation method of photocatalysis degradation organic contaminant, found that the degradation rate of methyl orange can reach 93%.
The evaluation method of photocatalysis degradation organic contaminant: take methyl orange as target contaminant, the methyl orange solution of configuration 30mg/L, the catalyst sample of 100mg is added in the 90mL methyl orange solution, carries out under these conditions the catalytic decolorization degraded of methyl orange solution, in this process, continue to stir.At first dark reaction is 30 minutes, gets subsequently the 6mL sample, immediately the centrifugal photochemical catalyst of removing.With the absorbance of 722 type spectrophotometric determination clear liquids at λ max=464nm place.Afterwards, carry out light-catalyzed reaction, got one time sample every 10 minutes, survey the absorbance of materialsing, it is 2 hours that total duration is tested in photocatalysis.Obtain the ultraviolet-visible absorption spectroscopy of sample after 90 minutes.

Claims (5)

1. Cu 2The preparation method of O composite photocatalyst is characterized in that comprising the steps:
(1) copper salt solution with 0.5 mol/L of the absolute ethyl alcohol of the distilled water of 83.4 unit volumes, 20 unit volumes and 5 unit volumes mixes, then adding expanded graphite stirs, then alternately add the NaOH solution of 1.0 mol/L of 9 unit volumes and the absolute ethyl alcohol of 30 unit volumes, all add at last the NH of 0.5 mol/L of 0.5 ~ 15 unit volume 2OHHCl solution left standstill after the stirring 1 ~ 6 hour;
(2) gained solution in the step 1 is carried out heating water bath also stirred in 1 ~ 30 minute, after solution reaction is finished layering, outwell supernatant liquor, mixed solution with absolute ethyl alcohol and distilled water washes precipitation, at last precipitation is dissolved in the absolute ethyl alcohol, 20 ~ 80 ℃ of lower oven dry precipitations, namely get a kind of Cu 2The O composite photocatalyst.
2. require described a kind of Cu according to claim 1 2The preparation method of O composite photocatalyst is characterized in that: the copper salt solution in the described step 1 is CuCl 2Or Cu (NO 3) 2Solution, the mass ratio of mantoquita and expanded graphite are 5:1 ~ 1:1.
3. require described a kind of Cu according to claim 1 2The preparation method of O composite photocatalyst is characterized in that: the load capacity of expanded graphite is 10% ~ 50% in the described step 1.
4. according to the preparation method of a kind of fly ash base photocatalysis brick claimed in claim 1, it is characterized in that: add NH in the described step 1 2The time of OHHCl solution is 1 ~ 30 second.
5. according to the preparation method of a kind of fly ash base photocatalysis brick claimed in claim 1, it is characterized in that: be used in the described step 2 washing in the mixed solution of precipitation, the volume ratio of absolute ethyl alcohol and distilled water is 1:1.
CN201310012470.5A 2013-01-14 2013-01-14 Preparation method of Cu2O compound photocatalyst Expired - Fee Related CN103071498B (en)

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Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN108217868A (en) * 2017-12-07 2018-06-29 吴亚琴 A kind of preparation method of high alga-killing rate composite algicide
CN110496624A (en) * 2019-08-22 2019-11-26 四川建筑职业技术学院 A kind of composite material and preparation method for sewage treatment
CN113117676A (en) * 2021-03-08 2021-07-16 新乡学院 Cu2Preparation method of O-CuO/bentonite photocatalytic composite material
CN113441156A (en) * 2021-06-24 2021-09-28 青岛科技大学 Hollowed-out spherical structure Cu2O/Cu9S5Photocatalytic material and preparation method and application thereof
CN114250627A (en) * 2021-11-30 2022-03-29 盐城工学院 Preparation method of cuprous oxide composite material for finishing cotton fabric

Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1772648A (en) * 2005-09-29 2006-05-17 江苏工业学院 Normal temperature and normal pressure ClO2 catalyzed oxidation process of treating high concentration organic waste water
CN101698496A (en) * 2009-10-28 2010-04-28 广东光华化学厂有限公司 Preparation method of electronic grade high-purity copper oxide superfine powder
CN101773831A (en) * 2009-11-27 2010-07-14 中国科学院广州地球化学研究所 Micro-pore cuprous oxide visible light catalyst and preparation method and application thereof
CN101947425A (en) * 2010-08-24 2011-01-19 中山大学 Method for directly synthesizing dimethyl carbonate from methanol and carbon dioxide and special electrical assisted catalytic reactor
CN102266764A (en) * 2011-06-17 2011-12-07 东华大学 Expanded graphite/zinc oxide composite photocatalyst and preparation method thereof
CN102533715A (en) * 2012-01-09 2012-07-04 同济大学 Method for preparing biological expanded graphite with visible light catalytic activity

Patent Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1772648A (en) * 2005-09-29 2006-05-17 江苏工业学院 Normal temperature and normal pressure ClO2 catalyzed oxidation process of treating high concentration organic waste water
CN101698496A (en) * 2009-10-28 2010-04-28 广东光华化学厂有限公司 Preparation method of electronic grade high-purity copper oxide superfine powder
CN101773831A (en) * 2009-11-27 2010-07-14 中国科学院广州地球化学研究所 Micro-pore cuprous oxide visible light catalyst and preparation method and application thereof
CN101947425A (en) * 2010-08-24 2011-01-19 中山大学 Method for directly synthesizing dimethyl carbonate from methanol and carbon dioxide and special electrical assisted catalytic reactor
CN102266764A (en) * 2011-06-17 2011-12-07 东华大学 Expanded graphite/zinc oxide composite photocatalyst and preparation method thereof
CN102533715A (en) * 2012-01-09 2012-07-04 同济大学 Method for preparing biological expanded graphite with visible light catalytic activity

Non-Patent Citations (1)

* Cited by examiner, † Cited by third party
Title
王伟等: "碳纳米管铜基复合颗粒的制备", 《中国有色金属学报》, vol. 21, no. 6, 30 June 2011 (2011-06-30) *

Cited By (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN108217868A (en) * 2017-12-07 2018-06-29 吴亚琴 A kind of preparation method of high alga-killing rate composite algicide
CN108217868B (en) * 2017-12-07 2020-12-01 广州市弗雷德环保科技有限公司 Preparation method of composite algaecide with high algae removal rate
CN110496624A (en) * 2019-08-22 2019-11-26 四川建筑职业技术学院 A kind of composite material and preparation method for sewage treatment
CN113117676A (en) * 2021-03-08 2021-07-16 新乡学院 Cu2Preparation method of O-CuO/bentonite photocatalytic composite material
CN113441156A (en) * 2021-06-24 2021-09-28 青岛科技大学 Hollowed-out spherical structure Cu2O/Cu9S5Photocatalytic material and preparation method and application thereof
CN114250627A (en) * 2021-11-30 2022-03-29 盐城工学院 Preparation method of cuprous oxide composite material for finishing cotton fabric

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