CN109126721A - Magnetic metal organic framework nano material, the preparation method and applications of three-layer nuclear shell structure - Google Patents
Magnetic metal organic framework nano material, the preparation method and applications of three-layer nuclear shell structure Download PDFInfo
- Publication number
- CN109126721A CN109126721A CN201810924858.5A CN201810924858A CN109126721A CN 109126721 A CN109126721 A CN 109126721A CN 201810924858 A CN201810924858 A CN 201810924858A CN 109126721 A CN109126721 A CN 109126721A
- Authority
- CN
- China
- Prior art keywords
- sio
- nano material
- organic framework
- metal organic
- nanometer
- 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
Links
Classifications
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J20/00—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
- B01J20/22—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising organic material
- B01J20/223—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising organic material containing metals, e.g. organo-metallic compounds, coordination complexes
- B01J20/226—Coordination polymers, e.g. metal-organic frameworks [MOF], zeolitic imidazolate frameworks [ZIF]
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J20/00—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
- B01J20/02—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material
- B01J20/06—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising oxides or hydroxides of metals not provided for in group B01J20/04
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J20/00—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
- B01J20/02—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material
- B01J20/10—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising silica or silicate
- B01J20/103—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising silica or silicate comprising silica
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J20/00—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
- B01J20/28—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof characterised by their form or physical properties
- B01J20/28002—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof characterised by their form or physical properties characterised by their physical properties
- B01J20/28009—Magnetic properties
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J20/00—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
- B01J20/28—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof characterised by their form or physical properties
- B01J20/28014—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof characterised by their form or physical properties characterised by their form
- B01J20/28016—Particle form
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/28—Treatment of water, waste water, or sewage by sorption
- C02F1/281—Treatment of water, waste water, or sewage by sorption using inorganic sorbents
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/28—Treatment of water, waste water, or sewage by sorption
- C02F1/285—Treatment of water, waste water, or sewage by sorption using synthetic organic sorbents
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/28—Treatment of water, waste water, or sewage by sorption
- C02F1/288—Treatment of water, waste water, or sewage by sorption using composite sorbents, e.g. coated, impregnated, multi-layered
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2101/00—Nature of the contaminant
- C02F2101/30—Organic compounds
- C02F2101/308—Dyes; Colorants; Fluorescent agents
Abstract
The invention discloses magnetic metal organic framework nano material, the preparation method and applications of a kind of three-layer nuclear shell structure.The method is first by Fe3O4@SiO2Particle carries out hydroxylating modification, obtains nanometer Fe3O4@SiO2- OH particle, then surface amination are modified to obtain nanometer Fe3O4@SiO2‑NH2Then particle is connect with Zn-MOF, finally obtain the magnetic metal organic framework nano material Fe of three-layer nuclear shell structure3O4@SiO2@Zn-MOF.The magnetic metal organic framework nano material of three-layer nuclear shell structure prepared by the present invention can be used for the absorption of organic dyestuff in water, it is good to Congo red and methylene blue adsorption effect, Congo red removal rate reaches 100% under the conditions of pH=5, methylene blue removal rate reaches 75% or more under the conditions of pH=7, the adsorbent material can be recycled easily by externally-applied magnetic field, effectively realize the reuse of material.
Description
Technical field
The present invention relates to a kind of magnetic metal organic framework nano material of three-layer nuclear shell structure, preparation method and its rigid
Application in arnotto and methylene blue adsorption number processing, belongs to adsorbent material technical field.
Background technique
Fe3O4It is extremely unstable in acidic environment as a kind of common magnetic material, it is easy to lose original magnetism,
Therefore it needs in Fe3O4Surface carries out coating modification.Wherein silica coats Fe as a kind of common cladding substance3O4It can
To form hud typed Fe3O4@SiO2Compound particle, to Fe3O4Form protection.Generally use solvent-thermal method preparation Fe3O4, in room temperature
Lower addition tetraethyl orthosilicate stirring preparation Fe3O4@SiO2.The Fe of preparation3O4@SiO2Compound particle surface is meso-hole structure, can
To remove water pollutant as adsorbent.According to reported document, Fe at present3O4@SiO2And its derivative is as adsorbent
It is already used to absorbing heavy metal ions in water Cu, methylene blue and malachite green etc., but their adsorption effect is all paid no attention to
Think.
