CN108940187A - Magnetic mesoporous nanosphere and preparation method thereof for dephosphorization load lanthanum hydroxide - Google Patents

Magnetic mesoporous nanosphere and preparation method thereof for dephosphorization load lanthanum hydroxide Download PDF

Info

Publication number
CN108940187A
CN108940187A CN201810698172.9A CN201810698172A CN108940187A CN 108940187 A CN108940187 A CN 108940187A CN 201810698172 A CN201810698172 A CN 201810698172A CN 108940187 A CN108940187 A CN 108940187A
Authority
CN
China
Prior art keywords
sio
added
preparation
load
solvent
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
Application number
CN201810698172.9A
Other languages
Chinese (zh)
Inventor
钱书杰
李元梓
陈磊
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.)
Nanjing University of Science and Technology
Original Assignee
Nanjing University of Science and Technology
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 Nanjing University of Science and Technology filed Critical Nanjing University of Science and Technology
Priority to CN201810698172.9A priority Critical patent/CN108940187A/en
Publication of CN108940187A publication Critical patent/CN108940187A/en
Pending legal-status Critical Current

Links

Classifications

    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J20/00Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
    • B01J20/02Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material
    • B01J20/10Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising silica or silicate
    • B01J20/103Solid 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
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J20/00Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
    • B01J20/02Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material
    • B01J20/0203Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising compounds of metals not provided for in B01J20/04
    • B01J20/0207Compounds of Sc, Y or Lanthanides
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J20/00Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
    • B01J20/02Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material
    • B01J20/06Solid 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
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J20/00Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
    • B01J20/28Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof characterised by their form or physical properties
    • B01J20/28002Solid 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
    • B01J20/28009Magnetic properties
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/28Treatment of water, waste water, or sewage by sorption
    • C02F1/281Treatment of water, waste water, or sewage by sorption using inorganic sorbents
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/10Inorganic compounds
    • C02F2101/105Phosphorus compounds

Landscapes

  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Analytical Chemistry (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Inorganic Chemistry (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Hydrology & Water Resources (AREA)
  • Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Catalysts (AREA)
  • Solid-Sorbent Or Filter-Aiding Compositions (AREA)

Abstract

The invention discloses a kind of magnetic mesoporous nanospheres and preparation method thereof for dephosphorization load lanthanum hydroxide.This method is by Fe3O4@SiO2@mSiO2It is mixed with lanthanide series compound according to 30%~200% ratio, second alcohol and water is added, lye is added dropwise while stirring at room temperature after ultrasonic treatment makes to react completely, then takes out and carries out Magneto separate and drying, La (OH)3Load is completed.Preparation method of the invention is simple and convenient, and synthesis cost is low, has innovation, and the specific grain surface product prepared is big, and adsorption capacity and rate of adsorption performance are excellent, while having magnetism, are easily isolated and recycle, reusable.

