Nothing Special   »   [go: up one dir, main page]

CN108912338A - A kind of preparation of supermolecule organic frame and in Adsorption water body pollutant application - Google Patents

A kind of preparation of supermolecule organic frame and in Adsorption water body pollutant application Download PDF

Info

Publication number
CN108912338A
CN108912338A CN201810637744.2A CN201810637744A CN108912338A CN 108912338 A CN108912338 A CN 108912338A CN 201810637744 A CN201810637744 A CN 201810637744A CN 108912338 A CN108912338 A CN 108912338A
Authority
CN
China
Prior art keywords
sofs
pollutant
supermolecule organic
supermolecule
organic frame
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Granted
Application number
CN201810637744.2A
Other languages
Chinese (zh)
Other versions
CN108912338B (en
Inventor
林奇
关晓文
王姣
樊彦青
陈燕燕
姚虹
张有明
魏太保
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.)
Northwest Normal University
Original Assignee
Northwest Normal University
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Northwest Normal University filed Critical Northwest Normal University
Priority to CN201810637744.2A priority Critical patent/CN108912338B/en
Publication of CN108912338A publication Critical patent/CN108912338A/en
Application granted granted Critical
Publication of CN108912338B publication Critical patent/CN108912338B/en
Expired - Fee Related legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Classifications

    • CCHEMISTRY; METALLURGY
    • C08ORGANIC MACROMOLECULAR COMPOUNDS; THEIR PREPARATION OR CHEMICAL WORKING-UP; COMPOSITIONS BASED THEREON
    • C08GMACROMOLECULAR COMPOUNDS OBTAINED OTHERWISE THAN BY REACTIONS ONLY INVOLVING UNSATURATED CARBON-TO-CARBON BONDS
    • C08G83/00Macromolecular compounds not provided for in groups C08G2/00 - C08G81/00
    • C08G83/008Supramolecular polymers
    • 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
    • B01J20/22Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising organic material
    • B01J20/26Synthetic macromolecular compounds
    • B01J20/262Synthetic macromolecular compounds obtained otherwise than by reactions only involving carbon to carbon unsaturated bonds, e.g. obtained by polycondensation
    • 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
    • C02F1/285Treatment of water, waste water, or sewage by sorption using synthetic organic 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
    • C02F2101/20Heavy metals or heavy metal compounds
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/30Organic compounds
    • C02F2101/308Dyes; Colorants; Fluorescent agents
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/30Organic compounds
    • C02F2101/34Organic compounds containing oxygen
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/30Organic compounds
    • C02F2101/34Organic compounds containing oxygen
    • C02F2101/345Phenols

Landscapes

  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Polymers & Plastics (AREA)
  • Medicinal Chemistry (AREA)
  • Health & Medical Sciences (AREA)
  • Hydrology & Water Resources (AREA)
  • Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Analytical Chemistry (AREA)
  • Solid-Sorbent Or Filter-Aiding Compositions (AREA)
  • Water Treatment By Sorption (AREA)

Abstract

Present invention design has synthesized a kind of column [5] arene-based supermolecule organic framework materials SOFs-P5G based on naphthalimide functionalization, it is in cyclohexanol, double 4,4 bipyridine salts of column [5] aromatic hydrocarbons and object of main body naphthalimide functionalization are formed with equimolar than self assembly.Supermolecule organic frame SOFs-P5G is shown into extraordinary Adsorption effect to the various organic pollutants in water body.By being monitored with ultra-violet absorption spectrum, SOFs-P5G is calculated, 50% is all larger than to the removal rate of various pollutants, wherein the removal rate to potassium permanganate is up to 99%.The supermolecule organic framework materials SOFs-P5G powder for being adsorbed with pollutant is added in dehydrated alcohol, at 35 ~ 40 DEG C after stirred in water bath 15 minutes, the pollutant being adsorbed is released, it is filtered again, it is dry, so that supermolecule organic framework materials SOFs-P5G is achieved the purpose that Recovery and recycle uses.

