CN103418340A - Reduction-oxidation graphene-Fe3O4 nano composite, preparation method thereof, and application of reduction-oxidation graphene-Fe3O4 nano composite in absorbing bisphenol A - Google Patents

Reduction-oxidation graphene-Fe3O4 nano composite, preparation method thereof, and application of reduction-oxidation graphene-Fe3O4 nano composite in absorbing bisphenol A Download PDF

Info

Publication number
CN103418340A
CN103418340A CN2013102875319A CN201310287531A CN103418340A CN 103418340 A CN103418340 A CN 103418340A CN 2013102875319 A CN2013102875319 A CN 2013102875319A CN 201310287531 A CN201310287531 A CN 201310287531A CN 103418340 A CN103418340 A CN 103418340A
Authority
CN
China
Prior art keywords
redox graphene
nano composite
composite material
bisphenol
graphene
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
CN2013102875319A
Other languages
Chinese (zh)
Other versions
CN103418340B (en
Inventor
程欲晓
周宇艳
杨娟
沈劼
强音
鲜跃仲
张仪轩
陈宁宁
李冰玉
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.)
INDUSTRIAL PRODUCTS AND RAW MATERIALS INSPECTION TECHNOLOGY CENTER OF SHANGHAI ENTRY-EXIT INSPECTION AND QUARANTINE BUREAU
East China Normal University
Original Assignee
INDUSTRIAL PRODUCTS AND RAW MATERIALS INSPECTION TECHNOLOGY CENTER OF SHANGHAI ENTRY-EXIT INSPECTION AND QUARANTINE BUREAU
East China Normal 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 INDUSTRIAL PRODUCTS AND RAW MATERIALS INSPECTION TECHNOLOGY CENTER OF SHANGHAI ENTRY-EXIT INSPECTION AND QUARANTINE BUREAU, East China Normal University filed Critical INDUSTRIAL PRODUCTS AND RAW MATERIALS INSPECTION TECHNOLOGY CENTER OF SHANGHAI ENTRY-EXIT INSPECTION AND QUARANTINE BUREAU
Priority to CN201310287531.9A priority Critical patent/CN103418340B/en
Publication of CN103418340A publication Critical patent/CN103418340A/en
Application granted granted Critical
Publication of CN103418340B publication Critical patent/CN103418340B/en
Expired - Fee Related legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Images

Abstract

The invention discloses a reduction-oxidation graphene-Fe3O4 nano composite, a preparation method thereof, and an application of the reduction-oxidation graphene-Fe3O4 nano composite in absorbing bisphenol A. The reduction-oxidation graphene-Fe3O4 nano composite comprises Fe3O4 nano particles and reduction-oxidation graphene. The reduction-oxidation graphene-Fe3O4 nano composite and a solution containing the bisphenol A are in full contact in an ambient temperature, the bisphenol A is absorbed and removed. Compared with the prior art, the advantages of small material dose, simplicity in operation, mild processing condition, fast processing speed, and no harm for the environment, and recycling nano-composite materials, and the like are achieved.