Description

Magnetic mesoporous nanosphere and preparation method thereof for dephosphorization load lanthanum hydroxide
Technical field
The present invention relates to a kind of magnetic mesoporous nanospheres and preparation method thereof for dephosphorization load lanthanum hydroxide, belong to water Contamination control field.
Background technique
Since water eutrophication phenomenon caused by phosphorus content is excessively high in water body is got worse, water body dephosphorized technology is drawn Extensive concern is played.Currently, having chemical precipitation method, bioanalysis and suction for removing phosphatic method in water body mainly both at home and abroad Attached method.Chemical method is although easy to operate, and phosphor-removing effect is significant, will not discharge phosphorus again, but operating cost is high, remaining metal Ion is easy to generate murder by poisoning to aqueous bio.Bioanalysis phosphor-removing effect is unstable, is easy by water temperature, dissolved oxygen, nitric acid The influence of the factors such as salt content, system operating load.There are respective advantage and disadvantage for both the above method, and not can be carried out phosphorus Recycling.
Absorption method dephosphorization is the parent using certain porous or large specific surface area solid material to phosphate anion in water And adsorption capacity, to realize the purpose removed to it.In comparison, this method economical and efficient, absorption are stablized, technique letter It is single, it is reliable for operation, and may be implemented to separate phosphorus from water body, recycling phosphor resource is to re-use.It can be used as The supplement of biological phosphate-eliminating can also be used as individual phosphorus removing method.
The selection criteria of dephosphorization adsorbent mainly has: adsorption capacity is high, selectivity is strong, the rate of adsorption is fast, resists other ions Interference performance is strong, unharmful substance dissolution, performance is stable, renewable is strong etc..Currently, utilizing the material of absorption method dephosphorization Active charcoal, biomass, metal oxide, silicon-based mesoporous molecular sieve, clay mineral etc..Mesoporous nano-grain is because it is with surface With interfacial effect, high specific surface area, rule cellular structure and nanometer range can modulation aperture, by the shadow of these factors It rings, the characteristic that this kind of particle has conventional material no.However existing mesoporous nano-grain has a defect that the suction for phosphorus It is attached indifferent, it is influenced, is adsorbed unstable by other ions.
Summary of the invention
The purpose of the present invention is to provide a kind of magnetic mesoporous nanosphere for dephosphorization load lanthanum hydroxide and its preparations Method.
Realize that the solution of the object of the invention is as follows:
A kind of preparation method of the magnetic mesoporous nanosphere for dephosphorization load lanthanum hydroxide, includes the following steps: step 1,
By FeCl3As source of iron, trisodium citrate is as stabilizer, in ethylene glycol simultaneously by using the reaction of hot solvent method
Magneto separate generates Fe3O4Nano particle;
Step 2, by Fe3O4Nano particle is added in aqueous isopropanol, is ultrasonically treated, and ammonium hydroxide and tetrem base is added dropwise Silicate (TEOS), mechanical stirring and Magneto separate obtain Fe3O4@SiO2
Step 3, by Fe3O4@SiO2It is added in alkali system, using surfactant templates and catalyst, mechanical stirring is led Water-oil phase layering is caused, to have mesoporous dendroid SiO2It is wrapped in Fe3O4@SiO2The surface of nanosphere;
Step 4, by Fe3O4@SiO2@mSiO2It is mixed with lanthanide series compound, solvent is added, makes Fe3O4@SiO2@mSiO2And lanthanum Based compound is evenly dispersed in a solvent, and lye, which is added dropwise, in ultrasonic treatment back mechanical stirring side makes to react completely, magnetic point after taking-up From and it is dry, complete load.
Preferably, in step 1, FeCl3Dosage is 2.5~4g, and trisodium citrate dosage is 0.8~1.6g, and ethylene glycol is used Amount is 80~120ml.
Preferably, in step 2, sonication treatment time is 30 minutes.
Preferably, in step 3, surfactant templates use hexadecyltrimethylammonium chloride (CTAC) or cetyl Trimethylammonium bromide (CTAB), catalyst use triethanolamine (TEA) or ammonium hydroxide, and it is triethanolamine that above-mentioned alkali system, which is catalyst, (TEA) or ammonium hydroxide provides.
Preferably, in step 4, lanthanide series compound is La (NO3)3·6H2O or LaCl3·7H2O, La (NO3)3·6H2O or LaCl3·7H2O and Fe3O4@SiO2@mSiO2Ratio use 30%~200%.
Preferably, in step 4, solvent is second alcohol and water.