Congo red and methylenum careuleum is two kinds of common dyestuffs.Congo red (CR) is a kind of common secondary diazo colours, it
Waste water mainly from textile, printing and dyeing, paper, rubber, plastics industry etc..Congo red derivative naphthalenedicarboxylic acid and metabolite
Benzidine may result in disease, and Congo red stable structure, it is difficult to which biodegrade not directly enters biochemical treatment system
Processing.Adsorbent currently used for removing Congo red has clay mineral (Evaluation of D113 cation exchange
resin for the removal of Eu(III)from aqueous solution,J.Rare Earth 28(2010)
862-867), oxide (Enhanced immobilization of ReO4-by nanoscale zerovalent iron
supported on layered double hydroxide via an advanced XAFS approach:
implications for TcO4_ sequestration, Appl.Catal.B-Environ.192 (2016) 268-276) and
Carbon nanomaterial (Naphthalene adsorption and desorption from aqueous C60fullerene,
J.Chem.Eng.Date 49(2004)675–683).Methylene blue (MB) is used as a kind of phenthazine salt, can be used for cotton, timber
With the dyeing of silk, but it is harmful to the human body.It is existing for remove the adsorbent material of methylene blue to include natural polymer, such as
Cellulose (Modified pineapple peel cellulose hydrogels embedded with sepia ink
For effective removal of methylene blue, Carbohydr.Polym.148 (2016) 1-10) and shell it is poly-
Sugar (CS) (Highly enhanced adsorption of congo red onto graphene oxide/chitosan
fibers by wet-chemical etching off silica nanoparticles,Chem.Eng.J.245(2014)
99-106), carbonaceous material (Coal based magnetic activated carbon as a high performance
Adsorbent for methylene blue, J.Porous Mater.23 (2016) 877-884), zeolite (Promoted
dye adsorption performance over desilicated natural zeolite,Microporous
Mesoporous Mater.145 (2011) 157-164.) etc..But there are some disadvantages for the above method, if any the generation of by-product
Cause secondary pollution;Dyestuff degradation rate is not high;It cannot be recycled, effective, quick, green, efficient requirement is not achieved.
Summary of the invention
The purpose of the present invention is to provide a kind of magnetic metal organic framework nano materials of three-layer nuclear shell structure, preparation side
Method and its adsorbing the application in Congo red and methylene blue.
To achieve the above object, technical scheme is as follows:
The preparation method of the magnetic metal organic framework nano material of three-layer nuclear shell structure, includes the following steps:
Step 1, nanometer Fe3O4@SiO2Surface functional group modification:
Fe3O4@SiO2Particle carries out hydroxylating modification: by nanometer Fe3O4@SiO2Particle and dodecyl sodium sulfate are added to
In water, ultrasonic disperse is uniform, is stirred to react, and after reaction, second alcohol and water alternately washs, and is drying to obtain nanometer Fe3O4@SiO2-
OH particle;
Nanometer Fe3O4@SiO2Surface amination modification: by nanometer Fe3O4@SiO2- OH particle and 3- aminopropyl trimethoxy silicon
Alkane (APTMS) is added in ethyl alcohol, is stirred to react, and after reaction, ethanol washing is drying to obtain nanometer Fe3O4@SiO2-NH2
Particle;
Step 2, nanometer Fe3O4@SiO2-NH2The metal organic framework nano material (Zn-MOF) of particle and Zn connection: will
Nanometer Fe3O4@SiO2-NH2Particle, the metal organic framework nano material (Zn-MOF) of Zn, 1- (3- dimethylamino-propyl) -3-
Ethyl-carbodiimide hydrochloride (EDC) and n-hydroxysuccinimide (NHS) are added to the water, and are stirred to react, after reaction,
It is alternately washed with second alcohol and water, is drying to obtain the magnetic metal organic framework nano material Fe of three-layer nuclear shell structure3O4@SiO2@
Zn-MOF。
Preferably, in step 1, the nanometer Fe3O4@SiO2Mass particle, dodecyl sodium sulfate quality, water body
Product is than being 0.1~0.3:0.3-~0.4:70~80, g:g:mL.
