CN104549127B - Magnetic coupling hydroxyapatite nano particulate and its preparation method and application - Google Patents
Magnetic coupling hydroxyapatite nano particulate and its preparation method and application Download PDFInfo
- Publication number
- CN104549127B CN104549127B CN201510044086.2A CN201510044086A CN104549127B CN 104549127 B CN104549127 B CN 104549127B CN 201510044086 A CN201510044086 A CN 201510044086A CN 104549127 B CN104549127 B CN 104549127B
- Authority
- CN
- China
- Prior art keywords
- hydroxyapatite
- magnetic coupling
- magnetic
- solution
- nano particle
- 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.)
- Active
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
- B01J20/02—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
- B01J20/28—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
- B01J20/28019—Spherical, ellipsoidal or cylindrical
-
- 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
- B01J20/30—Processes for preparing, regenerating, or reactivating
- B01J20/3085—Chemical treatments not covered by groups B01J20/3007 - B01J20/3078
-
- 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
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/58—Treatment of water, waste water, or sewage by removing specified dissolved compounds
- C02F1/62—Heavy metal compounds
-
- 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
- B01J2220/00—Aspects relating to sorbent materials
- B01J2220/40—Aspects relating to the composition of sorbent or filter aid materials
- B01J2220/48—Sorbents characterised by the starting material used for their preparation
- B01J2220/4806—Sorbents characterised by the starting material used for their preparation the starting material being of inorganic character
Landscapes
- Chemical & Material Sciences (AREA)
- Organic Chemistry (AREA)
- Analytical Chemistry (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Life Sciences & Earth Sciences (AREA)
- Hydrology & Water Resources (AREA)
- Engineering & Computer Science (AREA)
- Environmental & Geological Engineering (AREA)
- Water Supply & Treatment (AREA)
- Inorganic Chemistry (AREA)
- Solid-Sorbent Or Filter-Aiding Compositions (AREA)
Abstract
The invention discloses a kind of magnetic coupling hydroxyapatite nano particulate, by Fe3O4Nano particle is constituted with hydroxyapatite nanoparticle, Fe3O4Mol ratio with hydroxyapatite is(1‑10):1, the magnetic coupling hydroxyapatite nano particulate is Fe3O4Nano particle and the uniform spherical agglomeration thing or granule for distributing alternately of hydroxyapatite nanoparticle.The preparation method of magnetic coupling hydroxyapatite nano particulate of the present invention is simple, heavy metal ions in sewage and treatment later stage can efficiently be removed can realize that rapid magnetic is separated, to the adsorbance of lead ion in sewage up to 440 mg/g, the adsorbance of cadmium ion is up to 238 mg/g,, up to 139 mg/g, the adsorbance of copper ion is up to 135 mg/g for the adsorbance of zinc ion;Magnetic coupling hydroxyapatite nano particulate of the invention has quick magnetic response characteristic, and externally-applied magnetic field can just realize quick separation of solid and liquid, and separative efficiency is high, simple to operate, efficient, the noresidue in water body, will not cause secondary pollution to water body and environment.
Description
Technical field
The present invention relates to technical field of material, and in particular to a kind of magnetic coupling hydroxyapatite nano particulate and its
Preparation method and application.
Background technology
Battery manufacturing industry, metal smelt, mining etc. one is have stimulated the need for the development of modern economy and industrial production big
Highly energy-consuming, the extensive development of high pollution enterprise are criticized, substantial amounts of heavy metal ion is contained in the waste water that these enterprises produce, it is poisonous
Ion flows into river, river with the waste water that enterprise discharges, and gos deep into underground water, heavy damage ecological environment.Therefore heavy metal pollution is solved
Problem, the ecological environment of protection human survival has turned into the problem of countries in the world urgent need to resolve.
Hydroxyapatite is common a kind of material in current Industrial Waste Water Treatments, for the removal of heavy metal in sewage.
Native hydroxyl apatite is cheap and easy to get, with certain wastewater treatment efficiency, for example, reachable to the adsorbance of lead ion
28.6mg/g;Artificial synthesized big compared with pure, specific surface area, nano level hydroxyapatite can significantly improve a huge sum of money in sewage
Belong to the removal capacity of ion, the pattern depending on synthetic product is different, be 260-416mg/g to the adsorbance of lead ion, but hydroxyl phosphorus
Lime stone is general with powdered presence, there is separation of solid and liquid difficulty, the low defect of the rate of settling in the Industrial Waste Water Treatments later stage, one
Determine to increase in degree the cost of commercial Application, the hydroxyapatite remained in water body after use has one to microorganisms in water
Fixed toxic and side effect.
