CN113831491A - Preparation method and adsorption application of pyrimidazole covalent organic framework - Google Patents

Preparation method and adsorption application of pyrimidazole covalent organic framework Download PDF

Info

Publication number
CN113831491A
CN113831491A CN202111158517.XA CN202111158517A CN113831491A CN 113831491 A CN113831491 A CN 113831491A CN 202111158517 A CN202111158517 A CN 202111158517A CN 113831491 A CN113831491 A CN 113831491A
Authority
CN
China
Prior art keywords
organic framework
covalent organic
pyrimidazole
adsorption
uranyl
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
CN202111158517.XA
Other languages
Chinese (zh)
Other versions
CN113831491B (en
Inventor
邱建丁
张程蓉
梁汝萍
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.)
Nanchang University
Original Assignee
Nanchang 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 Nanchang University filed Critical Nanchang University
Priority to CN202111158517.XA priority Critical patent/CN113831491B/en
Publication of CN113831491A publication Critical patent/CN113831491A/en
Application granted granted Critical
Publication of CN113831491B publication Critical patent/CN113831491B/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Images

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
    • C08G16/00Condensation polymers of aldehydes or ketones with monomers not provided for in the groups C08G4/00 - C08G14/00
    • C08G16/02Condensation polymers of aldehydes or ketones with monomers not provided for in the groups C08G4/00 - C08G14/00 of aldehydes
    • C08G16/025Condensation polymers of aldehydes or ketones with monomers not provided for in the groups C08G4/00 - C08G14/00 of aldehydes with heterocyclic organic compounds
    • C08G16/0268Condensation polymers of aldehydes or ketones with monomers not provided for in the groups C08G4/00 - C08G14/00 of aldehydes with heterocyclic organic compounds containing nitrogen in the ring
    • 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

Landscapes

  • Chemical & Material Sciences (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Organic Chemistry (AREA)
  • Health & Medical Sciences (AREA)
  • Medicinal Chemistry (AREA)
  • Polymers & Plastics (AREA)
  • Analytical Chemistry (AREA)
  • Solid-Sorbent Or Filter-Aiding Compositions (AREA)

Abstract

本发明公开了一种嘧啶唑共价有机框架的制备方法及吸附应用,属于环境保护技术领域。本发明以1,3,5‑三(3‑氟‑4‑甲酰基苯基)苯、1,3,5‑三(4‑氰基‑4,4‑联苯)苯和2‑氨基‑4‑羧基吡啶为原料,构建了一种羧酸官能化的嘧啶唑基共价有机框架制备方法。嘧啶唑基共价有机框架的内孔径略大于铀的直径,可以实现对铀的选择性尺寸匹配吸附,大大降低了质子化效应;同时,嘧啶唑基共价有机框架具有规则的多孔通道和优异的亲水性,可促进铀酰离子的扩散,使其具有高的吸附容量和快速的吸附动力学。本发明方法简单、成本低、制备的材料结构明确且亲水性好,可高效吸附铀酰离子,具有良好的应用前景。

Figure 202111158517

The invention discloses a preparation method and adsorption application of a pyrimidazole covalent organic framework, and belongs to the technical field of environmental protection. The present invention uses 1,3,5-tris(3-fluoro-4-formylphenyl)benzene, 1,3,5-tris(4-cyano-4,4-biphenyl)benzene and 2-amino- Using 4-carboxypyridine as a raw material, a preparation method of a carboxylic acid-functionalized pyrimidine azolyl covalent organic framework was constructed. The inner pore size of the pyrimidineazole-based covalent organic framework is slightly larger than the diameter of uranium, which can achieve selective size-matching adsorption of uranium and greatly reduce the protonation effect; at the same time, the pyrimidineazole-based covalent organic framework has regular porous channels and excellent The hydrophilicity can promote the diffusion of uranyl ions, resulting in high adsorption capacity and fast adsorption kinetics. The method of the invention is simple, low in cost, and the prepared material has a clear structure and good hydrophilicity, can efficiently adsorb uranyl ions, and has a good application prospect.