Preferably, in step 1, the ultrasonic time is 10~20min.
Preferably, in step 1, the mixing time is 3.5~4.5h, 1 hour 10~20min of ultrasound of every stirring.
Preferably, in step 2, the nanometer Fe3O4@SiO2-NH2The metal organic framework nanometer material of mass particle, Zn
Expect (Zn-MOF) quality, 1- (3- dimethylamino-propyl) -3- ethyl-carbodiimide hydrochloride quality (EDC), N- hydroxysuccinimidyl acyl
Imines quality (NHS) quality, the volume ratio of water are 0.2~0.4:0.5~0.7:70~80:50~55:65~85, g:g:mg:
mg:mL。
Preferably, in step 2, mixing time is 40~80min.
The present invention also provides the magnetic metal organic framework nanometers for the three-layer nuclear shell structure that above-mentioned preparation method is prepared
Material.
Further, the magnetic metal organic framework nano material that the present invention provides above-mentioned three-layer nuclear shell structure is containing
Application in Congo red and/or methylene blue waste water adsorption treatment, includes the following steps:
The magnetic metal organic framework nano material of three-layer nuclear shell structure is added to containing Congo red and/or methylene blue
Waste water in, adjust pH value be 5~7.
Preferably, the adsorption time is 20~60min.
Compared with prior art, the invention has the following advantages that
The magnetic metal organic framework nano material of three-layer nuclear shell structure of the invention, wherein metal-organic framework materials
(Zn-MOF) it is evenly coated at magnetic material Fe3O4@SiO2On, core@shell@shell three-decker is formed, to Congo red and methylene blue
Adsorption effect it is good, Congo red removal rate reaches methylene blue removal rate under the conditions of 100%, pH=7 under the conditions of pH=5
Reach 75% or more.
Detailed description of the invention
Fig. 1 is the magnetic metal organic framework nano material Fe of three-layer nuclear shell structure3O4@SiO2@Zn-MOF synthesis flow shows
It is intended to.
Fig. 2 is Fe3O4、Fe3O4@SiO2And Fe3O4@SiO2-NH2Infrared spectrum, a.Fe3O4;b.Fe3O4@SiO2;
c.Fe3O4@SiO2-NH2。
Fig. 3 is Fe3O4@SiO2The scanning electron microscope and transmission electron microscope picture of@Zn-MOF.
Fig. 4 is adsorbent mass and Congo red and methylene blue removal rate relationship line chart.
Fig. 5 is adsorption time and Congo red and methylene blue removal rate relationship line chart.
Fig. 6 is pH value and Congo red and methylene blue removal rate relationship line chart.
Fig. 7 is ionic strength and Congo red and methylene blue removal rate relationship line chart.
Specific embodiment
Invention is further described below with reference to embodiment and attached drawing.
The metal organic framework nano material (Zn-MOF) based on Zn in following embodiment prepares bibliography
[Adual functional MOF as a luminescent sensor for quantitatively detecting
The concentration of nitrobenzene and temperature, Chemical Communication 49
(2013) 8964-8966], specific steps are as follows:
Metal organic framework nano material (Zn-MOF) using solvent structure based on Zn, by 0.038g organic ligand
2,4,6- tri- (3,5- dicarboxyphenyi amino) -1,3,5- triazine (H6TDPAT),0.079gZn(NO3)2·6H2O is added to
In the mixed solution of 4mlDMF, 2ml ethylene glycol and 0.5ml water, 30min is stirred, 0.5mL nitric acid is then added, and (DMF of 3.5M is molten
Liquid), after stirring 30min dissolution, it is transferred in reaction kettle and is reacted 3 days at 80 DEG C.Cooled to room temperature is collected by filtration, and uses
DMF is washed and is dried in air, obtains colourless bulk crystals Zn-MOF.