Description

A kind of preparation of supermolecule organic frame and the pollutant in Adsorption water body Using
Technical field
Column [5] aromatic hydrocarbons that the present invention relates to a kind of with naphthalimide functionalization(P5N)Based on, double 4,4 bipyridine salts(G) For supermolecule organic frame SOFs-P5G made of object self assembly, it is mainly used for belonging to the separation removal of pollutant in water body In water-treatment technology field.
Background technique
In in the past few decades, by weaving, leather, a large amount of waste water from dyestuff discharge that papermaking and printing industry generate is Lead to serious environmental problem, because most of commercial dyes are all highly toxic, or even carcinogenic by concentrated biological body. Many traditional physico-chemical process have been used for handling dye discoloration.Currently, in the various treatment process of waste water containing dye, Adsorption process has become one of the most useful technology.Various adsorbents such as silica, clay, active carbon and mesoporous silicon oxide Have been used for such processing.Adsorbent material(Such as active carbon)It the use of the organic pollutant in absorption waste water is a kind of environmentally protective Method, but since it is handled, the time is long, and cost recovery is high, therefore this low efficiency for the practical application in industry, spends Cost is too high, and is unfavorable for conveniently practical application.Therefore, removal pollutant rapidly and efficiently becomes one and great chooses The project of war.
Summary of the invention
The object of the present invention is to provide a kind of preparation methods of supermolecule organic frame;
It is a further object of the present invention to provide above-mentioned supermolecule organic frames as adsorbent in Adsorption organic pollutant Application.
One, the preparation of supermolecule organic framework materials
The preparation of supermolecule organic framework materials of the present invention is column [5] aromatic hydrocarbons of main body naphthalimide functionalization in cyclohexanol (P5N)With double 4,4 bipyridine salts of object(G)Assembled with equimolar ratio, is labeled as SOFs-P5G.
Wherein, column [5] aromatic hydrocarbons of main body naphthalimide functionalization(P5N)Structural formula be:
n=1,2,3,4;
Double 4,4 bipyridine salts of object(G)Structure be as follows:
The assembly model of Subjective and Objective is as follows:
The Analysis on Mechanism that supermolecule polymer gel TDPG is formed below by nuclear-magnetism figure, nuclear-magnetism titration hydrogen spectrogram.Fig. 1 is The moiety concentrations nuclear-magnetism figure of P5N.In Fig. 1, from(b)~(g)The concentration of P5N is gradually increased, it can be found that H1-7 is moved to High-Field It is dynamic, illustrate that there are π-π effects between the column aromatic hydrocarbons group of P5N and naphthalimide group and another molecule P5N.Fig. 2 is P5N and G Nuclear-magnetism titrate hydrogen spectrogram.Wherein(a)P5N;(b)~(h)G containing different equivalents.From fig. 2 it can be seen that on object G Hydrogen Proton Ha, Hb, Hc, Hd and He are to low field displacement, while the Hydrogen Proton H6 and H7 in main body P5N column aromatic hydrocarbons group is to High-Field Displacement, illustrates that object G pyridinium moieties enter the cavity of column aromatic hydrocarbons.Main body P5N and object G can be illustrated by the above phenomenon It is assembled by host and guest's recognition reaction and π-π effect, to obtain supermolecule organic framework materials SOFs-P5G.
Two, absorption of the supermolecule organic frame SOFs-P5G to each pollutant
12 clean 50mL volumetric flasks are taken, weigh the contaminant compound adsorbed respectively(Such as:Methylene blue, gold Orange, bismark brown Y, Giemsa stain agent, methyl orange, rhodamine B, tonyred 1, tonyred 2, picric acid, alpha naphthol, permanganic acid Potassium, potassium bichromate)In beaker, adding 10mL distilled water is completely dissolved solid, then respectively liquid relief to ready colorimetric Guan Zhong, is then diluted to 25mL scale with distilled water, and configuration concentration is 1 × 10-3mol·L−1Aqueous solution, for use.
