CN102489291A - Method for preparing expanded graphite load nanometer bismuth vanadate photochemical catalyst - Google Patents

Method for preparing expanded graphite load nanometer bismuth vanadate photochemical catalyst Download PDF

Info

Publication number
CN102489291A
CN102489291A CN2011104079292A CN201110407929A CN102489291A CN 102489291 A CN102489291 A CN 102489291A CN 2011104079292 A CN2011104079292 A CN 2011104079292A CN 201110407929 A CN201110407929 A CN 201110407929A CN 102489291 A CN102489291 A CN 102489291A
Authority
CN
China
Prior art keywords
expanded graphite
photochemical catalyst
metavanadate
preparation
bismuth
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.)
Granted
Application number
CN2011104079292A
Other languages
Chinese (zh)
Other versions
CN102489291B (en
Inventor
李�浩
刘保江
高品
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.)
Donghua University
Original Assignee
Donghua University
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 Donghua University filed Critical Donghua University
Priority to CN201110407929.2A priority Critical patent/CN102489291B/en
Publication of CN102489291A publication Critical patent/CN102489291A/en
Application granted granted Critical
Publication of CN102489291B publication Critical patent/CN102489291B/en
Expired - Fee Related legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Landscapes

  • Catalysts (AREA)

Abstract

The invention relates to a method for preparing expanded graphite load nanometer bismuth vanadate photochemical catalyst, which comprises the following steps: 1 adding bismuthate and stabilizing agent into phosphate buffer, stirring for 15 to 60 minutes to form turbid liquid, dissolving metavanadate into the phosphate buffer uniformly, adding the phosphate buffer into the turbid liquid, and stirring the solution to be uniform to form transparent solution; and 2 regulating potential of hydrogen (pH) value through alkaline solution, adding expanded graphite at the temperature of 20 DEG C to 100 DEG C, stirring, mixing, refluxing for 6 hours to 24 hours, centrifuging, filtering, washing, finally roasting the obtained products, cooling and grinding to obtain the final product. The method is low in cost, easy to apply and good in maneuverability and has low requirements for devices. The obtained expanded graphite powder bismuth vanadate is even in self-assembly, can efficiently degrade durable toxic and harmful substances under conditions of ultraviolet light and visible light, can be recovered and recycled easily and conveniently and is very suitable for deep processing of waste water.