Figure 202111158517

Description

Preparation method and adsorption application of pyrimidazole covalent organic framework
Technical Field
The invention relates to the technical field of environmental protection, in particular to a preparation method and adsorption application of a pyrimidazole covalent organic framework.
Background
Along with the rapid development of nuclear power, the spent fuel generated by the nuclear power station is continuously accumulated, and the spent fuel contains a large amount of fissile nuclides (A), (B)235Uranium and239plutonium, etc.) and convertible nuclides (mainly plutonium, etc.)238Uranium), which is a valuable nuclear resource, wherein uranium is a key element in nuclear fuel, but is also a highly toxic and radioactive environmental pollutant. Due to widespread use of nuclear power, large-scale uranium mining, nuclear accidents, and improper disposal of nuclear waste, large quantities of radioactive uranium permeate the environment primarily in the form of uranyl ions (Xiao, f.et al, Smart sonic crystalline hydrogel material for uranyl monitoring and removal in water, adv.funct.mater.2017,27,1702147). Therefore, a stable and efficient uranium adsorbent is of great importance for environmental protection and social development. Porous materials, such as Porous Organic Polymers (POPs) (Xu, M.et al, high throughput connected microporus polymers for current acquisition and detection of uranium, J.Mater.chem.A.2019,7,11214), Metal Organic Frameworks (MOFs) (Liu, W.et al, high throughput connected and selective urea acquisition in raw water systems using a luminescence detection agent, and any other suitable adsorbent material may be used as the adsorbent for uranium (U.S.A.A.. However, the performance of amorphous POPs is affected by irregular pores, most of which are buried (Aguila, b.et al, effective polymer capture using functional polymer. adv.mater.2017,29,1700665), hindering rapid mass transfer. Despite their regular porosity and good crystal structure, stability under extreme conditions (acid, base, temperature and radiation) remains a challenge (Xu, l.et al, Nano-MOF technique for influencing urea metabolism, ACS appl.mater.interfaces.2019,11,21619). High stability is particularly important for extracting uranyl ions, so that development of a uranyl ion adsorbing material with high adsorption capacity, good selectivity and stability is very important.
Covalent organic framework materials (COFs) are an emerging class of porous crystalline materials connected by covalent bonds (p.j.waller, f.gandara and o.m.yaghi, Acc, Chemistry of covalent organic frameworks, chem.res.2015,48,3053). COFs are considered to adsorb uranium due to their regular porosity, large specific surface area and excellent stabilityExcellent candidate material for the same. Although good progress has been made in the research of adsorbents based on amidoxime COFs, vanadium has a greater affinity for amidoximes than uranium and, during post-amidoxime modification, reduces the crystallinity and porosity of COFs (w. -r.cui, c. -r.zhang, w.jiang, f. -f.li, r. -p.liang, j.liu, j. -d.qiu, Regenerable and stable2carbon-conjugated scientific frames for selective detection and extraction of uranium, nat. Commun.2020,11,436). Therefore, a proper design thought and a construction method are found to solve the problems faced by the current amidoxime group COFs, and the method is an important breakthrough point of applying the COFs material to uranium adsorption research.
Disclosure of Invention
The invention aims to provide a preparation method of a pyrimidine azole covalent organic framework with a unique pore structure and an application of the pyrimidine azole covalent organic framework in adsorption of uranyl ions. The carboxylic acid functionalized pyrimidinyloxy covalent organic frameworks are prepared by using 1,3, 5-tris (3-fluoro-4-formylphenyl) benzene, 1,3, 5-tris (4-cyano-4, 4-biphenyl) benzene and 2-amino-4-carboxypyridine as raw materials. The carboxyl groups on the carboxylic acid functionalized pyrimidinyloxy covalent organic frameworks can coordinate with uranyl ions; the unique inner hole structure of the