Nanometer Fe in following embodiment3O4@SiO2Particle prepares bibliography [Silica coated
Fe3O4magnetic nanospheres for high removal of organic pollutants from
Wastewater, Chemical Engineering Journal 306 (2016) 280-288], specific steps are as follows:
(1) by 5.2g Iron(III) chloride hexahydrate, 11.5g anhydrous sodium acetate is dissolved in 100ml ethylene glycol, is stirred
0.5h is transferred in reaction kettle after completely dissolution, is reacted 8 hours at 200 DEG C.Solution is fallen from reaction kettle after the reaction was completed
Out, Magneto separate is carried out to solution with magnet, is then alternately washed with water and ethyl alcohol, finally dry nano ferriferrous oxide grain
Son.
(2) 0.2g nano ferriferrous oxide particle is added to 100ml ethyl alcohol, the three necks burning of 30ml water and 1.5ml ammonium hydroxide
In bottle, stirring 0.5h dissolves it sufficiently, then measures 2ml tetraethyl orthosilicate and is added dropwise, stirs 6 hours under room temperature.Instead
Should after solution carry out Magneto separate, then alternately washed with water and ethyl alcohol, finally dry nanometer Fe3O4@SiO2Particle.
The magnetic metal organic framework nano material Fe of three-layer nuclear shell structure of the invention3O4@SiO2The synthesis of@Zn-MOF
Flow chart is as shown in Figure 1.Step 1: preparing core@shell structure Fe3O4@SiO2, and surface functional group modification is carried out to it;Second
Step: preparation Zn-MOF material;Step 3: by the Fe after the resulting modified with functional group of the first step3O4@SiO2Product and second step system
Standby Zn-MOF material is combined, and forms the Fe of final product core@shell@shell three-decker3O4@SiO2@Zn-MOF。
Embodiment 1: the preparation of the magnetic metal organic framework nano material of three-layer nuclear shell structure
(1) nanometer Fe3O4@SiO2Surface functional group modification
Fe3O4@SiO2Surface hydroxylation modification: by 0.2gFe3O4@SiO2, 0.35g dodecyl sodium sulfate is dissolved in 50ml water
In, ultrasonic 15min dissolves it sufficiently, then stirs 4 hours at normal temperature.Each hour takes off ultrasonic 15min. reaction
Solution carries out Magneto separate afterwards, is then alternately washed with water and ethyl alcohol, finally dry product.
Fe3O4@SiO2Surface amination modification: by 0.15gFe3O4@SiO2- OH and 0.66mlAPTMS is dissolved in 75ml ethyl alcohol
In, it is stirred 20 hours under room temperature.Solution carries out Magneto separate after reaction, three times with ethanol washing, then dry product.
Wherein Fe3O4、Fe3O4@SiO2And Fe3O4@SiO2-NH2Infrared spectrum as shown in Fig. 2, Fe3O4、Fe3O4@SiO2With
Fe3O4@SiO2-NH2All in 553cm-1Appearance, this is Fe-O oscillating bond, illustrates that three kinds of particles all have ferroso-ferric oxide particle;
Fe3O4@SiO2And Fe3O4@SiO2-NH2In 1065,946,795cm-1There is absorption peak at place, this is stretching vibration and the change of Si-O key
Shape vibration illustrates coated with silica success;Fe3O4@SiO2-NH21563,1482cm-1There is absorption peak at place, this is amino
Stretching vibration and bending vibration.In 2800-3025cm-1The absorption peak at place then with Fe3O4@SiO2-NH2The flexible vibration of methylene
It moves related.2940,2879cm-1Locate appearance, explanation-NH2In the presence of all proving that amino is successfully connected with the appearance of upward peak.