Compared with prior art, the present invention the advantage is that:
(1) the method for the present invention is simple and convenient, and synthesis cost is low, has novelty;
(2) the specific grain surface product of the method for the present invention preparation is big, and adsorption capacity and rate of adsorption performance are excellent, while having magnetic Property, it is easily isolated and recycles, it is reusable.
Detailed description of the invention
Fig. 1 is the scanning electron microscope (SEM) photograph for the magnetic mesoporous nano particle that load has lanthanum hydroxide.
Fig. 2 is the transmission electron microscope picture for the magnetic mesoporous nano particle that load has lanthanum hydroxide.
Specific embodiment
Present invention is further described in detail with reference to the accompanying drawings and examples.
Embodiment 1
Step 1, by 3.25gFeCl3It is added in 100ml ethylene glycol with 1.2g trisodium citrate, 6g acetic acid is then added Sodium stirs 1h energetically and forms clarified solution, is put into the hydrothermal reaction kettle of 120ml polytetrafluoroethylene (PTFE), is placed in baking oven at 200 DEG C of heat 10h is managed, taking-up is cooled to room temperature, obtains black product.It with ethyl alcohol and is washed three times, and with being dried in vacuo, obtains Fe3O4 Nano particle.
Step 2, the Fe of step 1 is taken3O4Nano particle 0.3g is added in 300ml aqueous isopropanol, ultrasonic treatment 30min, then 40 DEG C of oil baths, while 600rpm mechanical stirring then instill ammonium hydroxide and 36ml that 20ml mass fraction is 28% Water, after stirring 30min, the TEOS of fast injection 1ml reacts and continues 2h, then carried out Magneto separate, then with ethyl alcohol and washing Three times, and with being dried in vacuo, one layer of SiO has been wrapped up2Fe3O4Mesoporous nano-grain.
Step 3, the particle for taking 0.1g step 2 to obtain is added in TEA the and 54ml water of the CTAC and 0.2ml of 6g, ultrasound 30min, 300rpm stirs 1h at 60 DEG C, is slowly added into the mixed solution of 4mlTEOS and 36ml hexamethylene, the oil bath at 60 DEG C 12h, then Magneto separate collects product, and three times with ethyl alcohol and washing.It is calcined into 400min at 600 DEG C, is loaded Two layers of SiO2Fe3O4Mesoporous nano-grain.
Step 4, the La (NO of the particle 60mg and 30mg that take step 3 to obtain3)3·6H220ml ethyl alcohol, ultrasound is added in O 30min, 300rpm is stirred at room temperature, while the NaOH that 12ml pH is 13 is added dropwise, and is reacted and is continued 4h, is taken out and is carried out Magneto separate, then Vacuum drying, La (OH)3Load is completed.
Embodiment 2
The present embodiment is identical as first three step of embodiment 1, the difference is that 60mg LaCl is added in step 43·7H2O, Solvent uses 10ml ethyl alcohol and 10ml water, and ultrasonic 30min, 300rpm is stirred at room temperature, while it is 13 that 12ml pH, which is added dropwise, NaOH reacts and continues 4h, takes out and carries out Magneto separate, then is dried in vacuo, La (OH)3Load is completed.
Embodiment 3
The present embodiment is identical as first three step of embodiment 1, the difference is that 90mg La (NO is added in step 43)3· 6H2O, solvent use 20ml water, and ultrasonic 30min, 300rpm is stirred at room temperature, while the NaOH that 12ml pH is 13 is added dropwise, reaction Continue 4h, takes out and carry out Magneto separate, then be dried in vacuo, La (OH)3Load is completed.
Comparative example 1
Particle 60mg and the La (NO of step 3 in Example 13)3·6H2O is mixed according to mass fraction 5:1, is added 10ml ethyl alcohol and 10ml water, ultrasonic 30min, 300rpm is stirred at room temperature, while the NaOH that 12ml pH is 13 is added dropwise, and reaction is held Continuous 4h, takes out and carries out Magneto separate, then be dried in vacuo, loaded La (OH)3Magnetic mesoporous particle.
Phosphorus adsorption experiment is carried out with material at this time, since the doping of lanthanum is very few, adsorption effect is undesirable.
Comparative example 2
La (the NO of the particle 60mg and 60mg of step 3 in Example 13)3·6H210ml ethyl alcohol, ultrasound is added in O mixing 30min, 300rpm stirring for 24 hours, after evaporating to solvent, places it at 600 DEG C and calcines 400min, loaded at 80 DEG C La (OH)3Magnetic mesoporous particle.
Phosphorus adsorption experiment is carried out with material at this time, since obvious agglomeration occurs for particle, adsorption effect is caused to be paid no attention to Think.
In Examples 1 to 3, synthetic nano particle evaluates the adsorption effect of phosphorus with adsorption isotherm experiment, absorption Data are fitted with Langmuir model and Freundlich model, the isothermal adsorption adsorbed such as the nano particle of table 1 to phosphorus Shown in model parameter table.
Table 1