pyrimidine-based covalent organic framework is beneficial to size matching of uranyl ions, selective size matching adsorption of the uranyl ions can be realized, and adsorption selectivity of the uranyl ions is improved; the pyrimidyl covalent organic framework has regular porous channels and excellent hydrophilicity, and can promote diffusion of uranyl ions, so that the pyrimidyl covalent organic framework has high adsorption capacity and rapid adsorption kinetics. The method not only can provide a new idea for the design and regulation of the microstructure of the adsorption material, but also provides a new way for preparing the high-efficiency uranium adsorbent. At present, no report on the synthesis of a carboxylic acid functionalized pyrimidine azole covalent organic framework and the adsorption of uranyl ions is found.
The invention is realized by the following technical scheme:
a preparation method of a pyrimidazole covalent organic framework comprises the following steps: the preparation method adopts a one-pot method strategy under solvothermal conditions to prepare the carboxylic acid functionalized pyrimidazole covalent organic framework, takes 1,3, 5-tri (3-fluoro-4-formylphenyl) benzene, 1,3, 5-tri (4-cyano-4, 4-biphenyl) benzene and 2-amino-4-carboxypyridine as raw materials, and reacts under certain conditions to form the carboxylic acid functionalized pyrimidazole covalent organic framework, and comprises the following specific steps:
1) adding 1,3, 5-tri (3-fluoro-4-formylphenyl) benzene, 1,3, 5-tri (4-cyano-4, 4-biphenyl) benzene and 2-amino-4-carboxypyridine into a reaction container, adding a catalyst and an organic solvent, performing ultrasonic treatment on the mixed solution, and uniformly mixing to obtain a reaction mixed solution;
2) degassing a reaction container filled with reaction mixed liquid through three times of freezing-pumping-unfreezing circulation, sealing flame, placing the reaction container in an environment with the temperature of 120 ℃ for reaction for 4 to 6 days, and cooling the reaction container to room temperature to obtain a reaction product;
3) and (3) separating a precipitate from the reaction product by vacuum filtration, washing the precipitate with ethanol, draining the precipitate to obtain a solid, and drying the solid at 80 ℃ in vacuum for 12 hours to prepare the carboxylic acid functionalized pyrimidineazole covalent organic framework.
Preferably, the molar ratio of 1,3, 5-tris (3-fluoro-4-formylphenyl) benzene, 1,3, 5-tris (4-cyano-4, 4-biphenyl) benzene and 2-amino-4-carboxypyridine in step 1) is 1: (0.5-2.0): (2.5-4.0).
Preferably, the catalyst in step 1) is p-toluenesulfonic acid.
Preferably, the organic solvent in the step 1) is one or more of ethanol, mesitylene, o-dichlorobenzene and dichloromethane.
The invention also provides application of the pyrimidazole covalent organic framework in adsorption of uranyl ions, which comprises the steps of adding the pyrimidazole covalent organic framework into aqueous solutions containing different concentrations of uranyl ions, oscillating for 12 hours by using a constant-temperature oscillator, filtering by using a 0.22-micrometer microporous filter membrane, collecting filtrate, measuring the content of residual uranyl ions in the filtrate by using inductively coupled plasma mass spectrometry, and calculating the adsorption capacity of the pyrimidazole covalent organic framework on the uranyl ions.
Preferably, the concentration range of the aqueous solution of the uranyl ions with different concentrations is 0-500 mg/L.
Preferably, the pH of the aqueous solution containing different concentrations of uranyl ions is adjusted to 2.0 to 6.0, more preferably 5.0, with nitric acid or sodium hydroxide solution before mixing with the covalent organic framework of pyrimidazole.
Preferably, the adsorption capacity is calculated by the following formula: q. q.st=(Co-Ct) M × V; wherein V is the volume of the solution, unit L, m is the amount of covalent organic framework used, unit g, CoIs the initial concentration of uranyl ions and the unit mg/L, CtIs the equilibrium concentration of uranyl ions and the unit mg/L.