(2) nanometer Fe3O4@SiO2-NH2The connection of the metal organic framework nano material (Zn-MOF) of particle and Zn
By the amidized Fe of 0.3g3O4@SiO2Particle, 0.6gZn-MOF, 75mgEDC, 52.5mgNHS are dissolved in 75ml water
Stirring one hour.Solution carries out Magneto separate after reaction, is alternately washed with second alcohol and water, then dry product Fe3O4@SiO2@
Zn-MOF.Wherein the metal organic framework nano material (Zn-MOF) of Zn is uniformly coated on amidized Fe3O4@SiO2On, it sweeps
Electronic Speculum and transmission electron microscope are retouched as shown in figure 3, material has apparent three-decker, formation is using ferroso-ferric oxide as core, silica
For second layer shell, the metal organic framework nano material (Zn-MOF) of Zn is the core@shell@shell structure of third layer shell, is more advantageous to
Sample adsorbs in pollutant and Magneto separate.
2. adsorbent mass of embodiment is to the magnetic metal organic framework nano material adsorption effect of three-layer nuclear shell structure
It influences
It is separately added into 20mg, 40mg, 60mg into the Congo red and methylene blue solution that 25ml concentration is 50mg/L,
The magnetic metal organic framework nano material absorbent of the three-layer nuclear shell structure of 80mg, 100mg is adsorbed.As a result such as Fig. 4 institute
Show, with the increase of adsorbent mass, Congo red and methylene blue removal rate all increases.The Congo red removal rate in 60mg is big
Amplitude improves, but as the increase of the increase removal rate of quality is unobvious.Methylene blue with adsorbent mass increase removal rate
Although being promoted, promoted little.The result shows that Congo red and methylene blue be all selected adsorbent quality be 60mg when the most
Properly.
Shadow of 3. adsorption time of embodiment to the magnetic metal organic framework nano material adsorption effect of three-layer nuclear shell structure
It rings
The magnetism of 60mg three-layer nuclear shell structure is added in the Congo red and methylene blue solution that 25ml concentration is 50mg/L
Metal organic framework nano material.Solution supernatant liquor is taken out when reacting 20,30,40,50,60min respectively to be tested.It is real
Test result as shown in figure 5, with adsorption time increase, Congo red and methylene blue removal rate all increases.60min is arrived
When, Congo red and methylene blue removal rate all reaches 80% or more, therefore selects 60min the most suitable for adsorption time.
Influence of the embodiment 4.pH value to the magnetic metal organic framework nano material adsorption effect of three-layer nuclear shell structure
The pH value difference for the Congo red and methylene blue solution that 25ml concentration is 50mg/L is adjusted with hydrochloric acid and sodium hydroxide
It is 3,5,7,9,11.Experimental result substantially achieves 100% as shown in fig. 6, the Congo red removal rate maximum when pH is 5;And it is sub-
Methyl blue is 7 maximum in pH, reaches 75% or more.Therefore the Congo red adsorption effect when pH is 5 is best;Methylene blue is in pH
Adsorption effect is best when 7.
Shadow of 5. ionic strength of embodiment to the magnetic metal organic framework nano material adsorption effect of three-layer nuclear shell structure
It rings
The NaCl of different quality ratio is added into the Congo red and methylene blue solution that 25ml concentration is 50mg/L, adjusts molten
The ionic strength of liquid is 0.01,0.1,1.0mol/L.Experimental result as shown in fig. 7, with NaCl concentration increase, it is Congo red and
The removal rate of methylene blue all declines.Illustrate that prepared adsorbent is larger by effects of ion intensity effect, ionic strength increases
Add and be unfavorable for adsorbent absorption dyestuff, therefore prepared adsorbent is not suitable for the high salinity waste water from dyestuff of processing.Therefore Congo red
It is all best for 0.01mol/L adsorption effect in NaCl concentration with methylene blue.
6. three-layer nuclear shell structure magnetic metal organic framework nano material removal effect of embodiment and Congo red and methylene
The linear relationship of blue concentration
1. ultraviolet specrophotometer condition:
It is measured using standard quartz cuvette, the measurement factor is 1.0, low speed 50nm/cm, scanning speed 240nm/min, light
Source UV+VIS lamp, measurement method are absorbance, response time 1s, optical path 10mm.Congo red absorbing wavelength is 496nm;It is sub-
The absorbing wavelength of methyl blue is 665nm.
The Congo red analysis parameter with methylene blue of table 1.