Description

A kind of preparation method of expanded graphite supporting nanometer pucherite photochemical catalyst
Technical field
The invention belongs to the preparation field of pucherite photochemical catalyst, particularly a kind of preparation method of expanded graphite supporting nanometer pucherite photochemical catalyst.
Background technology
In recent years, with titanium dioxide (TiO 2) for the photocatalysis technology of core representative in the environmental pollution improvement field; Particularly the application in waste water difficult for biological degradation processing and air cleaning more and more widely; But because its greater band gap; Only can under UV-irradiation, just have photocatalysis, thereby limit the further expansion of its application.In order to improve TiO 2To the utilization ratio of sunshine, lot of domestic and international experts and scholars are round visible light-responded TiO 2Photochemical catalyst has launched number of research projects, is primarily aimed at TiO 2Photocatalyst surface is structurally-modified, inorganic elements and doped with metal elements modification etc., is intended to enlarge its spectral response range, improves its visible light catalysis activity.However, the TiO of process modification 2Photochemical catalyst still exists problems such as visible light catalysis activity is undesirable, and the light degradation ability is relatively poor at this stage, causes its practicality relatively poor.
Nearest discovers to have the composite oxides pucherite (BiVO of monoclinic system scheelite-type structure 4) under radiation of visible light, just have photocatalytic activity, can produce oxygen and degradable organic pollutant by the decomposition water molecule, be a kind of potential photochemical catalyst.Yet, BiVO 4Absorption property very poor, and the photo-generated carrier that produces is difficult to migration, easy compound, thereby influenced its visible light activity.At present about being directed against BiVO 4Composite modified less with the research report that mixes, in addition about it being self-assembled to the good porous material of absorption property, also few like the report of active carbon etc.; Therefore; How strengthening its absorption in visible-range, and improve its visible light catalysis activity, is to research and develop BiVO at present 4The main research emphasis of high efficiency photocatalyst.
The sewage disposal conventional method mainly contains: physical partition method, biological degradation method, chemical decomposition method etc.; But all there is certain limitation in these methods; Therefore, the researcher begins to be devoted to develop efficient, low energy consumption, applied widely and the water treatment technology of deep oxidation ability arranged.In recent years, a lot of scholars are with TiO 2Be used for the organic pollution of photocatalytic degradation water body, though obtained certain effect, because the restriction of its photoresponse scope causes treatment effect often not ideal enough.By contrast, BiVO 4Just having good photocatalytic activity in the visible region, is a kind of potential desired light catalyst.
Summary of the invention
Technical problem to be solved by this invention provides a kind of preparation method of expanded graphite supporting nanometer pucherite photochemical catalyst, and this method is with low cost, and is simple, to equipment require lowly, operability is good; The expanded graphite powder pucherite self assembly of preparation is even, can be under ultraviolet light and visible light condition efficient degradation persistence poisonous and harmful substance, reclaiming utilizes easy, is highly suitable for the advanced treating of waste water.
The preparation method of a kind of expanded graphite supporting nanometer pucherite photochemical catalyst of the present invention comprises:
(1) bismuth salt, stabilizing agent are joined in the phosphate buffer, stir 15~60min, form suspension; Metavanadate evenly is dissolved in phosphate buffer earlier, joins then in the above-mentioned suspension, stir, form clear solution; Wherein, the mol ratio of bismuth salt and metavanadate is 1: 1, and bismuth salt and the metavanadate concentration in solution is 0.01~0.15mol/L, and the concentration of stabilizing agent in solution is 0.01~0.05mol/L;
(2) regulate pH value to 4.5~9.0 of above-mentioned clear solution with alkaline solution; Be 5: 1~20: 1 expanded graphite then at 20~100 ℃ of following addings and bismuth salt mass ratio, mix backflow 6-24h; Centrifugal, filter, after the washing; At last with the products therefrom roasting, after cooling is ground, the expanded graphite photochemical catalyst powder of nanometer pucherite that promptly got self assembly.
Bismuth salt in the said step (1) is bismuth nitrate, basic bismuth carbonate, bismuth chloride or bismuth acetate.
Stabilizing agent in the said step (1) is disodium ethylene diamine tetraacetate, tetrasodium ethylenediamine tetraacetate, gluconic acid sodium salt or BTCA.
Metavanadate in the said step (1) is sodium metavanadate, potassium metavanadate or ammonium metavanadate.
Phosphate buffer in the said step (1) is 0.025~0.05mol/L sodium dihydrogen phosphate and the solution composition of 0.05~0.1mol/L dibastic sodium phosphate by concentration.
Alkaline solution in the said step (2) is NaOH or the potassium hydroxide aqueous solution of 0.5~1.5mol/L.
Sintering temperature in the said step (2) is 180~400 ℃, and roasting time is 2~4h.
The present invention utilize the unique layer chain structure characteristic of expanded graphite, specific area greatly, characteristics such as high adsorption capacity, chemical inertness, in conjunction with BiVO 4Visible light catalysis activity, the success with nanometer BiVO 4Load on the expanded graphite; Be prepared into the high catalytic activity visible-light photocatalysis material that can suspend in water; And be applied to the advanced treating of waste water, can realize efficient removal, particularly conventional treatment is difficult to the effectively persistence micropollutants of removal organic pollution in the water; And non-secondary pollution, be the technology of environment-friendly type.