Compared with the prior art, the invention has the beneficial effects that:
(1) the carboxylic acid functionalized pyrimidazole covalent organic framework is synthesized by a solvothermal one-pot method, and the method has the advantages of simplicity, low cost, strong stability and good hydrophilicity.
(2) Carboxyl on the pyrimidine azole covalent organic framework prepared by the invention can coordinate with uranyl ions, and selective combination of the uranyl ions is facilitated.
(3) The pyrimidine azole covalent organic framework prepared by the invention can form a unique carboxylic acid functionalized nano pocket structure, and is beneficial to selectively combining uranyl ions.
(4) The internal aperture of the pyrimidine azole covalent organic framework nano pocket prepared by the invention is slightly larger than the diameter of the uranyl hydrate ion, and the size matching adsorption of the uranyl hydrate ion can be realized, so that the protonation effect is greatly reduced, and the selective adsorption performance of the uranyl hydrate ion is improved.
(5) The pyrimidine azole-based covalent organic framework prepared by the invention has regular porous channels and excellent hydrophilicity, can promote diffusion of uranyl ions, has high adsorption capacity and rapid adsorption kinetics, and has good application prospects.
Drawings
FIG. 1 is a schematic diagram of the synthetic route of FP-TZ-AAC.
FIG. 2 is a Fourier transform Infrared Spectroscopy (FT-IR) plot of FP, TZ, AAC and FP-TZ-AAC.
FIG. 3 shows PXRD patterns of FP, TZ, AAC and FP-TZ-AAC measured in experiments.
FIG. 4 is a graph showing adsorption capacities of FP-TZ-AAC for uranyl ions at different pH values.
FIG. 5 is an adsorption isotherm diagram of uranyl ions by FP-TZ-AAC.
Detailed Description
The technical solution of the present invention will be described clearly and completely with reference to the following examples, which are only a part of the examples of the present invention, but not all of them, which are conventional processes unless otherwise specified, and the raw materials which are commercially available from the public unless otherwise specified. All other embodiments, which can be derived by a person skilled in the art from the embodiments of the present invention without making creative efforts, fall within the protection scope of the present invention.
Example 1: preparation and characterization of pyrimidazole covalent organic frameworks
1,3, 5-tris (3-fluoro-4-formylphenyl) benzene (Fp) (22.3mg, 0.05mmol), 1,3, 5-tris (4-cyano-4, 4-biphenyl) benzene (TZ) (17.6mg, 0.046mmol), 2-amino-4-carboxypyridine (AAC) (24.9mg, 0.180mmol) and p-toluenesulfonic acid (7.0mg, 0.037mmol) were added to a Pyrex tube, ethanol (0.1mL) and mesitylene (0.3mL) were added, the mixture was sonicated for 10 minutes to mix well, degassed by three freeze-pump-thaw cycles, the Pyrex tube was flame sealed and placed in an oven at 120 ℃ for 5 days, cooled to room temperature, the reaction product was isolated by vacuum filtration as a precipitate and washed three times with ethanol to afford a solid, the resulting solid was vacuum dried at 80 ℃ for 12 hours, a pyrimidazole covalent organic framework (FP-TZ-AAC) was prepared.
FIG. 1 is a schematic diagram of the synthetic route of FP-TZ-AAC.
FIG. 2 is a Fourier transform Infrared Spectroscopy (FT-IR) plot of FP, TZ, AAC and FP-TZ-AAC. From FIG. 2, it was found that FP-TZ-AAC was 1615cm in FT-IR comparison with FP, TZ, AAC and FP-TZ-AAC-1A new absorption band appears, corresponding to C ═ N stretching vibration of the pyrimidazole ring, indicating successful preparation of the pyrimidazole covalent organic framework FP-TZ-AAC with carboxylic acid functional group as linking unit.
The crystallinity of FP-TZ-AAC is characterized by X-ray powder diffraction Pattern (PXRD). FIG. 3 is the experimentally measured PXRD spectra of FP, TZ, AAC and FP-TZ-AAC. As can be seen from FIG. 3, a strong diffraction peak appears at 3.4 ℃ in FP-TZ-AAC, and the diffraction peaks of the monomers FP, TZ and AAC disappear, which indicates that the pyrimidine azole covalent organic framework FP-TZ-AAC with high crystallinity is successfully synthesized by the method.