Description

Redox graphene-Fe 3O 4Nano composite material and preparation method thereof, and absorption bisphenol-A application
Technical field
The invention belongs to nanometer technology and water-treatment technology field, relate to a kind of redox graphene (rGO)-Fe 3O 4Nano composite material and preparation method thereof, with and the application in bisphenol-A in absorption.
Background technology
Bisphenol-A ((CH 3) 2C(C 6H 4OH) 2, BPA) be used as raw material and the additive of industrial production Merlon, epoxy resin and other plastics.Recent years, BPA can imitate estrogen as a kind of endocrine interferon (EDCs), and human and animal's health is caused negative impact and caused both at home and abroad very large concern and report.Even report points out that, under the low dosage of part per trillion, BPA also may cause tumour, inborn defect, maldevelopment.BPA in environment water is mainly from the discharge of municipal sewage and trade effluent, closely bound up with our daily life.Because BPA can't carry out biodegradation and chemical degradation, also difficulty is larger [, in the urgent need to developing fast, effectively, processing method cheaply, prevent its contaminated environment.
The processing method that BPA is traditional mainly comprises the technology such as absorption, solvent extraction, film separation and light degradation.Wherein, adsorption technology is processed means because the advantages such as it is simple to operate, efficiency is high, applicability is strong are considered to effective BPA.Carbonaceous material has very large specific area, and BPA is had to very strong adsorption capacity, as activated carbon, CNT all have been reported, is applied to the BPA adsorption treatment.
Graphene is a kind of emerging Two-dimensional Carbon material, has the specific area of excellent electric conductivity, mechanical strength, toughness and superelevation.The derivative of Graphene, as redox graphene (rGO) and functionalization graphene show good performance in fields such as catalysis, capacitor, photoelectric material, adsorbents.Owing between the local π on Graphene surface-electron system energy and phenyl ring, forming pi-pi accumulation, so Graphene has more advantage as adsorbent in the processing of organic dyestuff, agricultural chemicals, aldehydes matter.Recently, have been reported and adopt Graphene absorption BPA absorption, pi-pi accumulation effect and hydrogen bond action section are conducive to BPA and are adsorbed by Graphene.Yet, use on a large scale Graphene can have the difficult problem of separating and regenerating as adsorbent, therefore need exploitation efficiently cheap, be easy to regeneration and the graphene composite material separated.
Summary of the invention
For overcoming the above-mentioned existing problems of prior art, the present invention innovates and proposes a kind of redox graphene (rGO)-Fe 3O 4Nano composite material and preparation method thereof, and this redox graphene (rGO)-Fe 3O 4The application of nano composite material in the absorption bisphenol-A.
The present invention proposes a kind of redox graphene-Fe 3O 4Nano composite material, described redox graphene-Fe 3O 4Nano composite material comprises Fe 3O 4Nano particle and redox graphene; Wherein, described Fe 3O 4Nano particle is evenly dispersed in described redox graphene surface, and described graphene-structured is scraps of paper shape.
Redox graphene-Fe of the present invention 3O 4The saturation magnetization of nano composite material is 36-51emug -1.Preferably, saturation magnetization is 36emug -1Left and right.
Redox graphene-Fe of the present invention 3O 4In nano composite material, described Fe 3O 4The average diameter of nano particle is 8-15nm.Preferably, Fe 3O 4The average diameter of nano particle is the 10nm left and right.
Redox graphene-Fe of the present invention 3O 4Nano composite material, introduce Fe on the redox graphene surface 3O 4Nano particle can bring into play the easy advantage of separating of the high absorption capacity of redox graphene and magnetic material, and the existence of redox graphene can reduce Fe effectively simultaneously 3O 4The reunion of nano particle.Compared with prior art, redox graphene-Fe of the present invention 3O 4Nano composite material has high-specific surface area and magnetic responsiveness, and bisphenol-A (BPA) is had to good absorption property.Adsorbent based on magnetic Nano material just can be separated simply and be regenerated by externally-applied magnetic field, and without centrifugal or filtration, therefore, by externally-applied magnetic field, composite of the present invention can carry out Magnetic Isolation and cycling and reutilization easily.