The above-mentioned configured each pollutant aqueous solution of 50uL is pipetted respectively(1.0×10-3mol/L)In 5mL reagent bottle In, distilled water dilution is then added and is settled to 5mL scale, shakes up, forming concentration is 1.0 × 10-5Each pollutant of mol/L is dilute Solution is stood, for use.
12 parts of above-mentioned supermolecule organic frame SOFs-P5G powder prepared are weighed, every part is 2 milligrams, is added separately to Above-mentioned configured concentration is 1.0 × 10-5In each pollutant weak solution of mol/L, it is stirred at room temperature after forty minutes, it is quiet It sets.It was found that the color fade of each pollutant weak solution.Fig. 3 is SOFs-P5G to 12 kinds of pollutant Adsorption efficiency bar shapeds Figure(From left to right:Methylene blue, gold orange, bismark brown Y, Giemsa stain agent, methyl orange, rhodamine B, tonyred 1, tonyred 2, picric acid, alpha naphthol, potassium permanganate, potassium bichromate).As seen from Figure 3, supermolecule organic frame prepared by the present invention SOFs-P5G powder is for pollutant methylene blue, gold orange, bismark brown Y, Giemsa stain agent, methyl orange, rhodamine B, the Sudan Red 1, tonyred 2, picric acid, alpha naphthol, potassium permanganate, potassium bichromate all has good Adsorption effect.By with purple Outer absorption spectrum monitoring, is calculated its removal rate to various pollutants.As a result, its removal rate for all contaminants Both greater than 50 %, wherein the removal rate of potassium permanganate is up to 99 %.
Three, supermolecule organic frame SOFs-P5G desorption
The above-mentioned supermolecule organic framework materials SOFs-P5G powder for being adsorbed with pollutant is added in dehydrated alcohol, 35 ~ Behind stirred in water bath 15 minutes of 40 DEG C, the pollutant being adsorbed is released;It is filtered, it is dry, keep supermolecule organic Frame material SOFs-P5G achievees the purpose that Recovery and recycle uses.Fig. 4 is supermolecule organic framework materials SOFs-P5G to first Base orange(a), rhodamine B(b), picric acid(c), potassium permanganate(d)Removal efficiency bar chart is recycled for multiple times.As shown in Figure 4, For the pollutant in adsorbed water body after supermolecule organic framework materials SOFs-P5G desorption, still there is very high removal Rate.
Four, Adsorption basis mechanism of the SOFs-P5G to each pollutant
By the way that by taking Adsorption of Methyl Orange as an example, We conducted the discussion of adsorption mechanism.We conducted methyl oranges to SOFs- first The nuclear-magnetism titration experiments of P5G(See Fig. 5).All from Fig. 5 it will be seen that peak Hydrogen Proton Ha, Hb, Hc and Hd on pyridiniujm It is displaced to High-Field, the Hydrogen Proton H1, H2, H3 and H4 in methyl orange are displaced to low field, are illustrated in methyl orange and SOFs-P5G Pyridiniujm between exist through the electrostatic interaction of zwitterion(See Fig. 3).Meanwhile also being proved by two-dimentional nuclear-magnetism, such as Shown in Fig. 6, A, B, tetra- reference points of C and D are the Hydrogen Proton H1 in Hydrogen Proton H6 on column aromatic hydrocarbons, H7 and H11 and methyl orange respectively, The reference point of H2, H3 and H4 illustrate there is C-H- π and π-π effect between methyl orange and column aromatic hydrocarbons.It can be pushed away by these phenomenons It surveys, during removing each pollutant, there are a variety of interaction forces(Such as:C-H- π effect, π-π effect, zwitterion Electrostatic interaction etc.), therefore, SOFs-P5G can be used for that pollutant each in aqueous solution is efficiently separated and removed.And it is this Suction-operated is to be formed and with classes of compounds weak interaction force, but these weak interaction forces are easy to be broken It is bad, therefore desorption can be carried out and separate each pollutant, reach the recycling of adsorbent material, this absorption point There is important application value in molecule removal field from performance.