Magnetic separation technique starts to be applied to engineering of water treatment currently as an emerging technology, and magnetic separation technique is by magnetic
A kind of effect of field force, physical separation method that the material different to magnetic is separate is processing the heavy metal ion later stage, outward
Plus magnetic field quickly can separate from the aqueous solution, so as to overcome adsorbent to reclaim difficult defect, it is to avoid nano adsorber is to micro-
The toxic and side effect of biological and human body.Combined with hydroxyapatite about magnetic Nano material and reported less, such as CN 103541005A
A kind of preparation method of magnetic hydroxylapatite crystal whisker ball is disclosed, the method is repaiied with soluble calcium salt, soluble microcosmic salt, bilayer
The nano ferriferrous oxide ferrofluid of decorations is raw material, and urea is to prepare magnetic hydroxyl under acidity-basicity regulator, water bath condition
Apatite whiskers ball, can be used for the fields such as target medicine carrier, biological engineering material, but used in the method experimentation
Nano ferriferrous oxide needs to be modified by double-deck, and this increased the complexity of method to a certain extent, and to modify four oxygen
Change the coating material generally more difficult removal added by three-iron, this also increases the complexity of production to a certain extent.
H.Yang,S.Masse,H.Zhang,C.Hélary,L.Li,T.Coradin,Surface reactivity of
hydroxyapatite nanocoatings deposited on iron oxide magnetic spheres toward
toxic metals,J.Colloid Inter.Sci.417(2014)The Fe of 1-8. reports3O4@HydroxyapatiteIt is compound micro-
Ball and for lead ion removal, needed to use in this composite particles building-up process aspartic acid process carry out surface be modified,
Building-up process is complicated.Liao,D.;Zheng,W.;Li,X.;Yang,Q.;Yue,X.;Guo,L.;Zeng,G.Removal of
lead(II)from aqueous solutions using carbonate hydroxyapatite extracted from
The Li Dengxiao of eggshell waste.J.Hazard.Mater.2010,177 (1-3), 126-130. report are using discarded
Egg shell synthesized magnetic calcium hydroxy phosphate composite for lead ion removal, but this material scatter difference is to lead
The removal effect of ion is limited.CN102500333A propose with natural zeolite, hydroxyapatite, ferroso-ferric oxide, shitosan and
Cationic surfactant prepares a kind of magnetic cationic surfactant modified chitosan/hydroxy-apatite as stock
Stone/zeolite composition, as magnetic organic/inorganic composite material adsorbent, and this adsorbent can be applied to rotten in water removal
The heavy metal contaminants such as the organic pollution such as sour, Congo red and copper ion are grown, but the material prepares raw material complexity, to treatment
The pH value of sewage is required, and needs to adjust the pH value of sewage to partial neutral (6.0-7.0) before treatment, and operability is poor, and
Absorption property is not (, in 80mg/kg, cupric ion adsorption is in 27mg/kg for humic acid and Congo red adsorbance) high, and this is in certain journey
Its application in sewage disposal is limited on degree.
The content of the invention
The technical problems to be solved by the invention are:In view of the shortcomings of the prior art, there is provided a kind of magnetic coupling hydroxyl phosphorus
Lime stone nanoparticle, its preparation method is simple, easily operated, can be applied to process heavy metal wastewater thereby;The nanoparticle has excellent
Different acid resistance, also almost without Iron pick up in the case of pH=1.0-3.0, the nanoparticle is applied to the various pH for the treatment of
The heavy metal wastewater thereby of value, can efficiently remove heavy metal ions in sewage and treatment later stage can realize that rapid magnetic is separated.
The present invention solve the technical scheme that is used of above-mentioned technical problem for:Magnetic coupling hydroxyapatite nano particulate,
By Fe3O4Nano particle is constituted with hydroxyapatite nanoparticle, Fe3O4It is (1-10) with the mol ratio of hydroxyapatite:1, should
Magnetic coupling hydroxyapatite nano particulate is Fe3O4Nano particle and the uniform ball for distributing alternately of hydroxyapatite nanoparticle
Shape aggregate or granule.
The preparation method of magnetic coupling hydroxyapatite nano particulate, comprises the following steps:
1) under nitrogen protection atmosphere, by soluble trivalent iron salt with soluble divalent iron salt with (1.9-2.2):1 rubs
You form mixture than well mixed, then the mixture are dissolved in deionized water with the ratio of 0.5-0.7g/mL, mechanical agitation
After 10-30min, to ammoniacal liquor is added dropwise in solution, until the color blackening of solution, magnetic point is carried out after continuing mechanical agitation 0.5-1h
From magnetisable material, then magnetisable material deionized water and absolute ethyl alcohol cyclic washing to obtaining being obtained, then in vacuum condition
Under dry 1-6h in 45-80 DEG C, obtain the Fe of black3O4Nano particle;
2) Fe that will be prepared3O4Nano particle, soluble calcium salt and lauryl sodium sulfate are according to 1:(1-10):1
Mixed in molar ratio is formed uniformly mixture, then the mixture is dissolved in deionized water with the ratio of 0.8-2.5g/mL, and machinery is stirred
10-30min is mixed, the Na with above-mentioned soluble calcium salt equimolar concentration is then added in the solution2CO3, machinery is continued at room temperature
Magnetic Isolation is carried out after stirring 1-3h, magnetisable material is obtained, then magnetisable material deionized water and absolute ethyl alcohol to obtaining is anti-
After backwashing is washed, and then dries 1-6h in 45-80 DEG C under vacuum, obtains Fe3O4/CaCO3Nano particle presoma;
3) Fe that will be prepared3O4/CaCO3Nano particle presoma dissolves in the Na that concentration is 0.15-0.3mol/L3PO4
In the aqueous solution, uniform solution is obtained through sonic oscillation, solution is then transferred to autoclave, in 150-300 DEG C of condition
After lower hydro-thermal reaction 3-24h, room temperature is cooled to, product is washed repeatedly, alcohol is washed, finally Magnetic Isolation, vacuum drying again
Magnetic coupling hydroxyapatite nano particulate is obtained afterwards, and its form is Fe3O4Nano particle is equal with hydroxyapatite nanoparticle
The even spherical agglomeration thing or granule for distributing alternately, Fe3O4It is (1-10) with the mol ratio of hydroxyapatite:1.