The invention allows for a kind of redox graphene-Fe 3O 4The preparation method of nano composite material, be scattered in the redox Graphene in redistilled water through ultrasonic, adds hydrazine hydrate and ammonia spirit, obtain finely dispersed solution after stirring, reflux in 50-100 ℃ of oil bath, through centrifugal, vacuum drying, make redox graphene; By aforementioned redox graphene, FeCl 24H 2O, FeCl 3Be dispersed in redistilled water, add sodium hydrate regulator solution pH value to 11-12, be heated to 80 ℃ and stirring, through the distilled water washing, obtain purpose product redox graphene-Fe 3O 4Nano composite material.
In preparation method of the present invention, described redox graphene, FeCl 24H 2O, FeCl 3With ratio 1: 0.5~1.5: 1.5~3.0, be scattered in redistilled water.Preferably, described redox graphene, FeCl 24H 2O, FeCl 3Ratio be 200: 172: 281.
The invention allows for redox graphene-Fe 3O 4The application of nano composite material in the absorption bisphenol-A.Particularly, redox graphene-Fe of the present invention 3O 4Nano composite material can be used for bisphenol-A contained in adsorbent solution (BPA), for example, and for the bisphenol-A of the solution such as adsorbed water, milk, beverage.The present invention has proposed redox graphene-Fe with innovating first 3O 4Nanocomposite applications is in the absorption bisphenol-A.
In the present invention's application, utilize redox graphene-Fe 3O 4The method of nano composite material absorption bisphenol-A, for example, for the BPA of adsorbed water body.By redox graphene-Fe of the present invention 3O 4Nano composite material is positioned in the solution containing bisphenol-A, at room temperature stirs 2-6 hour, makes redox graphene-Fe 3O 4Nano composite material fully contacts with this solution, for example, fully stirs contact 2 hours or 6 hours, fully to adsorb bisphenol-A.This composite has high-specific surface area and magnetic responsiveness, and bisphenol-A in water body (BPA) is had to good absorption property.Then, the redox graphene-Fe of bisphenol-A will fully have been adsorbed by the magnetic separate mode 3O 4Nano composite material is separated from solution, for example, adopts externally-applied magnetic field to be separated nano composite material.After absorption, the content of bisphenol A in solution greatly reduces.Fully, after absorption, can realize removing the effect of bisphenol-A in solution.Redox graphene-Fe of the present invention 3O 4BPA in the effective adsorption aqueous solution of nano composite material energy-absorbing and the mode that can separate by magnetic are carried out cycling and reutilization.
In the present invention's application, the pH of the described solution containing bisphenol-A is adjusted to 2-8.Utilizing redox graphene-Fe 3O 4In the method for nano composite material absorption bisphenol-A, reaction is carried out at normal temperatures and pressures.Solution can be the various solution such as water, milk, beverage, unrestricted.
In the present invention's application, further, can utilize methyl alcohol, acetone equal solvent, the redox graphene-Fe that has adsorbed bisphenol-A obtained after separating by magnetic field 3O 4Nano composite material is carried out desorption and regeneration, then be positioned over containing in the solution of bisphenol-A with absorption bisphenol-A.Redox graphene-Fe of the present invention 3O 4Nano composite material can be repeated multiple times for adsorbing bisphenol-A, thereby realize the cycling and reutilization effect.
The present invention has that material usage is few, simple to operate, treatment conditions are gentle, it is quick to process, environmentally safe harmless, the advantage such as nano material can be recycled.Beneficial effect of the present invention comprises: redox graphene-Fe of the present invention 3O 4Nano composite material is to the bisphenol-A advantages of good adsorption effect, and sorbing material has high-specific surface area, and BPA is had to very strong adsorption capacity, and time of equilibrium adsorption is short.The preparation of nano material of the present invention is simple, is easy to control and operation.Nano material has high magnetic responsiveness, and the magnetic nanometer composite material after the present invention's absorption carries out Separation of Solid and Liquid by externally-applied magnetic field, and whole process rapidly and efficiently.The present invention can realize the recycling of resource, and the magnetic nanometer composite material after absorption can be recycled after regeneration.
The accompanying drawing explanation
Redox graphene-Fe that Fig. 1 is embodiment 1 3O 4The hysteresis graph of nano composite material.
Redox graphene-Fe that Fig. 2 is embodiment 1 3O 4The transmission electron microscope figure of nano composite material.
Redox graphene-Fe that Fig. 3 is embodiment 1 3O 4The scanning electron microscope diagram of nano composite material.
The sorption reaction time that Fig. 4 is embodiment 2 and bisphenol-A clearance change curve.
Fig. 5 is redox graphene-Fe of the present invention 3O 4Nano composite material recycles number of times and adsorption capacity changes schematic diagram.
Concrete embodiment