Detailed description of the invention
Fig. 1 is the concentration nucleus magnetic hydrogen spectrum figure of P5N.
The nuclear-magnetism that Fig. 2 is P5N and G titrates hydrogen spectrogram.
Fig. 3 is SOFs-P5G to 12 kinds of pollutant Adsorption efficiency bar charts.
Fig. 4 is SOFs-P5G pairs of supermolecule organic framework materials(a)Methyl orange,(b)Rhodamine B,(c)Picric acid,(d)It is high Removal efficiency bar chart is recycled for multiple times in potassium manganate.
Fig. 5 is that methyl orange titrates hydrogen spectrogram to the nuclear-magnetism of SOFs-P5G.
Fig. 6 is the two-dimentional nuclear-magnetism hydrogen spectrogram of methyl orange and SOFs-P5G.
Specific embodiment
Below by specific embodiment to the preparation of supermolecule organic framework materials SOFs-P5G of the present invention and absorption waste water The performance of middle organic pollutant is described further.
The preparation of embodiment 1, supermolecule organic framework materials SOFs-P5G
(1)The synthesis of main body P5N:In 50ml acetonitrile, 0.58g is added(5×10-3mol)Column [5] aromatic hydrocarbons P5 of bromo, 0.43g(1.5×10-3mol)Naphthalamide derivatives, in 80 DEG C of reaction 48h;To be cooled to room temperature after reaction, rotation Solvent is evaporated off, sample upper prop is mixed, with petroleum ether:Ethyl acetate=10:1~10:5(v/v)Elution, it is solidifying for obtaining yellow solid product Glue factor P5N;Yield is 75.6%.
(2)The synthesis of object G:1.9801g is added in 100ml acetonitrile(1.89 g, 6.3 mmol)1,10- dibromo-decane With 4,4'- bipyridyl(5.56g, 35.7 mmol), it is stirred at reflux at 90 ~ 100 DEG C 18 hours;It is cooled to room temperature, is leaked with Bu Shi Bucket is filtered, and with acetonitrile and ethanol washing 3 ~ 5 times, obtaining 3.3g pistac powdery product is guest compound G.It produces Rate is 86%.
(3)The synthesis of supermolecule organic framework materials SOFs-P5G:In 0.2ml cyclohexanol, main body P5N is added (0.0050g, 4.5 × 10-6mol), object G(0.0047g, 4.5 × 10-6mol), heating makes it completely dissolved, is subsequently cooled to Room temperature, drying, obtains stable supermolecule organic framework materials SOFs-P5G.
Embodiment 2, supermolecule organic frame SOFs-P5G efficiently separating and removing to pollutant
Configuration concentration is 5mL 1 × 10-5Each pollutant of M(Methylene blue, gold orange, bismark brown Y, Giemsa stain agent, first Base orange, rhodamine B, tonyred 1, tonyred 2, picric acid, alpha naphthol, potassium permanganate, potassium bichromate)Aqueous solution;Weigh oversubscription Sub- organic framework materials SOFs-P5G powder weighs 12 parts, and every part is 2 milligrams, is added separately to above-mentioned each pollutant weak solution In, it shakes after forty minutes, stands, take residual supernatant to do and carry out uv-spectrophotometric test, record its absorbance.Then basis Langbobier law calculates the concentration of its residual solution, to calculate eliminating rate of absorption.Supermolecule organic frame SOFs-P5G 1 is shown in Table for various pollutants removal rate:
Embodiment 3, supermolecule organic frame SOFs-P5G recycling
The aqueous solution for the organic framework materials SOFs-P5G powder for having adsorbed each pollutant is filtered, drying and processing.So Dry powder is moved to afterwards in 12 5 milliliters of reagent bottles respectively, 4 milliliters of dehydrated alcohols are added, the water-bath for being 35 degrees Celsius in temperature Middle concussion 15 minutes, discovery aqueous solution color become the color of each pollutant before adsorbing, illustrate organic framework materials SOFs- P5G releases each pollutant of absorption.Then it is once being filtered, with ethanol washing 3 ~ 5 times, drying obtains original The organic framework materials SOFs-P5G powder of beginning.The organic framework materials SOFs-P5G powder of recycling can also carry out repeatedly simultaneously Recycling.