Example 2: optimization of the Experimental conditions
The pH value has an effect on the basic morphology of uranium and the extraction capacity of the adsorbent, and therefore the effect of pH on the performance of the adsorbent was investigated. Adjusting the pH value of the aqueous solution to be within the range of 2.0-6.0 by using nitric acid or sodium hydroxide solution, adding 4mg of FP-TZ-AAC into 20mL of uranyl ion aqueous solution with the concentration of 500mg/L, oscillating for 12 hours by using a constant-temperature oscillator, filtering by using a 0.22 mu m microporous filter membrane, collecting filtrate, measuring the content of residual uranyl ions in the filtrate by using inductive coupling plasma mass spectrometry, and calculating the adsorption capacity of FP-TZ-AAC on the uranyl ions.
FIG. 4 is a graph of adsorption capacity of FP-TZ-AAC for uranyl ions at different pH. As can be seen from FIG. 4, the adsorption capacity of FP-TZ-AAC for uranyl ions gradually increases with the increase of pH, and the maximum adsorption capacity of FP-TZ-AAC for uranyl ions is 644mg/g at pH 5.0. The pH value influences the basic existing form of uranium, and when the pH value is more than 5.0, uranyl ions can form precipitates in an aqueous solution, so that the adsorption quantity is reduced. Therefore, the pH of 5.0 was selected as the optimum pH.
Example 3: adsorption application of covalent organic framework of pyrimidazole to uranyl ions
The influence of adsorption performance of the initial concentration FP-TZ-AAC of uranyl ions is researched. Adjusting the pH value of the aqueous solution to 5.0 by using nitric acid or sodium hydroxide solution, adding 4mg of FP-TZ-AAC into 20mL of aqueous solution containing uranyl ions with different concentrations (0-500mg/L), oscillating for 12 hours by using a constant-temperature oscillator, filtering by using a 0.22 mu m microporous filter membrane, collecting filtrate, measuring the content of the residual uranyl ions in the filtrate by using inductive coupling plasma mass spectrometry, calculating the adsorption capacity of the FP-TZ-AAC on the uranyl ions, and drawing an adsorption isotherm of the FP-TZ-AAC on the uranyl ions.
FIG. 5 is an adsorption isotherm diagram of uranyl ions by FP-TZ-AAC. As can be seen from fig. 5, due to the large driving force of the concentration gradient, the adsorption capacity of FP-TZ-AAC for uranyl ions increases rapidly with increasing concentration of uranyl ions until an equilibrium state is reached. Fitting finds that the isothermal adsorption process accords with a Langmuir model, and shows that the adsorption of the FP-TZ-AAC on the uranyl ions is single-layer adsorption, and the maximum adsorption capacity of the FP-TZ-AAC on the uranyl ions is 644 mg/g. The high adsorption capacity can be attributed to the fact that FP-TZ-AAC has regular porous channels and excellent hydrophilicity, and diffusion of uranyl ions is promoted.
The carboxylic acid functionalized pyrimidazole covalent organic framework synthesized by the solvothermal one-pot method has the advantages of high crystallinity, strong stability and good hydrophilicity. FP-TZ-AAC can form a unique carboxylic acid functionalized nano pocket structure, and carboxyl can coordinate with uranyl ions, so that selective combination of the uranyl ions is facilitated. Meanwhile, the inner aperture of the FP-TZ-AAC nano pocket is slightly larger than the diameter of the uranyl hydrate ions, so that size matching adsorption of the uranyl hydrate ions can be realized, and selective adsorption performance of the uranyl hydrate ions is improved. The FP-TZ-AAC has a regular porous channel and excellent hydrophilicity, can promote the diffusion of uranyl ions, has high adsorption capacity and rapid adsorption kinetics, and has good application prospect.
The foregoing is only a preferred embodiment of the present invention and it should be noted that modifications and adaptations can be made by those skilled in the art without departing from the principle of the present invention and are intended to be included within the scope of the present invention.