In China, the expanded graphite resource reserve is very big, but later owing to what find; Its development of exploitation level is lower; Add a little less than the relative thin of national nonmetallic ore processing industry basis, to such an extent as to the application of the great mineral reserve of this economic implications also is only limited to general filler, therefore; The prepared support type visible-light photocatalysis material of the present invention also has advantage with low cost, has boundless actual application prospect.
Beneficial effect
(1) the present invention is with low cost, and the preparation method is simple, to equipment require lowly, operability is good;
(2) the expanded graphite powder pucherite self assembly of the present invention preparation is even, can be under ultraviolet light and visible light condition efficient degradation persistence poisonous and harmful substance, reclaiming utilizes easy, is highly suitable for the advanced treating of waste water;
(3) expanded graphite itself is a kind of well behaved adsorbent, have specific area big with characteristics such as high adsorption capacity, in wastewater treatment, can also reach deodorizing simultaneously, beneficial effects such as absorption removal heavy metal ion.
The specific embodiment
Below in conjunction with specific embodiment, further set forth the present invention.Should be understood that these embodiment only to be used to the present invention is described and be not used in the restriction scope of the present invention.Should be understood that in addition those skilled in the art can do various changes or modification to the present invention after the content of having read the present invention's instruction, these equivalent form of values fall within the application's appended claims institute restricted portion equally.
Embodiment 1
(1) bismuth nitrate, disodium ethylene diamine tetraacetate are joined in the phosphate buffer, magnetic agitation 15min forms suspension; Sodium metavanadate evenly is dissolved in phosphate buffer earlier, dropwise joins in the above-mentioned suspension then, magnetic agitation is even, forms clear solution; Wherein the amount of substance concentration of bismuth nitrate, inclined to one side sodium vanadate and disodium ethylene diamine tetraacetate is 0.01mol/L, and phosphate buffer is made up of 0.025mol/L sodium dihydrogen phosphate and 0.05mol/L dibastic sodium phosphate;
(2) adopting concentration is that the pH value that the sodium hydrate aqueous solution of 0.5mol/L is regulated above-mentioned clear solution is 4.5, and at 60 ℃ of adding expanded graphites down, wherein the mass ratio of bismuth salt and expanded graphite is 1: 5 then; Magnetic agitation is mixed continuously, and backflow 6h, centrifugal, filtration are after the washing; Can get yellow product; At last with products therefrom in 180 ℃ of roasting 2h, after cooling is ground, the expanded graphite photochemical catalyst powder of nanometer pucherite that promptly got self assembly.
Embodiment 2
(1) bismuth chloride, gluconic acid sodium salt are joined in the phosphate buffer, magnetic agitation 35min forms suspension; Ammonium metavanadate evenly is dissolved in phosphate buffer earlier, dropwise joins in the above-mentioned suspension then, magnetic agitation is even, forms clear solution; Wherein bismuth chloride amount of substance concentration is that 0.06mol/L, gluconic acid sodium salt amount of substance concentration are 0.03mol/L, alum acid ammonium amount of substance concentration is 0.06mol/L partially, and phosphate buffer is made up of 0.03mol/L sodium dihydrogen phosphate and 0.08mol/L dibastic sodium phosphate;
(2) the employing degree is that the pH value that the potassium hydroxide aqueous solution of 1mol/L is regulated above-mentioned clear solution is 7, adds expanded graphites down at 80 ℃ then, and wherein the mass ratio of bismuth salt and expanded graphite is 1: 12; Magnetic agitation is mixed continuously, and backflow 15h, centrifugal, filtration are after the washing; Can get yellow product; At last with products therefrom in 300 ℃ of roasting 3h, after cooling is ground, the expanded graphite photochemical catalyst powder of nanometer pucherite that promptly got self assembly.
Embodiment 3
(1) bismuth acetate, BTCA are joined in the phosphate buffer, magnetic agitation 60min forms suspension; Potassium metavanadate evenly is dissolved in phosphate buffer earlier, dropwise joins in the above-mentioned suspension then, magnetic agitation is even, forms clear solution; Wherein bismuth acetate amount of substance concentration is that 0.15mol/L, BTCA amount of substance concentration are 0.05mol/L, the amount concentration of alum acid potassium sodium matter is 0.15mol/L partially, and phosphate buffer is made up of 0.05mol/L sodium dihydrogen phosphate and 0.1mol/L dibastic sodium phosphate;
(2) adopting concentration is that the pH value that the sodium hydrate aqueous solution of 1.5mol/L is regulated above-mentioned clear solution is 9, and at 100 ℃ of adding expanded graphites down, wherein the mass ratio of bismuth salt and expanded graphite is 1: 20 then; Magnetic agitation is mixed continuously, and backflow 24h, centrifugal, filtration are after the washing; Can get yellow product; At last with products therefrom in 400 ℃ of roasting 4h, after cooling is ground, the expanded graphite photochemical catalyst powder of nanometer pucherite that promptly got self assembly.
The wastewater treatment experiment: the dyeing waste water with the final discharging of certain printing and dyeing mill is a process object; After the micro-filtrate membrane filtration preliminary treatment; Add same amount therein respectively through embodiment 1~embodiment 3 prepared photochemical catalysts; Under sunshine, shone 6 hours continuously, to decolorization of dyeing rate and COD CrClearance is as shown in the table respectively:
Percent of decolourization COD CrClearance
Embodiment 1 99.3% 89.8%
Embodiment 2 98.1% 93.9%
Embodiment 3 99.5% 95.7%