Claims (8)

1. a kind of preparation method of supermolecule organic frame SOFs-P5G, be in cyclohexanol, main body naphthalimide functionalization Column [5] aromatic hydrocarbons is formed with equimolar than self assembly with double 4,4 bipyridine salts of object;
The structural formula of column [5] aromatic hydrocarbons of the main body naphthalimide functionalization is:
n=1,2,3,4;
The structural formula of double 4,4 bipyridine salts of the object is as follows:
2. the preparation method of supermolecule organic frame SOFs-P5G as described in claim 1, it is characterised in that:Main body naphthalimide Double contents of 4,4 bipyridine salts in system of column [5] aromatic hydrocarbons and object of functionalization are 1.5 ~ 2.5g/mL.
3. the supermolecule organic frame SOFs-P5G of method preparation as described in claim 1 is for the pollution in Adsorption water body Object.
4. supermolecule organic frame SOFs-P5G as claimed in claim 3 is for the pollutant in Adsorption water body, feature It is:Pollutant is to have dyestuff.
5. supermolecule organic frame SOFs-P5G as claimed in claim 4 is for the pollutant in Adsorption water body, feature It is:The organic dyestuff be methylene blue, gold orange, bismark brown Y, Giemsa stain agent, methyl orange, rhodamine B, tonyred 1, Tonyred 2.
6. supermolecule organic frame SOFs-P5G as claimed in claim 3 is for the pollutant in Adsorption water body, feature It is:The pollutant is potassium permanganate, potassium bichromate.
7. supermolecule organic frame SOFs-P5G as claimed in claim 3 is for the pollutant in Adsorption water body, feature It is:The pollutant is picric acid, alpha naphthol.
8. supermolecule organic frame SOFs-P5G as claimed in claim 3 is for the pollutant in Adsorption water body, feature It is:The supermolecule organic framework materials SOFs-P5G for having adsorbed pollutant is added to dehydrated alcohol, in 35 ~ 40 DEG C of water-baths Middle stirring can release pollutant, and supermolecule organic framework materials SOFs-P5G is made to reach Recovery and recycle use.
CN201810637744.2A 2018-06-20 2018-06-20 Preparation of supramolecular organic framework and application of supramolecular organic framework in adsorption removal of pollutants in water body Expired - Fee Related CN108912338B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201810637744.2A CN108912338B (en) 2018-06-20 2018-06-20 Preparation of supramolecular organic framework and application of supramolecular organic framework in adsorption removal of pollutants in water body

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201810637744.2A CN108912338B (en) 2018-06-20 2018-06-20 Preparation of supramolecular organic framework and application of supramolecular organic framework in adsorption removal of pollutants in water body

Publications (2)

Publication Number Publication Date
CN108912338A true CN108912338A (en) 2018-11-30
CN108912338B CN108912338B (en) 2020-10-16

Family

ID=64420193

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201810637744.2A Expired - Fee Related CN108912338B (en) 2018-06-20 2018-06-20 Preparation of supramolecular organic framework and application of supramolecular organic framework in adsorption removal of pollutants in water body

Country Status (1)

Country Link
CN (1) CN108912338B (en)

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN109701659A (en) * 2019-01-29 2019-05-03 盐城工学院 Accumulate two-photon Z-type photochemical catalyst and its preparation method and application
CN110938214A (en) * 2019-12-20 2020-03-31 西北师范大学 Supramolecular polymer based on tripodal column [5] arene and preparation and application thereof
CN112242577A (en) * 2020-10-16 2021-01-19 苏州大学 Recycling method of lithium ion battery anode material
CN113097644A (en) * 2021-04-01 2021-07-09 长兴常兴化工有限公司 Preparation method of SOFs-P5G/PVDF lithium ion battery diaphragm
CN116376046A (en) * 2023-05-10 2023-07-04 五邑大学 Method for preparing metal-organic polymer based on cage-shaped supermolecular monomer