Claims (9)

1.一种嘧啶唑共价有机框架的制备方法,其特征在于,包括如下步骤:1. a preparation method of a pyrimidazole covalent organic framework, is characterized in that, comprises the steps: 1)将1,3,5-三(3-氟-4-甲酰基苯基)苯、1,3,5-三(4-氰基-4,4-联苯)苯和2-氨基-4-羧基吡啶加入到反应容器中,加入催化剂,再加入有机溶剂,对混合液进行超声处理混合均匀,得到反应混合液;1) Combine 1,3,5-tris(3-fluoro-4-formylphenyl)benzene, 1,3,5-tris(4-cyano-4,4-biphenyl)benzene and 2-amino- 4-Carboxypyridine is added into the reaction vessel, a catalyst is added, an organic solvent is added, and the mixed solution is subjected to ultrasonic treatment and mixed uniformly to obtain a reaction mixed solution; 2)将装有反应混合液的反应容器经过冷冻-泵-解冻循环脱气并火焰密封,置于120℃环境中反应4-6天后,冷却至室温得到反应产物;2) degas the reaction vessel containing the reaction mixture through a freeze-pump-thaw cycle and flame sealing, place it in a 120°C environment to react for 4-6 days, and cool it to room temperature to obtain a reaction product; 3)将反应产物通过真空过滤分离出沉淀物,并用乙醇洗涤,抽干后得到固体,将所得固体在80℃下真空干燥12小时,制成羧酸官能化的嘧啶唑共价有机框架。3) The reaction product was separated into the precipitate by vacuum filtration, washed with ethanol, and dried to obtain a solid. The obtained solid was vacuum-dried at 80° C. for 12 hours to prepare a carboxylic acid-functionalized pyrimidazole covalent organic framework. 2.根据权利要求1所述一种嘧啶唑共价有机框架的制备方法,其特征在于,步骤1)所述1,3,5-三(3-氟-4-甲酰基苯基)苯、1,3,5-三(4-氰基-4,4-联苯)苯和2-氨基-4-羧基吡啶的摩尔比为1:(0.5-2.0):(2.5-4.0)。2. the preparation method of a kind of pyrimidazole covalent organic framework according to claim 1, is characterized in that, step 1) described 1,3,5-tris (3-fluoro-4-formylphenyl) benzene, The molar ratio of 1,3,5-tris(4-cyano-4,4-biphenyl)benzene and 2-amino-4-carboxypyridine was 1:(0.5-2.0):(2.5-4.0). 3.根据权利要求1所述一种嘧啶唑共价有机框架的制备方法,其特征在于,步骤1)所述催化剂为对苯甲磺酸。3. The preparation method of a pyrimidazole covalent organic framework according to claim 1, wherein the catalyst in step 1) is p-toluenesulfonic acid. 4.根据权利要求1所述一种嘧啶唑共价有机框架的制备方法,其特征在于,步骤1)所述有机溶剂为乙醇、均三甲苯、邻二氯苯、二氯甲烷中的一种或几种。4. the preparation method of a kind of pyrimidazole covalent organic framework according to claim 1, is characterized in that, the organic solvent described in step 1) is a kind of in ethanol, mesitylene, ortho-dichlorobenzene, methylene dichloride or several. 5.如权利要求1-4任一项所述方法制备得到的嘧啶唑共价有机框架在吸附铀酰离子中的应用。5. The application of the pyrimidazole covalent organic framework prepared by the method according to any one of claims 1-4 in the adsorption of uranyl ions. 6.根据权利要求5所述嘧啶唑共价有机框架在吸附铀酰离子中的应用,其特征在于,包括将嘧啶唑共价有机框架加入到含不同浓度铀酰离子的水溶液中,使用恒温震荡器震荡12小时,用0.22μm微孔滤膜过滤,收集滤液,采用电感耦合等离子体质谱测量滤液中剩余的铀酰离子含量,计算嘧啶唑共价有机框架对铀酰离子的吸附容量。6. the application of pyrimidazole covalent organic framework in adsorption uranyl ion according to claim 5, is characterized in that, comprises that pyrimidazole covalent organic framework is added in the aqueous solution containing uranyl ion of different concentration, uses constant temperature vibration The device was shaken for 12 hours, filtered with a 0.22 μm microporous membrane, and the filtrate was collected. Inductively coupled plasma mass spectrometry was used to measure the remaining uranyl ion content in the filtrate, and the adsorption capacity of pyrimidazole covalent organic framework for uranyl ion was calculated. 7.根据权利要求6所述嘧啶唑共价有机框架在吸附铀酰离子中的应用,其特征在于,所述不同浓度铀酰离子的水溶液的浓度范围为0-500mg/L。7. The application of the pyrimidazole covalent organic framework in adsorption of uranyl ions according to claim 6, wherein the concentration range of the aqueous solutions of uranyl ions with different concentrations is 0-500 mg/L. 8.根据权利要求6所述嘧啶唑共价有机框架在吸附铀酰离子中的应用,其特征在于,所述含有不同浓度铀酰离子的水溶液与所述嘧啶唑共价有机框架混合前,需用硝酸或氢氧化钠溶液调节溶液pH为2.0-6.0,更优选为5.0。8. The application of the pyrimidazole covalent organic framework in the adsorption of uranyl ions according to claim 6, characterized in that, before the aqueous solution containing uranyl ions of different concentrations is mixed with the pyrimidazole covalent organic framework, it needs to be The pH of the solution is adjusted to 2.0-6.0 with nitric acid or sodium hydroxide solution, more preferably 5.0. 9.根据权利要求6所述嘧啶唑共价有机框架在吸附铀酰离子中的应用,其特征在于,所述吸附容量通过以下公式计算:qt=(Co-Ct)/m×V;其中V是溶液体积、单位L,m是共价有机框架使用量,单位g,Co是铀酰离子初始浓度、单位mg/L,Ct是铀酰离子平衡浓度、单位mg/L。9 . The application of the pyrimidazole covalent organic framework according to claim 6 in the adsorption of uranyl ions, wherein the adsorption capacity is calculated by the following formula: q t =(C o -C t )/m×V ; where V is the volume of the solution, in L, m is the amount of covalent organic framework used, in g, C o is the initial concentration of uranyl ions, in mg/L, and C t is the equilibrium concentration of uranyl ions in mg/L.
CN202111158517.XA 2021-09-30 2021-09-30 Preparation method and adsorption application of pyrimidazole covalent organic framework Active CN113831491B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN202111158517.XA CN113831491B (en) 2021-09-30 2021-09-30 Preparation method and adsorption application of pyrimidazole covalent organic framework