Lauryl sodium sulfate (abbreviation SDS) is a kind of surfactant, as a kind of anion surfactant, is had
Certain critical micelle concentration, when the critical micelle concentration more than this surfactant, this anion surfactant
Microballoon micelle easily is agglomerated into, due to the interaction between surfactant and calcium ion, this microballoon micelle is in calcium carbonate
Play a part of to promote calcium carbonate granule nucleation, grow and be agglomerated into big particle in Crystallization, in addition four under mechanical agitation
Fe 3 O nano particle can be uniformly embedded into the space between calcium carbonate granule.
Preferably, step 1) described in soluble trivalent iron salt be FeCl3、FeCl3·6H2O、Fe(NO3)3·9H2O
And Fe2(SO4)3In one or more, described soluble divalent iron salt is FeCl2、FeCl2·4H2O and FeSO4·7H2In O
One or more.
Preferably, step 2) described in soluble calcium salt be CaCl2With Ca (NO3)2In one or two.
Application of the magnetic coupling hydroxyapatite nano particulate of the invention in heavy metal wastewater thereby is processed.Magnetic of the invention
Property composite hydroxylapatite nanoparticle there is excellent acid resistance, in the case of pH value=1.0-3.0 also almost without iron from
Son is separated out, and can efficiently remove the Pb in sewage2+、Cd2+、Zn2+、Cu2+Etc. heavy metal ion and treatment the later stage can realize quick magnetic
Property separate, using permanent magnet can in short time (in such as 1 minute) effectively Magnetic Isolation, separative efficiency up to more than 98%,
Noresidue in water body.For the sewage of the different pH value containing heavy metal ion, magnetic coupling hydroxyapatite of the invention is received
The adsorption mechanism of rice particulate heavy metal ion is different.With magnetic coupling hydroxyapatite nano particulate pair of the invention
Pb2+Absorption as a example by, during pH value=3-6, with ion exchange with absorption complex mechanism based on, its reaction equation is:
Ca10(PO4)6(OH)2+xPb2+→xCa2++Ca10-xPbx(PO4)6(OH)2
As pH value=1-3, predominantly dissolving-PRECIPITATION MECHANISM, the reaction equation of course of dissolution is:
nCa10(PO4)6(OH)2+4mH+→10nCa2++3mHPO4 2-+(2n-m)(PO4)3(OH)10-+mH2O
The reaction equation of precipitation process is:
(x+5y)Pb2++xHPO4 2-+y(PO4)3(OH)10-→xPbHPO4+yPb5(PO4)3(OH)
Either which kind of adsorption mechanism, adsorbance higher is respectively provided with to heavy metal ions in sewage, adsorbs the network for being formed
Compound or sediment, the phase can be by Magnetic Isolation and Fe after treatment3O4Quickly and easily separated from water body together, separated
Efficiency high, the noresidue in water body will not be polluted to water body and environment.Therefore, magnetic coupling hydroxy-apatite of the invention
When stone nanoparticle is applied to waste water control, do not limited by pH value of sewage water, before processing need not be pre-adjusted the pH value of sewage, fitted
It is wide with scope, it is applicable to the heavy metal wastewater thereby of various pH value.