Claims (7)

1. a kind of preparation method of the magnetic mesoporous nanosphere for dephosphorization load lanthanum hydroxide, which is characterized in that including as follows Step:
Step 1, by FeCl3As source of iron, trisodium citrate is reacted in ethylene glycol by using hot solvent method as stabilizer And Magneto separate generates Fe3O4Nano particle;
Step 2, by Fe3O4Nano particle is added in aqueous isopropanol, is ultrasonically treated, and ammonium hydroxide and tetraethyl orthosilicic acid is added dropwise Salt, mechanical stirring and Magneto separate obtain Fe3O4@SiO2
Step 3, by Fe3O4@SiO2It is added in alkali system, using surfactant templates and catalyst, mechanical stirring leads to oil Water two phase stratification, to have mesoporous dendroid SiO2It is wrapped in Fe3O4@SiO2The surface of nanosphere;
Step 4, by Fe3O4@SiO2@mSiO2It is mixed with lanthanide series compound, solvent is added, makes Fe3O4@SiO2@mSiO2With group of the lanthanides It is evenly dispersed in a solvent to close object, lye, which is added dropwise, in ultrasonic treatment back mechanical stirring side makes to react completely, and Magneto separate is simultaneously after taking-up It is dry, complete load.
2. the method according to claim 1, wherein in step 1, FeCl3Dosage is 2.5~4g, trisodium citrate Dosage is 0.8~1.6g, and ethylene glycol dosage is 80~120ml.
3. the method according to claim 1, wherein sonication treatment time is 30 minutes in step 2.
4. the method according to claim 1, wherein surfactant templates use cetyl three in step 3 Ammonio methacrylate or cetyl trimethylammonium bromide, catalyst use triethanolamine or ammonium hydroxide.
5. the method according to claim 1, wherein the lanthanide series compound is La (NO in step 43)3· 6H2O or LaCl3·7H2O, La (NO3)3·6H2O or LaCl3·7H2O and Fe3O4@SiO2@mSiO2Ratio using 30%~ 200%.
6. the method according to claim 1, wherein the solvent is second alcohol and water in step 4.
7. a kind of load the magnetic mesoporous of lanthanum hydroxide for dephosphorization based on method described in any one of claims 1-6 preparation Nanosphere.
CN201810698172.9A 2018-06-29 2018-06-29 Magnetic mesoporous nanosphere and preparation method thereof for dephosphorization load lanthanum hydroxide Pending CN108940187A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201810698172.9A CN108940187A (en) 2018-06-29 2018-06-29 Magnetic mesoporous nanosphere and preparation method thereof for dephosphorization load lanthanum hydroxide

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201810698172.9A CN108940187A (en) 2018-06-29 2018-06-29 Magnetic mesoporous nanosphere and preparation method thereof for dephosphorization load lanthanum hydroxide

Publications (1)

Publication Number Publication Date
CN108940187A true CN108940187A (en) 2018-12-07

Family

ID=64484367

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201810698172.9A Pending CN108940187A (en) 2018-06-29 2018-06-29 Magnetic mesoporous nanosphere and preparation method thereof for dephosphorization load lanthanum hydroxide

Country Status (1)

Country Link
CN (1) CN108940187A (en)

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN110947363A (en) * 2019-12-04 2020-04-03 四川农业大学 Magnetic-drive light carbon sponge for oil-water separation and preparation method thereof
CN112844300A (en) * 2019-11-28 2021-05-28 南京理工大学 Magnetic nanoparticles for removing glyphosate in water body and preparation method thereof
CN115475597A (en) * 2022-08-10 2022-12-16 中国地质大学(武汉) Core-shell magnetic mesoporous silica material, method for preparing same by using iron tailings and application of core-shell magnetic mesoporous silica material

Citations (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102247804A (en) * 2011-05-20 2011-11-23 上海大学 Preparation method of active carbon fiber phosphorous removing agent carrying lanthanum hydroxide

Patent Citations (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102247804A (en) * 2011-05-20 2011-11-23 上海大学 Preparation method of active carbon fiber phosphorous removing agent carrying lanthanum hydroxide