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN202111158517.XA CN113831491B (en) 2021-09-30 2021-09-30 Preparation method and adsorption application of pyrimidazole covalent organic framework

Publications (2)

Publication Number Publication Date
CN113831491A true CN113831491A (en) 2021-12-24
CN113831491B CN113831491B (en) 2023-03-24

Family

ID=78967881

Family Applications (1)

Application Number Title Priority Date Filing Date
CN202111158517.XA Active CN113831491B (en) 2021-09-30 2021-09-30 Preparation method and adsorption application of pyrimidazole covalent organic framework

Country Status (1)

Country Link
CN (1) CN113831491B (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN114574709A (en) * 2022-03-02 2022-06-03 北京工业大学 Method for recovering precious metal based on floating covalent organic polymer material
CN115677959A (en) * 2022-11-11 2023-02-03 南昌大学 Preparation method and adsorption application of an amidoxime functionalized three-dimensional covalent organic framework

Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1078470A (en) * 1992-03-20 1993-11-17 森德克斯(美国)股份有限公司 Any pyrido [2, the 3-d] pyrimidine-2 that replaces, 4-(1H, 3H)-two ketone and pyrido [2,3-d] pyrimidine-2 (1H, 3H)-ketone
CN1341098A (en) * 1999-01-13 2002-03-20 拜尔有限公司 W-carboxyaryl substituted diphenyl ureas as raf kinase inhibitors
US20190169036A1 (en) * 2016-08-10 2019-06-06 Research Triangle Institute Solid-state crystallization of metal organic frameworks within mesoporous materials methods and hybrid materials thereof
CN113045723A (en) * 2021-03-23 2021-06-29 南昌大学 Preparation method of porous covalent organic framework and application of porous covalent organic framework in capture of uranyl ions
CN113087864A (en) * 2021-03-23 2021-07-09 南昌大学 Preparation method of heterocyclic covalent organic polymer and application of heterocyclic covalent organic polymer in uranyl ion adsorption

Patent Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1078470A (en) * 1992-03-20 1993-11-17 森德克斯(美国)股份有限公司 Any pyrido [2, the 3-d] pyrimidine-2 that replaces, 4-(1H, 3H)-two ketone and pyrido [2,3-d] pyrimidine-2 (1H, 3H)-ketone
CN1341098A (en) * 1999-01-13 2002-03-20 拜尔有限公司 W-carboxyaryl substituted diphenyl ureas as raf kinase inhibitors
US20190169036A1 (en) * 2016-08-10 2019-06-06 Research Triangle Institute Solid-state crystallization of metal organic frameworks within mesoporous materials methods and hybrid materials thereof
CN113045723A (en) * 2021-03-23 2021-06-29 南昌大学 Preparation method of porous covalent organic framework and application of porous covalent organic framework in capture of uranyl ions
CN113087864A (en) * 2021-03-23 2021-07-09 南昌大学 Preparation method of heterocyclic covalent organic polymer and application of heterocyclic covalent organic polymer in uranyl ion adsorption