Citations (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN106974897A (en) * 2017-02-20 2017-07-25 西北农林科技大学 One kind targeting multi-functional cerium dioxide nano medicine-carried system of stimulating responsive
CN107043461A (en) * 2017-05-14 2017-08-15 西北师范大学 The preparation and application of the supermolecule sensor of the formyl derivative of naphthalene two based on post [5] aromatic hydrocarbons and pyridine functional
CN107536803A (en) * 2017-07-25 2018-01-05 西北农林科技大学 One kind targeting pH GSH double responsiveness multifunctional nano vesica medicine-carried systems
EP3276354A1 (en) * 2016-07-29 2018-01-31 Klinikum rechts der Isar der Technischen Universität München Molecular sensor for nmr/mri based on analyte-dependent spectral changes of temporarily encapsulated hyperpolarized 129xe
CN107936262A (en) * 2017-12-07 2018-04-20 西北师范大学 A kind of preparation and application of supermolecule polymer frame material
CN107935926A (en) * 2017-11-06 2018-04-20 西北师范大学 It can identify the preparation and application of the gelator and its supermolecule polymer gel of fragrant acid isomer
CN108070092A (en) * 2017-11-20 2018-05-25 西北师范大学 The application of supermolecular gel and its identification iron ion and L-Cys of the one kind based on functionalization column [5] aromatic hydrocarbons

Patent Citations (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
EP3276354A1 (en) * 2016-07-29 2018-01-31 Klinikum rechts der Isar der Technischen Universität München Molecular sensor for nmr/mri based on analyte-dependent spectral changes of temporarily encapsulated hyperpolarized 129xe
CN106974897A (en) * 2017-02-20 2017-07-25 西北农林科技大学 One kind targeting multi-functional cerium dioxide nano medicine-carried system of stimulating responsive
CN107043461A (en) * 2017-05-14 2017-08-15 西北师范大学 The preparation and application of the supermolecule sensor of the formyl derivative of naphthalene two based on post [5] aromatic hydrocarbons and pyridine functional
CN107536803A (en) * 2017-07-25 2018-01-05 西北农林科技大学 One kind targeting pH GSH double responsiveness multifunctional nano vesica medicine-carried systems
CN107935926A (en) * 2017-11-06 2018-04-20 西北师范大学 It can identify the preparation and application of the gelator and its supermolecule polymer gel of fragrant acid isomer
CN108070092A (en) * 2017-11-20 2018-05-25 西北师范大学 The application of supermolecular gel and its identification iron ion and L-Cys of the one kind based on functionalization column [5] aromatic hydrocarbons
CN107936262A (en) * 2017-12-07 2018-04-20 西北师范大学 A kind of preparation and application of supermolecule polymer frame material

Non-Patent Citations (2)

* Cited by examiner, † Cited by third party
Title
NAZAROVA A A , SHIBAEVA K S , STOIKOV I I: "Synthesis of the monosubstituted pillar[5]arenes with 1-aminophosphonate fragment", 《PHOSPHORUS SULFUR & SILICON & THE RELATED ELEMENTS》 *
刘丹: "基于柱[5]芳烃配体的金属有机骨架材料的构筑结构与性能研究", 《中国优秀硕士学位论文全文数据库(电子期刊).工程科技I辑》 *

Cited By (9)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN109701659A (en) * 2019-01-29 2019-05-03 盐城工学院 Accumulate two-photon Z-type photochemical catalyst and its preparation method and application
CN109701659B (en) * 2019-01-29 2020-08-25 盐城工学院 Accumulative two-photon Z-type photocatalyst and preparation method and application thereof
CN110938214A (en) * 2019-12-20 2020-03-31 西北师范大学 Supramolecular polymer based on tripodal column [5] arene and preparation and application thereof
CN112242577A (en) * 2020-10-16 2021-01-19 苏州大学 Recycling method of lithium ion battery anode material
CN112242577B (en) * 2020-10-16 2022-03-11 苏州大学 Recycling method of lithium ion battery anode material
CN113097644A (en) * 2021-04-01 2021-07-09 长兴常兴化工有限公司 Preparation method of SOFs-P5G/PVDF lithium ion battery diaphragm
CN113097644B (en) * 2021-04-01 2023-03-31 河南锂动电源有限公司 Preparation method of SOFs-P5G/PVDF lithium ion battery diaphragm
CN116376046A (en) * 2023-05-10 2023-07-04 五邑大学 Method for preparing metal-organic polymer based on cage-shaped supermolecular monomer
CN116376046B (en) * 2023-05-10 2024-08-09 五邑大学 Method for preparing metal-organic polymer based on cage-shaped supermolecular monomer