Compared with prior art, the advantage of the invention is that:The inventive method is in Fe3O4/CaCO3Nano particle presoma
Preparation process in the organic solvent such as ethylene glycol, isopropanol is not used, because organic solvent can increase cost, and organic solvent has
There is certain toxicity;The Fe of synthesis3O4Nano particle need not be modified its surface in use, Fe3O4In conduct
The lauryl sodium sulfate effect of surfactant it is lower can and CaCO3Form the uniform spherical agglomeration thing for distributing alternately or group
Granular Fe3O4/CaCO3Nano particle presoma, the Fe3O4/CaCO3Nano particle presoma can be prepared using hydrothermal method
Magnetic coupling hydroxyapatite nano particulate, preparation method is simple;Magnetic coupling hydroxyapatite nano particulate of the invention is
Fe3O4Nano particle and the uniform spherical agglomeration thing for distributing alternately of hydroxyapatite nanoparticle or pellet shape monodispersity
Grain, with excellent acid resistance, also almost without Iron pick up in the case of pH value=1.0-3.0;Magnetic of the invention is answered
Close the heavy metal wastewater thereby that hydroxyapatite nano particulate is applied to the various pH value for the treatment of, can efficiently remove in sewage heavy metal from
The son and treatment later stage can realize that rapid magnetic is separated, to the adsorbance of lead ion in sewage up to 440mg/g, the absorption of cadmium ion
, up to 238mg/g, up to 139mg/g, the adsorbance of copper ion is up to 135mg/g for the adsorbance of zinc ion for amount;It is compared to non-
The simple hydroxyapatite of magnetic, magnetic coupling hydroxyapatite nano particulate of the present invention has quick magnetic response characteristic, outward
Plus magnetic field can just realize quick separation of solid and liquid, separative efficiency is high, simple to operate, efficient, and the noresidue in water body will not be to water
Body and environment cause secondary pollution.
Brief description of the drawings
Fig. 1 is Fe prepared by embodiment 13O4Nano particle (#2), Fe3O4/CaCO3Nano particle presoma (#1) and magnetic
The XRD comparison diagrams of composite hydroxylapatite nanoparticle (#3);
Fig. 2 a are Fe prepared by embodiment 23O4The SEM figures of nano particle;
Fig. 2 b are Fe prepared by embodiment 23O4/CaCO3The SEM figures of nano particle presoma;
Fig. 2 c are the SEM figures of magnetic coupling hydroxyapatite nano particulate prepared by embodiment 2;
Fig. 3 is the magnetic coupling hydroxyapatite nano particulate for preparing of embodiment 1 at various ph values to Pb2+Consolidate
Qualitative energy, the Ca to separating out2+Concentration and the Ca to being separated out in the aqueous solution containing lead ion2+The curve map of concentration.
Specific embodiment
The present invention is described in further detail below in conjunction with accompanying drawing embodiment.
The preparation method of the magnetic coupling hydroxyapatite nano particulate of embodiment 1, is carried out in accordance with the following steps:
1) under nitrogen protection atmosphere, by the FeCl of 0.85g3·6H2The FeCl of O and 0.30g2·4H2O is well mixed shape
Resulting mixture, then the mixture is dissolved in 200mL deionized waters, after mechanical agitation 30min, to being added dropwise over ammonia in solution
Water, until the color blackening of solution, Magnetic Isolation is carried out after continuing mechanical agitation 1h, obtains magnetisable material, then the magnetic to obtaining
Property material deionized water and absolute ethyl alcohol cyclic washing, then dry 6h in 45 DEG C under vacuum, obtain 0.46g black
Fe3O4Nano particle;
2) Fe of the 0.46g that will be prepared3O4The CaCl of nano particle, 0.89g2With the lauryl sodium sulfate of 1.15g
It is well mixed to form mixture, then the mixture is dissolved in 120mL deionized waters, mechanical agitation 30min, then in the solution
The Na for adding 40mL to contain 0.85g2CO3The aqueous solution, carry out Magnetic Isolation after continuing mechanical agitation 3h at room temperature, obtain magnetic
Property material, then magnetisable material deionized water and absolute ethyl alcohol cyclic washing to obtaining, then under vacuum in 45 DEG C
6h is dried, the Fe of 0.75g is obtained3O4/CaCO3Nano particle presoma;
3) Fe of the 0.75g that will be prepared3O4/CaCO3Nano particle presoma dissolves in 70mL concentration for 0.15mol/L
Na3PO4In the aqueous solution, uniform solution is obtained through sonic oscillation, solution is then transferred to 100mL autoclaves,
Under the conditions of 180 DEG C after hydro-thermal reaction 3h, room temperature is cooled to, product is washed repeatedly, alcohol is washed, finally Magnetic Isolation again, very
Sky obtains the magnetic coupling hydroxyapatite nano particulate of embodiment 1 after drying, its form is Fe3O4Nano particle and hydroxyl
Spherical agglomeration thing or granule that apatite nano particle uniformly distributes alternately, Fe3O4It is 5 with the mol ratio of hydroxyapatite:2.
Fig. 1 is the Fe that embodiment 1 is prepared3O4Nano particle (#2), Fe3O4/CaCO3Nano particle presoma (#1) and
The XRD comparison diagrams of magnetic coupling hydroxyapatite nano particulate (#3), as can be seen from Figure 1 magnetic coupling hydroxyapatite nano
It is existing in particulate to belong to Fe3O4Phase:(220), also there is the phase for belonging to hydroxyapatite (311), (400), (511), (440):
(002), (211), (300), (202), (130), (222), (213), and Fe3O4/CaCO3Nano particle presoma is anti-through hydro-thermal
Magnetic coupling hydroxyapatite nano particulate has been fully converted into after answering.