In conjunction with following specific embodiments and the drawings, the present invention is described in further detail, and protection content of the present invention is not limited to following examples.Under the spirit and scope that do not deviate from inventive concept, variation and advantage that those skilled in the art can expect all are included in the present invention, and take appending claims as protection domain.Implement process of the present invention, condition, reagent, experimental technique etc., except the following content of mentioning specially, be universal knowledege and the common practise of this area, the present invention is not particularly limited content.
Redox graphene-Fe of the present invention 3O 4The preparation method of nano composite material comprises: graphene oxide is scattered in redistilled water through ultrasonic, adds hydrazine hydrate and ammonia spirit, obtain finely dispersed solution after stirring, reflux in 50-100 ℃ of oil bath, through centrifugal, vacuum drying, make redox graphene; By 200mg redox graphene, 172.2mg FeCl 24H 2O and 280.95mg FeCl 3Be dissolved in the 200ml deionized water, then add 1.5mLNaOH (10molL -1), the final pH of system is controlled at 11-12, then mechanical agitation 1 hour under the condition of 80 ℃.The gained sediment carries out Magnetic Isolation, and vacuum drying again after washing obtains redox graphene-Fe 3O 4Nano composite material.
Utilize redox graphene-Fe of the present invention 3O 4The waste water that nano composite material is processed containing bisphenol-A adsorbs bisphenol-A, particularly, with distilled water configuration 20mg/L bisphenol-A solutions simulate waste water solution, gets 10mg Graphene-Fe 3O 4Nano composite material (rGO-MNPs) is dispersed in as adsorbent in the BPA solution of 20mg/L of 50mL, after stirring at room 2-6 hour, with magnet by this nano material absorption migration out, calculates the clearance of bisphenol-A in solution and reaches 95% left and right.
Utilize redox graphene-Fe 3O 4Nano composite material absorption, containing bisphenol-A, further, is carried out redox graphene-Fe 3O 4Nano composite material regeneration: the redox graphene-Fe that will adsorb bisphenol-A 3O 4Nano composite material, with after deionized water washing one time, adds 10mL methyl alcohol, and concussion 30min finally, with deionized water washing 2-3 time, can come into operation in oven for drying again.Redox graphene-Fe 3O 4After nano composite material again drops into and recycles 5 times, its adsorption capacity still can keep 95% original left and right.
Embodiment 1:
Redox graphene is scattered in redistilled water through ultrasonic, adds hydrazine hydrate and ammonia spirit, obtains finely dispersed solution after stirring, in 50-100 ℃ of oil bath, refluxes, and through centrifugal, vacuum drying, makes redox graphene; By the 200mg redox graphene, 172.2mg FeCl 24H 2O and 280.95mg FeCl 3Be dissolved in the 200ml deionized water, then add 1.5mL NaOH (10molL -1), the final pH of reaction system is controlled at 11-12, and then mechanical agitation 1 hour under the condition of 80 ℃, be precipitated thing.The gained sediment carries out Magnetic Isolation, and vacuum drying again after washing obtains redox graphene-Fe 3O 4Nano composite material, its saturation magnetization is 36emu g -1, as shown in Figure 1.The redox graphene structure is scraps of paper shape, Fe 3O 4Nano particle is evenly dispersed in Graphene surface, Fe 3O 4The average diameter of nano particle is the 10nm left and right, and as shown in Figure 2, transmission electron microscope picture as shown in Figure 3 for its scanning electron microscope (SEM) photograph.
Embodiment 2:
Get the waste water solution of 50mL containing 20mg/L BPA, pH=2-8, add 10mg redox graphene-Fe therein 3O 4Nano composite material, at stirring at room absorption certain hour, as 6 hours.With magnet, nano composite material is removed, detect the content of bisphenol A in the rear solution of absorption, calculate bisphenol-A clearance in solution.As shown in Figure 4, along with the increase in processing time, in solution, the clearance of bisphenol-A raises gradually for bisphenol-A clearance and processing time change curve, and in the 2h left and right, its absorption reaches balance, and the clearance of bisphenol-A reaches 96% left and right.
Embodiment 3:
Redox graphene-the Fe of bisphenol-A will have been adsorbed 3O 4Nano composite material, with after deionized water washing one time, adds 10mL methyl alcohol, and concussion 30min finally, with deionized water washing 2-3 time, can come into operation in the absorption of bisphenol-A in oven for drying, with reference to the application process of embodiment 2 again.Redox graphene-Fe after regeneration 3O 4After nano composite material recycles 5 times, it is original 95% that its adsorption capacity still can keep, and recycles number of times on the impact of BPA adsorption capacity as shown in Figure 5.