The results are shown in Table 1, and Congo red and methylene blue the range of linearity is all 10-50mg/L, related coefficient (R2) be situated between
In 0.93-0.99, good linear relationship is shown.
Claims (10)
1. the preparation method of the magnetic metal organic framework nano material of three-layer nuclear shell structure, which is characterized in that including walking as follows
It is rapid:
Step 1, nanometer Fe3O4@SiO2Surface functional group modification:
Fe3O4@SiO2Particle carries out hydroxylating modification: by nanometer Fe3O4@SiO2Particle and dodecyl sodium sulfate are added to water
In, ultrasonic disperse is uniform, is stirred to react, and after reaction, second alcohol and water alternately washs, and is drying to obtain nanometer Fe3O4@SiO2-OH
Particle;
Nanometer Fe3O4@SiO2Surface amination modification: by nanometer Fe3O4@SiO2- OH particle and 3- aminopropyl front three oxosilane add
Enter into ethyl alcohol, be stirred to react, after reaction, ethanol washing is drying to obtain nanometer Fe3O4@SiO2-NH2Particle;
Step 2, nanometer Fe3O4@SiO2-NH2The metal organic framework nano material of particle and Zn connection: by nanometer Fe3O4@SiO2-
NH2Particle, the metal organic framework nano material of Zn, 1- (3- dimethylamino-propyl) -3- ethyl-carbodiimide hydrochloride and N-
HOSu NHS is added to the water, and is stirred to react, and after reaction, is alternately washed with second alcohol and water, is drying to obtain three layers
The magnetic metal organic framework nano material Fe of core-shell structure3O4@SiO2@Zn-MOF。
2. preparation method according to claim 1, which is characterized in that in step 1, the nanometer Fe3O4@SiO2Particle
Quality, dodecyl sodium sulfate quality, the volume ratio of water are 0.1~0.3:0.3-~0.4:70~80, g:g:mL.
3. preparation method according to claim 1, which is characterized in that in step 1, the ultrasonic time be 10~
20min。
4. preparation method according to claim 1, which is characterized in that in step 1, the mixing time be 3.5~
4.5h, 1 hour 10~20min of ultrasound of every stirring.
5. preparation method according to claim 1, which is characterized in that in step 2, the nanometer Fe3O4@SiO2-NH2Grain
Protonatomic mass, the metal organic framework nano material quality of Zn, 1- (3- dimethylamino-propyl) -3- ethyl-carbodiimide hydrochloride matter
Amount, n-hydroxysuccinimide quality quality, the volume ratio of water be 0.2~0.4:0.5~0.7:70~80:50~55:65~
85, g:g:mg:mg:mL.
6. preparation method according to claim 1, which is characterized in that in step 2, mixing time is 40~80min.
7. the magnetic metal for the three-layer nuclear shell structure that preparation method according to any one of claims 1 to 6 is prepared is organic
Skeleton nano material.
8. the magnetic metal organic framework nano material of three-layer nuclear shell structure according to claim 7 is containing Congo red
And/or the application in the waste water adsorption treatment of methylene blue.
9. application according to claim 8, which comprises the steps of:
The magnetic metal organic framework nano material of three-layer nuclear shell structure is added to containing Congo red and/or methylene blue useless
In water, adjusting pH value is 5~7.