The preparation method of the magnetic coupling hydroxyapatite nano particulate of embodiment 2, is carried out in accordance with the following steps:
1) under nitrogen protection atmosphere, by the FeCl of 1.7g3·6H2The FeCl of O and 0.60g2·4H2O is well mixed to be formed
Mixture, then the mixture is dissolved in 200mL deionized waters, after mechanical agitation 30min, to being added dropwise over ammoniacal liquor in solution,
Until the color blackening of solution, Magnetic Isolation is carried out after continuing mechanical agitation 3h, magnetisable material, then the Magnetic Materials to obtaining are obtained
Matter deionized water and absolute ethyl alcohol cyclic washing, then dry 5h in 50 DEG C under vacuum, obtain 0.92g black
Fe3O4Nano particle;
2) Fe of the 0.92g that will be prepared3O4The CaCl of nano particle, 0.89g2With the lauryl sodium sulfate of 1.15g
It is well mixed to form mixture, then the mixture is dissolved in 120mL deionized waters, mechanical agitation 30min, then in the solution
The Na for adding 40mL to contain 0.85g2CO3The aqueous solution, carry out Magnetic Isolation after continuing mechanical agitation 6h at room temperature, obtain magnetic
Property material, then magnetisable material deionized water and absolute ethyl alcohol cyclic washing to obtaining, then under vacuum in 50 DEG C
5h is dried, the Fe of 1.2g is obtained3O4/CaCO3Nano particle presoma;
3) Fe of the 1.2g that will be prepared3O4/CaCO3It is 0.3mol/L's that nano particle presoma dissolves in 70mL concentration
Na3PO4In the aqueous solution, uniform solution is obtained through sonic oscillation, solution is then transferred to 100mL autoclaves, 180
Under the conditions of DEG C after hydro-thermal reaction 3h, room temperature is cooled to, product is washed repeatedly, alcohol is washed, finally Magnetic Isolation again, vacuum is done
The magnetic coupling hydroxyapatite nano particulate of embodiment 2 is obtained after dry, its form is Fe3O4Nano particle and hydroxy-apatite
Spherical agglomeration thing or granule that stone nano particle uniformly distributes alternately, Fe3O4It is 5 with the mol ratio of hydroxyapatite:1.
Fig. 2 a are the Fe that embodiment 2 is prepared3O4The SEM figures of nano particle, its individual particle particle size is 20-
30nm;Fig. 2 b are the Fe that embodiment 2 is prepared3O4/CaCO3The SEM figures of nano particle presoma, from Fig. 2 b, small particle
Fe3O4With block CaCO3Composition spherical agglomeration thing, wherein Fe3O4With CaCO3Uniformly distribute alternately, spherical agglomeration thing structure
Stabilization;Fig. 2 c are the SEM figures of magnetic coupling hydroxyapatite nano particulate prepared by embodiment 2, from Fig. 2 c, with presoma
Fe3O4/CaCO3Pattern slightly has difference, is substantially also the spherical agglomeration thing of monodispersity, and the spherical agglomeration thing is Fe3O4And hydroxyl
Apatite is uniformly distributed the magnetic coupling hydroxyapatite nano particulate of composition.
The magnetic coupling hydroxyapatite nano particulate that embodiment 1 is prepared is used for Pb2+Removal, study its right
Pb2+Fixed performance, experimental procedure is as follows:
1. 50mL Pb are prepared respectively in 5 conical flasks of 250mL2+Concentration is the solution of 400mg/L, uses HNO3With
The NaOH aqueous solution adjusts the pH value of solution respectively so that the pH value of solution is respectively 2.0,3.0,4.0,5.0 and in 5 conical flasks
6.0, the magnetic coupling hydroxyapatite nano particulate for then preparing 50mg embodiments 1 is separately added into this 5 conical flasks
In, conical flask is placed in Desk type constant-temperatureoscillator oscillator afterwards, temperature is set to 25 DEG C, and oscillation rate is 180r/min, and the time is 3h.
2. 3mL solution is taken respectively from above-mentioned 5 conical flasks with syringe, first filtered with the water system that aperture is 0.45 micron
Head filters out magnetic coupling hydroxyapatite material, then by filtrate with Inductively coupled plasma optical emission spectrometer (ICP-AES)
Measure, remaining metal ion content in solution after the solid lead reaction of acquisition.The magnetic hydroxylapatite is calculated to receive
Rice grain is for Pb2+Saturated extent of adsorption reach 440mg/g.