Claims (9)

1. a redox graphene-Fe 3O 4Nano composite material, is characterized in that, described redox graphene-Fe 3O 4Nano composite material comprises Fe 3O 4Nano particle and redox graphene, wherein, described Fe 3O 4Nano particle is evenly dispersed in described redox graphene surface, and described redox graphene structure is scraps of paper shape, described Fe 3O 4The average diameter of nano particle is 8-15nm; Described redox graphene-Fe 3O 4The saturation magnetization of nano composite material is 36-51emug -1.
2. redox graphene-Fe as claimed in claim 1 3O 4Nano composite material, is characterized in that, described Fe 3O 4The average diameter of nano particle is 10nm.
3. redox graphene-Fe as claimed in claim 1 3O 4Nano composite material, is characterized in that, described redox graphene-Fe 3O 4The saturation magnetization of nano composite material is 36emug -1.
4. a redox graphene-Fe 3O 4The preparation method of nano composite material, is characterized in that, graphene oxide is scattered in redistilled water through ultrasonic, add hydrazine hydrate and ammonia spirit, obtain finely dispersed solution after stirring, reflux in 50-100 ℃ of oil bath, through centrifugal, vacuum drying, make redox graphene; By aforementioned redox graphene, FeCl 24H 2O, FeCl 3Be dispersed in redistilled water, add sodium hydrate regulator solution pH value to 11-12, be heated to 80 ℃ and stirring, through the distilled water washing, obtain redox graphene-Fe as claimed in claim 1 3O 4Nano composite material.
5. preparation method as claimed in claim 4, is characterized in that, described redox graphene, FeCl 24H 2O, FeCl 3Ratio be 1: 0.5~1.5: 1.5~3.0.
6. redox graphene-Fe as claimed in claim 1 3O 4The application of nano composite material in the absorption bisphenol-A.
7. application as claimed in claim 6, utilize the bisphenol-A in redox graphene-Fe3O4 nano composite material adsorbent solution, it is characterized in that, described redox graphene-Fe3O4 nano composite material is positioned in the solution containing bisphenol-A, at room temperature stir 2-6 hour, by described redox graphene-Fe3O4 nano composite material absorption bisphenol-A; Separate from solution and separate by magnetic having adsorbed the redox graphene of bisphenol-A-Fe3O4 nano composite material.
8. application as claimed in claim 6, is characterized in that, the pH of the described solution containing bisphenol-A is 2-8.
9. application as claimed in claim 6, is characterized in that, further comprises, utilizes methyl alcohol, acetone solvent, by the redox graphene of absorption bisphenol-A-Fe3O4 nano composite material desorption and regeneration, then is positioned in the solution containing bisphenol-A, with the absorption bisphenol-A.
CN201310287531.9A 2013-07-09 2013-07-09 Reduction-oxidation graphene-Fe3O4 nano composite, preparation method thereof, and application of reduction-oxidation graphene-Fe3O4 nano composite in absorbing bisphenol A Expired - Fee Related CN103418340B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201310287531.9A CN103418340B (en) 2013-07-09 2013-07-09 Reduction-oxidation graphene-Fe3O4 nano composite, preparation method thereof, and application of reduction-oxidation graphene-Fe3O4 nano composite in absorbing bisphenol A

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201310287531.9A CN103418340B (en) 2013-07-09 2013-07-09 Reduction-oxidation graphene-Fe3O4 nano composite, preparation method thereof, and application of reduction-oxidation graphene-Fe3O4 nano composite in absorbing bisphenol A

Publications (2)

Publication Number Publication Date
CN103418340A true CN103418340A (en) 2013-12-04
CN103418340B CN103418340B (en) 2015-06-10

Family

ID=49644026

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201310287531.9A Expired - Fee Related CN103418340B (en) 2013-07-09 2013-07-09 Reduction-oxidation graphene-Fe3O4 nano composite, preparation method thereof, and application of reduction-oxidation graphene-Fe3O4 nano composite in absorbing bisphenol A

Country Status (1)

Country Link
CN (1) CN103418340B (en)

Cited By (13)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN104001495A (en) * 2014-06-06 2014-08-27 河南师范大学 Preparation method of bismuth oxychloride/graphene composite visible light catalyst
CN104237348A (en) * 2014-10-09 2014-12-24 无锡百灵传感技术有限公司 Electrochemical sensor based on graphene modified electrodes
CN104609636A (en) * 2015-02-11 2015-05-13 四川大学 Method for removing endocrine disruptors in water by using iron and manganese double-phase-doped graphene to activate single persulfate
CN104722276A (en) * 2015-04-14 2015-06-24 中国工程物理研究院材料研究所 Magnetic cucurbit urils/grapheme oxide composite material and preparation method thereof
CN105413663A (en) * 2016-01-07 2016-03-23 南京医科大学 Bisphenol A adsorption material and preparation method and application thereof
CN105688813A (en) * 2016-03-07 2016-06-22 西北工业大学 Magnetic graphene adsorbing material for adsorbing phosphorus in water, preparation method and adsorption method
CN105802579A (en) * 2016-04-06 2016-07-27 华南师范大学 Nano Fe3O4/graphene composite material with high saturation magnetization and electromagnetic shielding function as well as preparation method of composite material
CN108212107A (en) * 2018-01-10 2018-06-29 上海应用技术大学 A kind of preparation method of redox graphene-beta-cyclodextrin sorbing material of magnetism
CN108602677A (en) * 2016-01-12 2018-09-28 正道石墨烯科技有限公司 Nano-particle/porous graphene compound, its synthetic method and application
CN108837799A (en) * 2018-06-05 2018-11-20 中国科学院兰州化学物理研究所 It is a kind of can Magnetic Isolation ferroso-ferric oxide/phosphorylation graphene composite nano material and its application
CN110193345A (en) * 2019-05-05 2019-09-03 淮海工学院 A kind of preparation method of magnetic nanometer composite material
CN112850691A (en) * 2021-01-07 2021-05-28 焦作大学 Graphene modified material, preparation method and application
CN113398949A (en) * 2021-08-16 2021-09-17 广西大学 Magnetic reduction graphene oxide/silver tungstate composite photocatalyst and preparation method and application thereof

Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102500133A (en) * 2011-10-15 2012-06-20 东南大学 Application method of graphene sponge
US20120168383A1 (en) * 2010-12-29 2012-07-05 Korea Institute Of Science And Technology Graphene-iron oxide complex and fabrication method thereof
CN102553593A (en) * 2012-01-10 2012-07-11 常州大学 Method for preparing magnetic nanometer ferroferric oxide-graphene composite catalyst
CN102977247A (en) * 2012-12-12 2013-03-20 天津工业大学 Preparation method of magnetic functionalized graphene oxide based molecularly imprinted hybrid material
CN103127907A (en) * 2011-12-05 2013-06-05 中国科学技术大学 Nanometer adsorption material and preparation method thereof

Patent Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US20120168383A1 (en) * 2010-12-29 2012-07-05 Korea Institute Of Science And Technology Graphene-iron oxide complex and fabrication method thereof
CN102500133A (en) * 2011-10-15 2012-06-20 东南大学 Application method of graphene sponge
CN103127907A (en) * 2011-12-05 2013-06-05 中国科学技术大学 Nanometer adsorption material and preparation method thereof
CN102553593A (en) * 2012-01-10 2012-07-11 常州大学 Method for preparing magnetic nanometer ferroferric oxide-graphene composite catalyst
CN102977247A (en) * 2012-12-12 2013-03-20 天津工业大学 Preparation method of magnetic functionalized graphene oxide based molecularly imprinted hybrid material

Non-Patent Citations (3)

* Cited by examiner, † Cited by third party
Title
QIUHUA WU等: "Preparation of a graphene-based magnetic nanocomposite for the extraction of carbamate pesticides from environmental water samples", 《JOURNAL OF CHROMATOGRAPHY A》 *
徐婧等: "氧化石墨烯对水中内分泌干扰物双酚A的吸附性能", 《物理化学学报》 *
邵晓萍等: "共沉淀制备不同粒径Fe3O4纳米颗粒及磁性能的研究", 《功能材料》 *

Cited By (17)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN104001495B (en) * 2014-06-06 2016-09-21 河南师范大学 A kind of preparation method of bismuth oxychloride/Graphene composite visible light catalyst
CN104001495A (en) * 2014-06-06 2014-08-27 河南师范大学 Preparation method of bismuth oxychloride/graphene composite visible light catalyst
CN104237348A (en) * 2014-10-09 2014-12-24 无锡百灵传感技术有限公司 Electrochemical sensor based on graphene modified electrodes
CN104609636A (en) * 2015-02-11 2015-05-13 四川大学 Method for removing endocrine disruptors in water by using iron and manganese double-phase-doped graphene to activate single persulfate
CN104609636B (en) * 2015-02-11 2016-05-11 四川大学 A kind of method of utilizing ferrimanganic two-phase doped graphene to activate incretion interferent in single persulfate removal water
CN104722276A (en) * 2015-04-14 2015-06-24 中国工程物理研究院材料研究所 Magnetic cucurbit urils/grapheme oxide composite material and preparation method thereof
CN104722276B (en) * 2015-04-14 2016-09-28 中国工程物理研究院材料研究所 A kind of melon ring/graphene oxide magnetic composite and preparation method thereof
CN105413663A (en) * 2016-01-07 2016-03-23 南京医科大学 Bisphenol A adsorption material and preparation method and application thereof
CN105413663B (en) * 2016-01-07 2017-10-13 南京医科大学 The sorbing material and preparation method and applications of a kind of bisphenol-A
CN108602677A (en) * 2016-01-12 2018-09-28 正道石墨烯科技有限公司 Nano-particle/porous graphene compound, its synthetic method and application
CN105688813A (en) * 2016-03-07 2016-06-22 西北工业大学 Magnetic graphene adsorbing material for adsorbing phosphorus in water, preparation method and adsorption method
CN105802579A (en) * 2016-04-06 2016-07-27 华南师范大学 Nano Fe3O4/graphene composite material with high saturation magnetization and electromagnetic shielding function as well as preparation method of composite material
CN108212107A (en) * 2018-01-10 2018-06-29 上海应用技术大学 A kind of preparation method of redox graphene-beta-cyclodextrin sorbing material of magnetism
CN108837799A (en) * 2018-06-05 2018-11-20 中国科学院兰州化学物理研究所 It is a kind of can Magnetic Isolation ferroso-ferric oxide/phosphorylation graphene composite nano material and its application
CN110193345A (en) * 2019-05-05 2019-09-03 淮海工学院 A kind of preparation method of magnetic nanometer composite material
CN112850691A (en) * 2021-01-07 2021-05-28 焦作大学 Graphene modified material, preparation method and application
CN113398949A (en) * 2021-08-16 2021-09-17 广西大学 Magnetic reduction graphene oxide/silver tungstate composite photocatalyst and preparation method and application thereof