Non-Patent Citations (2)

* Cited by examiner, † Cited by third party
Title
HANSEN, KO等: "Kinase Chemodiversity from the Arctic: The Breitfussins", 《JOURNAL OF MEDICINAL CHEMISTRY》 *
LIU, J等: "Pyrimidazole-Based Covalent Organic Frameworks: Integrating Functionality and Ultrastability via Isocyanide Chemistry", 《JOURNAL OF THE AMERICAN CHEMICAL SOCIETY》 *

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN114574709A (en) * 2022-03-02 2022-06-03 北京工业大学 Method for recovering precious metal based on floating covalent organic polymer material
CN114574709B (en) * 2022-03-02 2023-11-24 北京工业大学 A method for recycling precious metals based on floating covalent organic polymer materials
CN115677959A (en) * 2022-11-11 2023-02-03 南昌大学 Preparation method and adsorption application of an amidoxime functionalized three-dimensional covalent organic framework

Also Published As

Publication number Publication date
CN113831491B (en) 2023-03-24

Similar Documents

Publication Publication Date Title
CN101693757B (en) Hydrophilous porous phenolic resin as well as preparation method and application thereof
CN113831491A (en) Preparation method and adsorption application of pyrimidazole covalent organic framework
CN106040182B (en) A kind of preparation method of phenyl boric acid type metal-organic framework material modified carbon foamed absorbent
CN111804285B (en) Amino-amidoxime group bifunctional hypercrosslinked microporous uranium adsorbent and preparation method thereof
CN113201144B (en) Rigid tetracarboxyl hydrogen bond organic framework material and preparation and application thereof
CN112892501A (en) Double-imidazole polyionic liquid and metal organic framework composite material as well as preparation method and application thereof
CN107552004B (en) A kind of preparation method and application of metal organic framework material
CN110938194B (en) Carbazolyl hydrophobic porous organic polymer and preparation method and application thereof
CN105688844A (en) Mesoporous chelate resin containing phosphorus-oxygen functional groups and method for separating and enriching uranium
CN113372567B (en) Synthetic method of metal organic framework based on naphthalimide-based connecting agent and adsorption application of metal organic framework to uranyl ions
CN113042011A (en) A kind of fluorine-containing conjugated microporous polymer and its preparation method and application
CN113372524A (en) Non-reversible thiourea-linked covalent organic framework capable of rapidly removing mercury, and preparation method and application thereof
CN113087864B (en) Preparation method of heterocyclic covalent organic polymer and application of heterocyclic covalent organic polymer in uranyl ion adsorption
CN107827192B (en) A kind of MOFs material is used for the purposes and method of trace amount mercury ion in adsorbed water body
Bai et al. Synthesis of microporous aromatic framework with scholl-coupling reaction for efficient uranium (VI) capture
CN113929905B (en) Preparation method and application of imine bond-connected fluorescent covalent organic framework
CN110523396A (en) A kind of uranium separation method and uranium adsorption material
CN105418843A (en) Preparation method of porous polymerized ionic liquid used for capture/absorption of CO2
CN112174964B (en) A kind of cationic nonporous macrocyclic organic compound and its preparation method and application
CN115160519B (en) Preparation method of porous covalent organic framework and application of porous covalent organic framework in uranium extraction from seawater
CN114409009A (en) Method for adsorbing hydroquinone based on polymer PIM-1
CN116535593A (en) A kind of ethylenediimine-based covalent organic framework and its preparation method and application
CN116925344B (en) Porous triazinyl sulfur-containing polyamide material, and preparation method and application thereof
CN107511134A (en) A kind of mesoporous Zr polymerization of olefin using catalyst polymer and its preparation and application
CN115646450A (en) ZIF-8-based porous carbon material with hydrophobic pore surface and large and microporous pore volume and preparation method and application 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
GR01 Patent grant
GR01 Patent grant