10. application according to claim 9, which is characterized in that the adsorption time is 20~60min.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201810924858.5A CN109126721A (en) | 2018-08-14 | 2018-08-14 | Magnetic metal organic framework nano material, the preparation method and applications of three-layer nuclear shell structure |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201810924858.5A CN109126721A (en) | 2018-08-14 | 2018-08-14 | Magnetic metal organic framework nano material, the preparation method and applications of three-layer nuclear shell structure |
Publications (1)
Publication Number | Publication Date |
---|---|
CN109126721A true CN109126721A (en) | 2019-01-04 |
Family
ID=64793067
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CN201810924858.5A Pending CN109126721A (en) | 2018-08-14 | 2018-08-14 | Magnetic metal organic framework nano material, the preparation method and applications of three-layer nuclear shell structure |
Country Status (1)
Country | Link |
---|---|
CN (1) | CN109126721A (en) |
Cited By (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN110028144A (en) * | 2019-02-26 | 2019-07-19 | 华中师范大学 | A kind of multilayered structure defluorinating agent and its preparation method and application |
CN110508252A (en) * | 2019-09-29 | 2019-11-29 | 合肥海关技术中心 | A kind of preparation method of the magnetic metal organic framework material for Adsorption of Mercury |
CN116282338A (en) * | 2023-04-27 | 2023-06-23 | 东华工程科技股份有限公司 | Chemical wastewater treatment agent and preparation method thereof |
Citations (9)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US20070269380A1 (en) * | 2005-10-11 | 2007-11-22 | Washington, University Of | Methotrexate-modified nanoparticles and related methods |
CN103551197A (en) * | 2013-11-11 | 2014-02-05 | 北京化工大学 | Magnetic metal-organic framework material with pocket-channel structure and preparation and reaction for acylation thereof |
CN105597685A (en) * | 2016-01-12 | 2016-05-25 | 郑州轻工业学院 | Preparation method and application of Fe3O4@SiO2@Zr-MOF |
CN105688869A (en) * | 2016-03-21 | 2016-06-22 | 山东省分析测试中心 | Preparation method and application of magnetic metal - organic nanotube material |
CN106582543A (en) * | 2016-12-29 | 2017-04-26 | 郑州大学 | Chiral MOF (Metal-Organic Framework) magnetic graphene functional material, and preparation method and application thereof |
CN106807308A (en) * | 2015-11-30 | 2017-06-09 | 上海交通大学 | A kind of magnetic nano-particle of core shell structure and its preparation and application |
CN106987580A (en) * | 2016-02-29 | 2017-07-28 | 华南理工大学 | A kind of biocompatible metal organic framework material zinc glutamate and its preparation and application |
CN107099524A (en) * | 2017-06-16 | 2017-08-29 | 中国药科大学 | A kind of utilization surface carboxyl groups modification magnetic ball prepares the method that immobilised enzymes screens arimedex |
CN108355611A (en) * | 2018-01-22 | 2018-08-03 | 西北师范大学 | A kind of MOF complexs and its synthesis and application in absorption organic dyestuff in wastewater |
-
2018
- 2018-08-14 CN CN201810924858.5A patent/CN109126721A/en active Pending
Patent Citations (9)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US20070269380A1 (en) * | 2005-10-11 | 2007-11-22 | Washington, University Of | Methotrexate-modified nanoparticles and related methods |
CN103551197A (en) * | 2013-11-11 | 2014-02-05 | 北京化工大学 | Magnetic metal-organic framework material with pocket-channel structure and preparation and reaction for acylation thereof |
CN106807308A (en) * | 2015-11-30 | 2017-06-09 | 上海交通大学 | A kind of magnetic nano-particle of core shell structure and its preparation and application |
CN105597685A (en) * | 2016-01-12 | 2016-05-25 | 郑州轻工业学院 | Preparation method and application of Fe3O4@SiO2@Zr-MOF |
CN106987580A (en) * | 2016-02-29 | 2017-07-28 | 华南理工大学 | A kind of biocompatible metal organic framework material zinc glutamate and its preparation and application |
CN105688869A (en) * | 2016-03-21 | 2016-06-22 | 山东省分析测试中心 | Preparation method and application of magnetic metal - organic nanotube material |
CN106582543A (en) * | 2016-12-29 | 2017-04-26 | 郑州大学 | Chiral MOF (Metal-Organic Framework) magnetic graphene functional material, and preparation method and application thereof |
CN107099524A (en) * | 2017-06-16 | 2017-08-29 | 中国药科大学 | A kind of utilization surface carboxyl groups modification magnetic ball prepares the method that immobilised enzymes screens arimedex |
CN108355611A (en) * | 2018-01-22 | 2018-08-03 | 西北师范大学 | A kind of MOF complexs and its synthesis and application in absorption organic dyestuff in wastewater |