Also Published As

Publication number Publication date
CN103418340B (en) 2015-06-10

Similar Documents

Publication Publication Date Title
CN103418340B (en) Reduction-oxidation graphene-Fe3O4 nano composite, preparation method thereof, and application of reduction-oxidation graphene-Fe3O4 nano composite in absorbing bisphenol A
Qu et al. Applications of functionalized magnetic biochar in environmental remediation: A review
Xiang et al. Carbon-based materials as adsorbent for antibiotics removal: mechanisms and influencing factors
Ma et al. Hydrothermal synthesis of magnetic sludge biochar for tetracycline and ciprofloxacin adsorptive removal
Zhang et al. Preparation of magnetic polyethylenimine lignin and its adsorption of Pb (II)
Wang et al. Nanomaterials as sorbents to remove heavy metal ions in wastewater treatment
Zhang et al. Nanomaterials-enabled water and wastewater treatment
Monisha et al. Green remediation of pharmaceutical wastes using biochar: a review
Ma et al. Efficient adsorptive removal of fluoroquinolone antibiotics from water by alkali and bimetallic salts co-hydrothermally modified sludge biochar
Bhatia et al. Application of nanoadsorbents for removal of lead from water
CN102718279B (en) Method for removing humic acid pollutants from water by magnetic polyaniline adsorbent
Liu et al. Removal of 17β-estradiol from aqueous solution by graphene oxide supported activated magnetic biochar: adsorption behavior and mechanism
Ma et al. One-pot hydrothermal synthesis of magnetic N-doped sludge biochar for efficient removal of tetracycline from various environmental waters
Zare et al. Water decontamination using bio-based, chemically functionalized, doped, and ionic liquid-enhanced adsorbents
CN104059167B (en) A kind of preparation method and applications of polyamine compounds modified magnetic chitosan
CN104475056A (en) Preparation method of clomiphene polymer capable of adsorbing heavy metal ions and application of clomiphene polymer
Li et al. Rapid and efficient adsorption of tetracycline from aqueous solution in a wide pH range by using iron and aminoacetic acid sequentially modified hierarchical porous biochar
Karthikeyan et al. Removal of phosphate and nitrate ions from water by amine crosslinked magnetic banana bract activated carbon and its physicochemical performance
Yang et al. Adsorption behavior of cross-linked chitosan modified by graphene oxide for Cu (II) removal
CN109126743B (en) Preparation method of polyurethane foam adsorption material
Chen et al. Emerging adsorbents for micro/nanoplastics removal from contaminated water: advances and perspectives
Nujić et al. Toxic metal ions in drinking water and effective removal using graphene oxide nanocomposite
Osman et al. Advanced adsorbents for ibuprofen removal from aquatic environments: a review
Cao et al. Strong adsorption and high stability of the thin-layered MXene adsorbent: Simple synthesis and application to reduce the toxicity of wastewater towards mung beans
Ibrahim et al. Outlook on the carbon-based materials for heavy metal removal

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

Granted publication date: 20150610

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