Non-Patent Citations (1)

* Cited by examiner, † Cited by third party
Title
JIANPING YANG ET AL: ""Monodisperse core-shell structured magnetic mesoporous aluminosilicate nanospheres with large dendritic mesochannels"", 《NANO RESEARCH》 *

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN112844300A (en) * 2019-11-28 2021-05-28 南京理工大学 Magnetic nanoparticles for removing glyphosate in water body and preparation method thereof
CN110947363A (en) * 2019-12-04 2020-04-03 四川农业大学 Magnetic-drive light carbon sponge for oil-water separation and preparation method thereof
CN115475597A (en) * 2022-08-10 2022-12-16 中国地质大学(武汉) Core-shell magnetic mesoporous silica material, method for preparing same by using iron tailings and application of core-shell magnetic mesoporous silica material
CN115475597B (en) * 2022-08-10 2024-03-29 中国地质大学(武汉) Core-shell magnetic mesoporous silica material, method for preparing material by using iron tailings and application of material

Similar Documents

Publication Publication Date Title
CN104998623B (en) A kind of composite magnetic nano particle adsorbent and its preparation method and application
CN105148852B (en) A kind of sulfhydryl modified magnetic MOFs adsorbents and its preparation method and application
CN108940187A (en) Magnetic mesoporous nanosphere and preparation method thereof for dephosphorization load lanthanum hydroxide
Zhao et al. Preparation of molecularly imprinted polymers based on magnetic carbon nanotubes for determination of sulfamethoxazole in food samples
WO2019237619A1 (en) Magnetic ferromanganese oxide-loaded mesoporous cellulose biochar composite material, preparation method therefor and use thereof
CN112316906B (en) Preparation method of ferromagnetic amino-modified lanthanide metal organic framework material and application of ferromagnetic amino-modified lanthanide metal organic framework material in adsorption dephosphorization
CN110773127B (en) Hydrophobic active carbon material, preparation method and application thereof
CN101599335B (en) Oxidation resistant dimethyl silicon oil based magnetic fluid and preparation method thereof
CN104722276B (en) A kind of melon ring/graphene oxide magnetic composite and preparation method thereof
US9480967B2 (en) Metal organic framework adsorbent for solar adsorption refrigeration
CN103920473B (en) The preparation method of carbon modifying titanium dioxide composite magnetic nano adsorber
CN106732358B (en) A kind of biomass carbonization microballoon loading iron oxide and its preparation and application
CN106955716B (en) A kind of magnetic coupling diatomite material and preparation method thereof
CN106824069B (en) For handling the preparation method of the rear-earth-doped iron Carbon Materials of arsenic-containing waste water
CN102063988A (en) Magnetic clay material and preparation method thereof
CN109126746A (en) A kind of preparation method of magnetism lignosulfonates adsorbent material
Li et al. Synthesis and application of core–shell magnetic metal–organic framework composites Fe 3 O 4/IRMOF-3
CN107376852A (en) A kind of preparation method of@FP composite adsorbing materials of HKUST 1 and its application in adsorption cleaning handles lead waste water
CN107774232A (en) A kind of magnetic active carbon mixture of the ball containing charcoal and preparation method thereof
Wang et al. Preparation of egg white@ zeolitic imidazolate framework-8@ polyacrylic acid aerogel and its adsorption properties for organic dyes
CN106824090B (en) Preparation method and application of novel magnetic metal organic framework composite material
CN110124640A (en) The application of the compound and preparation and adsorption and dephosphorization of lanthanum molybdate and ferrimagnet
Molavi et al. Green Synthesis of Cerium-Based Metal–Organic Framework (Ce-UiO-66 MOF) for Wastewater Treatment
CN105817211A (en) Congo red dye adsorbent, preparation and method for treating Congo red dye wastewater with same
CN106378111B (en) A kind of magnetic Fe with nucleocapsid3O4/ PMMA nano-compound adsorbents and preparation method thereof

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

Application publication date: 20181207

RJ01 Rejection of invention patent application after publication