The magnetic coupling hydroxyapatite nano particulate that embodiment 1 is prepared is at various ph values to Pb2+Stationarity
Energy, the Ca to separating out2+Concentration and the Ca to being separated out in the aqueous solution containing lead ion2+The curve map of concentration is shown in Fig. 3, from absorption
Calcium ion concentration change curve can be seen that magnetic coupling hydroxyapatite nano particulate in pH value=3-6, only in preceding solution
There is micro Ca2+Separate out, show that the magnetic coupling hydroxyapatite nano particulate can be with stable existence;When pH value continues to be reduced to
When 2, there is part Ca2+Separate out, show that the magnetic coupling hydroxyapatite nano particle fraction dissolves;But as treatment identical value pH
Under when containing lead solution, as pH value=3-6, Ca2+Amount of precipitation increase (calcium ion concentration change curve in solution after absorption),
Substantially and Pb simultaneously2+Fixed amount be consistent (adsorbed plumbum ion concentration curve), i.e. Pb2+In instead of hydroxyapatite
Ca2+Position;There is substantial amounts of Ca when pH value continues to be reduced to 2, in mixed solution2+Separate out, and far above Pb2+Fixed amount,
Mainly due to the dissolving of hydroxyapatite in strong acidic condition magnetic composite hydroxylapatite nanoparticle, and highly acid ring
Border inhibits what the generation of lead deposits thing was caused.
The magnetic coupling hydroxyapatite nano particulate that embodiment 1 is prepared is used for Cd2+Removal, study its right
Cd2+Fixed performance, experimental procedure is as follows:
1. 50mL Cd are prepared respectively in 1 conical flask of 250mL2+Concentration is the solution of 217mg/L, uses HNO3With
The pH value that the NaOH aqueous solution adjusts solution respectively is 3.0, the magnetic coupling hydroxy-apatite for then preparing 50mg embodiments 1
In stone nanoparticle this conical flask, conical flask is placed in Desk type constant-temperatureoscillator oscillator afterwards, temperature is set to 25 DEG C, oscillation rate
It is 180r/min, the time is 3h.
2. 3mL solution is distinguished from above-mentioned conical flask with syringe, first will with the water system filtering head that aperture is 0.45 micron
Magnetic coupling hydroxyapatite material is filtered out, then filtrate is carried out with Inductively coupled plasma optical emission spectrometer (ICP-AES)
Measurement, obtains solid Cd2+Remaining metal ion content in solution after reaction.It is calculated magnetic hydroxylapatite nanometer
Grain is for Cd2+Saturated extent of adsorption reach 238mg/g.
The magnetic coupling hydroxyapatite nano particulate that embodiment 1 is prepared is used for Zn2+Removal, study its right
Zn2+Fixed performance, experimental procedure is as follows:
1. 50mL Zn are prepared respectively in 1 conical flask of 250mL2+Concentration is the solution of 126mg/L, uses HNO3With
The pH value that the NaOH aqueous solution adjusts solution respectively is 3.0, the magnetic coupling hydroxy-apatite for then preparing 50mg embodiments 1
In stone nanoparticle this conical flask, conical flask is placed in Desk type constant-temperatureoscillator oscillator afterwards, temperature is set to 25 DEG C, oscillation rate
It is 180r/min, the time is 3h.
2. 3mL solution is distinguished from above-mentioned conical flask with syringe, first will with the water system filtering head that aperture is 0.45 micron
Magnetic coupling hydroxyapatite material is filtered out, then filtrate is carried out with Inductively coupled plasma optical emission spectrometer (ICP-AES)
Measurement, obtains solid Zn2+Remaining metal ion content in solution after reaction.It is calculated magnetic hydroxylapatite nanometer
Grain is for Zn2+Saturated extent of adsorption reach 139mg/g.
The magnetic coupling hydroxyapatite nano particulate that embodiment 2 is prepared is used for Cu2+Removal, study its right
Cu2+Fixed performance, experimental procedure is as follows:
1. 50mL Cu are prepared respectively in 1 conical flask of 250mL2+Concentration is the solution of 123mg/L, uses HNO3With
The pH value that the NaOH aqueous solution adjusts solution respectively is 4.0, the magnetic coupling hydroxy-apatite for then preparing 50mg embodiments 1
In stone nanoparticle this conical flask, conical flask is placed in Desk type constant-temperatureoscillator oscillator afterwards, temperature is set to 25 DEG C, oscillation rate
It is 180r/min, the time is 3h.
2. 3mL solution is distinguished from above-mentioned conical flask with syringe, first will with the water system filtering head that aperture is 0.45 micron
Magnetic coupling hydroxyapatite material is filtered out, then filtrate is carried out with Inductively coupled plasma optical emission spectrometer (ICP-AES)
Measurement, obtains solid Cu2+Remaining metal ion content in solution after reaction.It is calculated magnetic hydroxylapatite nanometer
Grain is for Cu2+Saturated extent of adsorption reach 135mg/g.