Also Published As

Publication number Publication date
CN108912338B (en) 2020-10-16

Similar Documents

Publication Publication Date Title
CN108912338A (en) A kind of preparation of supermolecule organic frame and in Adsorption water body pollutant application
Li et al. Metal-organic frameworks as advanced sorbents in sample preparation for small organic analytes
CN106018634B (en) A kind of nitrate anion type hydrotalcite adsorbent is to the absorption of six kinds of phenoxy carboxylic acid herbicides in water and De contamination method
CN107698614B (en) A kind of carborane-diimide derivative and synthetic method and sensor array and preparation method and application based on it
CN109406474A (en) A kind of aggregation-induced emission-molecular engram fluorescent optical sensor preparation method and application detecting rhodamine B
Llaver et al. Analytical developments and applications of ionic liquids for environmental studies
CN109364880A (en) It is a kind of with circulation parsing function supermolecule organic framework materials and removal water body in organic dyestuff application
Huang et al. Fabric phase sorptive extraction: Two practical sample pretreatment techniques for brominated flame retardants in water
Zhang et al. An SPE-assisted BODIPY fluorometric paper sensor for the highly selective and sensitive determination of Cd 2+ in complex sample: Rice
CN106750316A (en) A kind of preparation method of magnetic core-shell nanoparticle surface uranyl molecularly imprinted polymer
CN101343538B (en) Fluorescence silica gel particle and uses thereof
CN110951105A (en) Nicotinamide virtual template surface molecularly imprinted material and preparation method and application thereof
CN105037283B (en) Metal organic frame and its synthetic method and application of the one kind based on Cu (II) ion
Ma et al. High-Performance enrichment and sensitive analysis of bisphenol and its analogues in water and milk using a novel Ni-Based cationic Metal-Organic framework
CN105498721A (en) Aflatoxin molecularly imprinted material and preparation method thereof
Yu et al. Recovery and post-treatment processes for ionic liquids and deep eutectic solvents
Zheng et al. A Novel Metal‐Organic Framework Composite, MIL‐101 (Cr)@ MIP, as an Efficient Sorbent in Solid‐Phase Extraction Coupling with HPLC for Tribenuron‐Methyl Determination
Chang et al. ICP-OES determination of trace metal ions after preconcentration by 4-(8-hydroxy-5-quinolylazo) naphthalenesulfonic acid modified silica gel
CN109847407B (en) Purification method of valrubicin
Öter et al. Synthesis and characterization of a molecularly ımprinted polymer adsorbent for selective solid-phase extraction from wastewater of propineb
CN109776811A (en) A kind of preparation and application of glyphosate molecular imprinted solid phase extraction cartridge
CN108693272B (en) Method for analyzing and preparing N- (p-toluenesulfonyl) -L-alanine and enantiomer thereof by HPLC method
CN110483803A (en) The application of supermolecule organic frame and its absorption organic dyestuff of the one kind based on twin columns [5] aromatic hydrocarbons
CN1128663C (en) Application of beta-cyclodextrin bonded silicone gel as solid phase extraction adsorption medium
Khani et al. Mixed Magnetic Dispersive Micro‐Solid Phase–Cloud Point Extraction of Sunset Yellow in Food and Pharmaceutical Samples

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
GR01 Patent grant
GR01 Patent grant
CF01 Termination of patent right due to non-payment of annual fee

Granted publication date: 20201016

Termination date: 20210620

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