Claims (7)

1. the preparation method of an expanded graphite supporting nanometer pucherite photochemical catalyst comprises:
(1) bismuth salt, stabilizing agent are joined in the phosphate buffer, stir 15~60min, form suspension; Metavanadate evenly is dissolved in phosphate buffer earlier, joins then in the above-mentioned suspension, stir, form clear solution; Wherein, the mol ratio of bismuth salt and metavanadate is 1: 1, and bismuth salt and the metavanadate concentration in solution is 0.01~0.15mol/L, and the concentration of stabilizing agent in solution is 0.01~0.05mol/L;
(2) regulate pH value to 4.5~9.0 of above-mentioned clear solution with alkaline solution; Be 5: 1~20: 1 expanded graphite then at 20~100 ℃ of following addings and bismuth salt mass ratio, mix backflow 6-24h; Centrifugal, filter, after the washing; At last with the products therefrom roasting, after cooling is ground, the expanded graphite photochemical catalyst powder of nanometer pucherite that promptly got self assembly.
2. the preparation method of a kind of expanded graphite supporting nanometer pucherite photochemical catalyst according to claim 1 is characterized in that: the bismuth salt in the said step (1) is bismuth nitrate, basic bismuth carbonate, bismuth chloride or bismuth acetate.
3. the preparation method of a kind of expanded graphite supporting nanometer pucherite photochemical catalyst according to claim 1 is characterized in that: the stabilizing agent in the said step (1) is disodium ethylene diamine tetraacetate, tetrasodium ethylenediamine tetraacetate, gluconic acid sodium salt or BTCA.
4. the preparation method of a kind of expanded graphite supporting nanometer pucherite photochemical catalyst according to claim 1 is characterized in that: the metavanadate in the said step (1) is sodium metavanadate, potassium metavanadate or ammonium metavanadate.
5. the preparation method of a kind of expanded graphite supporting nanometer pucherite photochemical catalyst according to claim 1 is characterized in that: the phosphate buffer in the said step (1) is 0.025~0.05mol/L sodium dihydrogen phosphate and the solution composition of 0.05~0.1mol/L dibastic sodium phosphate by concentration.
6. the preparation method of a kind of expanded graphite supporting nanometer pucherite photochemical catalyst according to claim 1 is characterized in that: the alkaline solution in the said step (2) is NaOH or the potassium hydroxide aqueous solution of 0.5~1.5mol/L.
7. the preparation method of a kind of expanded graphite supporting nanometer pucherite photochemical catalyst according to claim 1 is characterized in that: the sintering temperature in the said step (2) is 180~400 ℃, and roasting time is 2~4h.
CN201110407929.2A 2011-12-09 2011-12-09 Method for preparing expanded graphite load nanometer bismuth vanadate photochemical catalyst Expired - Fee Related CN102489291B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201110407929.2A CN102489291B (en) 2011-12-09 2011-12-09 Method for preparing expanded graphite load nanometer bismuth vanadate photochemical catalyst

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201110407929.2A CN102489291B (en) 2011-12-09 2011-12-09 Method for preparing expanded graphite load nanometer bismuth vanadate photochemical catalyst

Publications (2)

Publication Number Publication Date
CN102489291A true CN102489291A (en) 2012-06-13
CN102489291B CN102489291B (en) 2014-08-13

Family

ID=46181175

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201110407929.2A Expired - Fee Related CN102489291B (en) 2011-12-09 2011-12-09 Method for preparing expanded graphite load nanometer bismuth vanadate photochemical catalyst

Country Status (1)

Country Link
CN (1) CN102489291B (en)

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN105839172A (en) * 2016-04-25 2016-08-10 陕西科技大学 Monoclinic-phase BiVO4/GO (graphene oxide)/RGO (reduced graphene oxide) crystal and preparation method thereof
CN109796059A (en) * 2019-01-29 2019-05-24 山西能源学院 A method of utilizing photocatalysis technology purification of organic waste water
CN110252382A (en) * 2019-06-28 2019-09-20 华南理工大学 A kind of composite photo-catalyst of basic salt of bismuth-containing and preparation method thereof
CN113351222A (en) * 2021-06-23 2021-09-07 湖北民族大学 Bismuth vanadate and manganese dioxide magnetic composite photocatalysis-oxidizing agent and preparation method thereof

Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101857222A (en) * 2010-05-28 2010-10-13 常州大学 Preparation method of large-area and continuous graphen/zinc oxide composite structure
CN102125832A (en) * 2011-01-19 2011-07-20 南京理工大学 Visible light responsive pucherite-graphene composite photocatalyst and preparation method thereof
CN102157315A (en) * 2011-03-21 2011-08-17 福州大学 Emitting cathode based on composite material of graphene/zinc oxide nanowire and preparation of same

Patent Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101857222A (en) * 2010-05-28 2010-10-13 常州大学 Preparation method of large-area and continuous graphen/zinc oxide composite structure
CN102125832A (en) * 2011-01-19 2011-07-20 南京理工大学 Visible light responsive pucherite-graphene composite photocatalyst and preparation method thereof
CN102157315A (en) * 2011-03-21 2011-08-17 福州大学 Emitting cathode based on composite material of graphene/zinc oxide nanowire and preparation of same