Claims (4)
1. the preparation method of magnetic coupling hydroxyapatite nano particulate, it is characterised in that comprise the following steps:
1) under nitrogen protection atmosphere, by soluble trivalent iron salt with soluble divalent iron salt with (1.9-2.2):1 mol ratio
It is well mixed to form mixture, then the mixture is dissolved in deionized water with the ratio of 0.5-0.7g/mL, mechanical agitation 10-
After 30min, to ammoniacal liquor is added dropwise in solution, until the color blackening of solution, Magnetic Isolation is carried out after continuing mechanical agitation 0.5-1h,
Magnetisable material, then magnetisable material deionized water and absolute ethyl alcohol cyclic washing to obtaining are obtained, then under vacuum
1-6h is dried in 45-80 DEG C, the particle size for obtaining black is the Fe of 20-30nm3O4Nano particle;
2) Fe that will be prepared3O4Nano particle, soluble calcium salt and lauryl sodium sulfate are according to 1:(1-10):1 mole
Mixture is formed than well mixed, then the mixture is dissolved in deionized water with the ratio of 0.8-2.5g/mL, mechanical agitation
10-30min, then adds the Na with above-mentioned soluble calcium salt equimolar concentration in the solution2CO3, machinery is continued at room temperature and is stirred
Magnetic Isolation is carried out after mixing 1-3h, magnetisable material is obtained, then to the magnetisable material deionized water and absolute ethyl alcohol that obtain repeatedly
Washing, then dries 1-6h in 45-80 DEG C under vacuum, obtains Fe3O4/CaCO3Nano particle presoma;
3) Fe that will be prepared3O4/CaCO3Nano particle presoma dissolves in the Na that concentration is 0.15-0.3mol/L3PO4It is water-soluble
In liquid, uniform solution is obtained through sonic oscillation, solution is then transferred to autoclave, the water under the conditions of 150-300 DEG C
After thermal response 3-24h, room temperature is cooled to, product is washed repeatedly, alcohol is washed, finally Magnetic Isolation again, after vacuum drying i.e.
Magnetic coupling hydroxyapatite nano particulate is obtained, its form is Fe3O4Nano particle and hydroxyapatite nanoparticle homogeneous phase
Between be distributed spherical agglomeration thing, Fe3O4It is (1-10) with the mol ratio of hydroxyapatite:1.
2. the preparation method of magnetic coupling hydroxyapatite nano particulate according to claim 1, it is characterised in that step
1) the soluble trivalent iron salt described in is FeCl3、FeCl3·6H2O、Fe(NO3)3·9H2O and Fe2(SO4)3In one kind or
Various, described soluble divalent iron salt is FeCl2、FeCl2·4H2O and FeSO4·7H2One or more in O.
3. the preparation method of magnetic coupling hydroxyapatite nano particulate according to claim 1 and 2, it is characterised in that step
It is rapid 2) described in soluble calcium salt be CaCl2With Ca (NO3)2In one or two.
4. the magnetic coupling hydroxyapatite nano particulate that prepared by claim 1 is in treatment pH value in the heavy metal wastewater thereby of 2-3
Application.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201510044086.2A CN104549127B (en) | 2015-01-29 | 2015-01-29 | Magnetic coupling hydroxyapatite nano particulate and its preparation method and application |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201510044086.2A CN104549127B (en) | 2015-01-29 | 2015-01-29 | Magnetic coupling hydroxyapatite nano particulate and its preparation method and application |
Publications (2)
Publication Number | Publication Date |
---|---|
CN104549127A CN104549127A (en) | 2015-04-29 |
CN104549127B true CN104549127B (en) | 2017-05-31 |
Family
ID=53066836
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CN201510044086.2A Active CN104549127B (en) | 2015-01-29 | 2015-01-29 | Magnetic coupling hydroxyapatite nano particulate and its preparation method and application |
Country Status (1)
Country | Link |
---|---|
CN (1) | CN104549127B (en) |
Families Citing this family (13)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN105255853B (en) * | 2015-11-10 | 2018-03-06 | 河南工业大学 | A kind of preparation method of magnetic hydroxylapatite immobilized lipase and the application in edible oil and fat processing |
CN105771875B (en) * | 2016-05-18 | 2018-04-13 | 湖南大学 | Magnetic Nano chlorapatite adsorbent and preparation method thereof |
CN105903069A (en) * | 2016-06-28 | 2016-08-31 | 扬州大学 | One-step synthesis method of hydroxyapatite/ferriferrous oxide composite material |
CN107042093B (en) * | 2017-03-07 | 2019-07-12 | 四川大学 | A kind of preparation method of the big ball adsorbent material of composite magnetic hydroxyapatite |
CN107684903B (en) * | 2017-10-11 | 2021-05-28 | 中国农业科学院麻类研究所 | Method for preparing magnetic humic acid modified quartz sand and modified quartz sand |
CN109088060B (en) * | 2018-08-01 | 2021-07-20 | 武汉理工大学 | Preparation method of lithium ion battery cathode material based on ionic bond |
CN109351322A (en) * | 2018-11-07 | 2019-02-19 | 西南大学 | A kind of preparation method for the micro-nano MFH composite material handling lead-contaminated soil |
CN109663571A (en) * | 2018-11-22 | 2019-04-23 | 浙江农林大学 | A kind of preparation method of magnetism-metal organic frame MOF material |