Cited By (6)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN110028144A (en) * | 2019-02-26 | 2019-07-19 | 华中师范大学 | A kind of multilayered structure defluorinating agent and its preparation method and application |
CN110028144B (en) * | 2019-02-26 | 2021-07-20 | 华中师范大学 | Multi-layer structure fluorine removal agent and preparation method and application thereof |
CN110508252A (en) * | 2019-09-29 | 2019-11-29 | 合肥海关技术中心 | A kind of preparation method of the magnetic metal organic framework material for Adsorption of Mercury |
CN110508252B (en) * | 2019-09-29 | 2022-02-25 | 合肥海关技术中心 | Preparation method of magnetic metal organic framework material for adsorbing mercury |
CN116282338A (en) * | 2023-04-27 | 2023-06-23 | 东华工程科技股份有限公司 | Chemical wastewater treatment agent and preparation method thereof |
CN116282338B (en) * | 2023-04-27 | 2023-08-22 | 东华工程科技股份有限公司 | Chemical wastewater treatment agent and preparation method thereof |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
Panda et al. | Magnetite nanoparticles as sorbents for dye removal: a review | |
CN109126721A (en) | Magnetic metal organic framework nano material, the preparation method and applications of three-layer nuclear shell structure | |
CN105879842B (en) | A kind of magnetism PAFs solid extracting agents and its preparation method and application | |
Huang et al. | Application of molecularly imprinted polymers in wastewater treatment: a review | |
Li et al. | Surface molecular imprinting onto fluorescein-coated magnetic nanoparticles via reversible addition fragmentation chain transfer polymerization: A facile three-in-one system for recognition and separation of endocrine disrupting chemicals | |
CN106975443B (en) | A kind of preparation method and application of magnetic modified bentonite adsorbent | |
CN106637929B (en) | Hydrophobic oleophylic cotton fiber and preparation method and application thereof | |
US20030195277A1 (en) | Printing medium comprising aerogel materials | |
CN106378097B (en) | The preparation of molecular engram silica magnetic attapulgite is simultaneously applied to identification tyrosine enantiomer | |
CN106693920A (en) | Magnetic nano composite material and a preparation method and application thereof | |
Zeng et al. | Colorimetric determination of tetrabromobisphenol A based on enzyme-mimicking activity and molecular recognition of metal-organic framework-based molecularly imprinted polymers | |
CN108504347B (en) | Enhanced dual-emission fluorescent composite material and preparation method and application thereof | |
CN110548478A (en) | modified magnetic nano particle and application thereof | |
CN109550485A (en) | A kind of preparation method of amination chitosan magnetic | |
CN113750968A (en) | Water-insoluble cyclodextrin-based metal organic framework material and preparation method thereof | |
Bettini et al. | SiO2 based nanocomposite for simultaneous magnetic removal and discrimination of small pollutants in water | |
El-Desouky et al. | Effective methods for removing different types of dyes–modelling analysisstatistical physics treatment and DFT calculations: a review | |
Zhang et al. | Elevating the stability and adsorption performance of metal-organic frameworks by chitosan and attapulgite for capturing methylene blue in the water | |
CN111359590A (en) | Magnetic porous cellulose acetate microsphere and preparation method and application thereof | |
CN106111210B (en) | The preparation method and its method for dismounting of detachable magnetic microsphere supported precious metal catalyst | |
CN101708464B (en) | Cation resin matrix CdS-loaded composite material and preparation method thereof | |
CN110064381A (en) | A kind of alginate complex microsphere and its preparation method and application of efficient removal contents of many kinds of heavy metal ion | |
CN106185958B (en) | The preparation method of hydrophobic mesoporous silicon and its application in waterproof color coating is prepared | |
CN112462049A (en) | Preparation method of artificial antibody for detecting heavy metal ions | |
CN108459002A (en) | A kind of preparation method of magnetic blotting sensor and application |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
PB01 | Publication | ||
PB01 | Publication | ||
SE01 | Entry into force of request for substantive examination | ||
SE01 | Entry into force of request for substantive examination | ||
RJ01 | Rejection of invention patent application after publication | ||
RJ01 | Rejection of invention patent application after publication |
Application publication date: 20190104 |