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN105839172A (en) * 2016-04-25 2016-08-10 陕西科技大学 Monoclinic-phase BiVO4/GO (graphene oxide)/RGO (reduced graphene oxide) crystal and preparation method thereof
CN109796059A (en) * 2019-01-29 2019-05-24 山西能源学院 A method of utilizing photocatalysis technology purification of organic waste water
CN110252382A (en) * 2019-06-28 2019-09-20 华南理工大学 A kind of composite photo-catalyst of basic salt of bismuth-containing and preparation method thereof
CN110252382B (en) * 2019-06-28 2020-08-18 华南理工大学 Bismuth-containing basic salt composite photocatalyst and preparation method thereof
CN113351222A (en) * 2021-06-23 2021-09-07 湖北民族大学 Bismuth vanadate and manganese dioxide magnetic composite photocatalysis-oxidizing agent and preparation method thereof

Also Published As

Publication number Publication date
CN102489291B (en) 2014-08-13

Similar Documents

Publication Publication Date Title
EP3885039A1 (en) Graphite-like carbon nitride doped modified microsphere catalyst, and preparation method therefor and application thereof
CN102500356A (en) Preparation method for carbon nanotube-nano-bismuth vanadate composite photocatalyst
CN106076335B (en) A kind of preparation method and application of heterogeneous Fenton catalyst
CN103752268B (en) The filter core preparation method and application of heavy metal and arsenic, fluorine in absorption drinking water
CN102068998B (en) Preparation and application methods of BiOBr/BiOCl compound photocatalyst
CN102489290A (en) Preparation method of nano bismuth vanadate photocatalyst loaded on active carbon fiber
CN105727901B (en) A kind of preparation method of optically catalytic TiO 2 sorbing material
CN101862662B (en) Multi-doped half-load type Fenton-assisting titanium dioxide photochemical catalyst as well as preparation method and application method
CN101244383A (en) Process for producing absorbent charcoal loading titanium dioxide photocatalyst
CN103464122B (en) A kind of preparation method of graphene/chitosan adsorbent resin
CN104475131B (en) Visible light response type nanosheet bismuth oxychloride catalyst and preparation method thereof
CN104525173B (en) A kind of CNT composite Ti O2the preparation method of green deep water treatment agent
CN102513091A (en) Preparation method for graphene self-assembled nanometer bismuth vanadate photocatalyst
CN105964248A (en) Preparation method of coal ash microsphere loaded modified nanometer titanium dioxide composite photocatalyst
CN102489291B (en) Method for preparing expanded graphite load nanometer bismuth vanadate photochemical catalyst
CN107413364A (en) A kind of preparation method and applications of hollow mesoporous titanium dioxide of core-shell structure coated graphite phase carbon nitride composite photo-catalyst
CN104624211A (en) Preparation method of complex photocatalyst responsive to visible light and application of complex photocatalyst
CN109046466A (en) A kind of photochemical catalyst and its preparation method and application that the derivative carbon-based material of ZIF-8 is CdS-loaded
CN106964333B (en) Rare earth supported catalyst for treating sewage, preparation method and application thereof, and method for treating sewage by catalytic oxidation of ozone
CN101780416B (en) Iron and chrome co-doped nano titanium dioxide/zeolite compound photocatalyst and preparation method thereof
CN109499563A (en) A kind of preparation method of zinc oxide-active carbon composite catalyst
CN107684926B (en) Photocatalyst for treating dye in high-salinity wastewater and preparation method thereof
CN110102327A (en) A kind of defect carbonitride coupling pucherite catalysis material and preparation method thereof and purposes
CN103301866B (en) A kind of preparation method of nano-silicon aluminum pipe load nitrogen-doped titanium dioxide
CN108393083A (en) A kind of bismuth vanadate photocatalyst and preparation method for sewage disposal

Legal Events

Date Code Title Description
C06 Publication
PB01 Publication
C10 Entry into substantive examination
SE01 Entry into force of request for substantive examination
C14 Grant of patent or utility model
GR01 Patent grant
CB03 Change of inventor or designer information
CB03 Change of inventor or designer information

Inventor after: Gu Yongxing

Inventor after: Li Hao

Inventor after: Liu Baojiang

Inventor after: Gao Pin

Inventor before: Li Hao

Inventor before: Liu Baojiang

Inventor before: Gao Pin

CF01 Termination of patent right due to non-payment of annual fee
CF01 Termination of patent right due to non-payment of annual fee

Granted publication date: 20140813

Termination date: 20181209