CN111644159B (en) * | 2020-05-25 | 2022-11-22 | 哈尔滨工业大学 | Magnetic adsorbent based on modified eggshell and preparation method and application thereof |
CN112014373B (en) * | 2020-08-28 | 2023-01-13 | 陕西理工大学 | SERS Raman substrate, preparation method thereof and method for analyzing and detecting pesticide residues |
CN112792118B (en) * | 2020-12-22 | 2022-03-29 | 济南大学 | Method for preparing active filler by using hydroxyapatite, zero-valent iron and humic acid and application thereof |
CN113871129B (en) * | 2021-11-08 | 2023-06-20 | 昆明理工大学 | Preparation method and application of liquid magnetic fluid |
CN114887580B (en) * | 2022-04-02 | 2024-06-21 | 江西省科学院微生物研究所(江西省流域生态研究所) | Preparation method and application of hydroxyapatite-coated high-magnetic nanomaterial |
Family Cites Families (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
WO2004065306A1 (en) * | 2003-01-17 | 2004-08-05 | Hitachi Maxell, Ltd. | Composite particle and process for producing the same |
CN101703917A (en) * | 2009-11-25 | 2010-05-12 | 湖南大学 | Magnetic nano hydroxyapatite adsorbent, preparation and application thereof |
CN101759170B (en) * | 2009-12-23 | 2011-07-06 | 天津大学 | Magnetic nano sheet-shaped hydroxyapatite and preparation method and application thereof |
CN102139866B (en) * | 2010-09-28 | 2013-05-29 | 上海师范大学 | Method for preparing magnetic mesoporous apatite microsphere material by utilizing hydrothermal method |
CN102381691A (en) * | 2011-07-29 | 2012-03-21 | 沈阳大学 | Preparation method of nano hydroxylapatite adsorbent for absorbing heavy metal ions in waste water |
-
2015
- 2015-01-29 CN CN201510044086.2A patent/CN104549127B/en active Active
Also Published As
Publication number | Publication date |
---|---|
CN104549127A (en) | 2015-04-29 |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
CN104549127B (en) | Magnetic coupling hydroxyapatite nano particulate and its preparation method and application | |
Li et al. | Efficient removal of thallium (I) from wastewater using flower-like manganese dioxide coated magnetic pyrite cinder | |
Zhang et al. | Fabrication of L-cysteine stabilized α-FeOOH nanocomposite on porous hydrophilic biochar as an effective adsorbent for Pb2+ removal | |
CN1894029B (en) | Porous formed article and method for production thereof | |
Yang et al. | Phosphate recovery through adsorption assisted precipitation using novel precipitation material developed from building waste: behavior and mechanism | |
CN111718719B (en) | Vulcanized nano zero-valent iron-acid activated montmorillonite composite material and preparation method and application thereof | |
US8337805B1 (en) | Method for preparing magnetite nanoparticles from low-grade iron ore and magnetite nanoparticles prepared by the same | |
CN108706561B (en) | Method for preparing high-purity iron phosphate by using pyrite cinder | |
CN102941057B (en) | Preparation method and application of magnetic compound arsenic adsorption agent | |
CN112221461A (en) | Phosphorus adsorption material and preparation method thereof | |
Shin et al. | Adsorption characteristics of multi-metal ions by red mud, zeolite, limestone, and oyster shell | |
Xiao et al. | Phosphorus removal and recovery from secondary effluent in sewage treatment plant by magnetite mineral microparticles | |
CN112316906A (en) | Preparation method of ferromagnetic amino-modified lanthanide metal organic framework material and application of material in adsorption and dephosphorization | |
Liao et al. | The construction of magnetic hydroxyapatite-functionalized pig manure-derived biochar for the efficient uranium separation | |
CN111085162B (en) | Superfine arsenic removal adsorbent, preparation method thereof and arsenic removal method | |
US11577215B2 (en) | Method for producing absorbent | |
Dastoorian et al. | Fabrication of poorly crystalline hydroxyapatite nano-particles by rapid auto-ignition route as efficient adsorbent for removal of disperse blue dye | |
CN104828869A (en) | Sodium manganese oxide micro-powder and preparation method thereof | |
CN113842883B (en) | Lanthanum-loaded iron carbon nanotube film material for environmental remediation and preparation method and application thereof | |
Xia et al. | Phosphorus hyperaccumulation in nano-MgO using a circular recovery process based on multiple phase transitions from periclase to brucite | |
Bian et al. | Resource recovery of wastewater treatment sludge: synthesis of a magnetic cancrinite adsorbent | |
CN110280227A (en) | MnO2The preparation and its application of the difunctional composite material of/PEI/TA | |
Ni et al. | Complexation-based selectivity of organic phosphonates adsorption from high-salinity water by neodymium-doped nanocomposite | |
CN102886240B (en) | Adsorbent for removing toxic element arsenic in water and application thereof | |
CN103480324B (en) | A kind of mesoporous Fe 3o 4microballoon and methods for making and using same thereof |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
C06 | Publication | ||
PB01 | Publication | ||
C10 | Entry into substantive examination | ||
SE01 | Entry into force of request for substantive examination | ||
GR01 | Patent grant | ||
GR01 | Patent grant |