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CN101885797A - A kind of functional polymer and its preparation method and application - Google Patents

A kind of functional polymer and its preparation method and application Download PDF

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CN101885797A
CN101885797A CN 201010225020 CN201010225020A CN101885797A CN 101885797 A CN101885797 A CN 101885797A CN 201010225020 CN201010225020 CN 201010225020 CN 201010225020 A CN201010225020 A CN 201010225020A CN 101885797 A CN101885797 A CN 101885797A
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mercaptobenzothiazole
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杜滨阳
曹峥
徐君庭
范志强
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Zhejiang University ZJU
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Abstract

本发明公开了一种功能性聚合物,是由N-乙烯基咪唑结构单元和2-巯基苯并噻唑衍生物结构单元组成的重均分子量为6000-15000的无规共聚物;所述的无规共聚物中N-乙烯基咪唑结构单元的摩尔百分含量为20%-45%,2-巯基苯并噻唑衍生物结构单元的摩尔百分含量为55%-80%。本发明还公开了该功能性聚合物的制备方法以及应用。该聚合物结构中包含咪唑环与S、N杂原子基团两种易于重金属离子配位的结合点,因而本发明制备的聚合物及其薄膜可以选择性吸附和检测水中的重金属离子。The invention discloses a functional polymer, which is a random copolymer with a weight average molecular weight of 6000-15000 composed of N-vinylimidazole structural units and 2-mercaptobenzothiazole derivative structural units; The molar percentage of the N-vinylimidazole structural unit in the regular copolymer is 20%-45%, and the molar percentage of the 2-mercaptobenzothiazole derivative structural unit is 55%-80%. The invention also discloses the preparation method and application of the functional polymer. The polymer structure contains two binding points of imidazole ring and S and N heteroatom groups that are easy to coordinate heavy metal ions, so the polymer and its film prepared by the invention can selectively adsorb and detect heavy metal ions in water.

Description

一种功能性聚合物及其制备方法和应用 A kind of functional polymer and its preparation method and application

技术领域technical field

本发明涉及有机聚合物传感材料和环境监测领域,具体涉及一种基于石英晶体微天平技术的功能性聚合物及其制备和应用,该功能性聚合物可应用于水体中重金属离子识别、检测和制备化学传感器领域。The invention relates to the field of organic polymer sensing materials and environmental monitoring, in particular to a functional polymer based on quartz crystal microbalance technology and its preparation and application. The functional polymer can be applied to the identification and detection of heavy metal ions in water and the field of preparing chemical sensors.

背景技术Background technique

最近20多年来,粗放式的经济增长造成我国国民经济高速发展的同时也严重污染了自然环境。各种环境污染物特别是工业生产中产生的重金属离子如镉、钴、铅及铜离子等进入水、土壤环境,不仅污染自然环境,而且危害人类生存和健康。所以水体中痕量重金属离子的识别和检测对于金属元素的回收、重复利用及早期环境污染监测有重要意义。Over the past 20 years, extensive economic growth has resulted in the rapid development of my country's national economy, but also seriously polluted the natural environment. Various environmental pollutants, especially heavy metal ions such as cadmium, cobalt, lead and copper ions produced in industrial production, enter the water and soil environment, which not only pollutes the natural environment, but also endangers human survival and health. Therefore, the identification and detection of trace heavy metal ions in water is of great significance for the recovery and reuse of metal elements and early monitoring of environmental pollution.

目前重金属离子的检测方法主要有电感耦合等离子体质谱法、原子吸收光谱及电化学阳极溶出伏安法等。尽管这些技术灵敏度高、特异性强,但存在样品前处理复杂、操作耗时、仪器昂贵和运行费用高、离线检测等缺陷,难以适应当前检测工作的需要。公开号为CN 101021515A的中国专利申请中公开了一种在水体中原位取样、分离、富集和测量重金属离子的方法,利用渗透作用使重金属离子从膜内侧扩散出来与高分子化合物发生反应,这些高分子化合物主要是羟甲基纤维素、壳聚糖及聚丙烯酸钠等,其官能团可以与重金属离子结合,但实际上并没有选择性吸附的性能,检测步骤复杂,耗费时间;又由于其是利用原子吸收光谱法计算重金属离子浓度,无法实时检测。中国专利CN200610009925.8中公开了一种荧光分子探针在过渡金属及重金属离子检测中的应用,设计合成了一种在各种溶液特别是含水溶液中对Co2+选择性荧光增强识别的荧光探针,该荧光分子结构较为复杂,分离和提纯需要进行柱色谱步骤,作为传感材料实现工业化应用具有一定难度,且仍然无法实现在线实时和简便快速检测。因此,需要寻求一种更为简单快速的定性定量技术来鉴定水体中可能存在的重金属离子。At present, the detection methods of heavy metal ions mainly include inductively coupled plasma mass spectrometry, atomic absorption spectroscopy, and electrochemical anodic stripping voltammetry. Although these techniques have high sensitivity and specificity, they have defects such as complicated sample pretreatment, time-consuming operation, expensive instruments and high operating costs, and offline detection, making it difficult to meet the needs of current detection work. The Chinese patent application with the publication number CN 101021515A discloses a method for in-situ sampling, separation, enrichment and measurement of heavy metal ions in water bodies, using osmosis to diffuse heavy metal ions from the inside of the membrane to react with polymer compounds, these Macromolecular compounds are mainly hydroxymethylcellulose, chitosan and sodium polyacrylate, etc., whose functional groups can combine with heavy metal ions, but in fact there is no selective adsorption performance, and the detection steps are complicated and time-consuming; and because they are The concentration of heavy metal ions is calculated by atomic absorption spectrometry, which cannot be detected in real time. Chinese patent CN200610009925.8 discloses the application of a fluorescent molecular probe in the detection of transition metals and heavy metal ions, and designed and synthesized a fluorescent material that selectively enhances the recognition of Co 2+ in various solutions, especially aqueous solutions. As a probe, the fluorescent molecular structure is relatively complex, and column chromatography steps are required for separation and purification. It is difficult to realize industrial application as a sensing material, and it is still impossible to achieve online real-time and simple and fast detection. Therefore, it is necessary to seek a simpler and faster qualitative and quantitative technology to identify the heavy metal ions that may exist in water.

发明内容Contents of the invention

本发明提供了一种功能性聚合物及其薄膜,可以用于检测痕量重金属离子。The invention provides a functional polymer and its film, which can be used to detect trace heavy metal ions.

一种功能性聚合物,是由下列式M1所示的N-乙烯基咪唑结构单元和式M2所示的2-巯基苯并噻唑衍生物结构单元组成的重均分子量为6000-15000的无规共聚物;A functional polymer, which is composed of the N-vinylimidazole structural unit shown in the following formula M1 and the 2-mercaptobenzothiazole derivative structural unit shown in the formula M2, is a random polymer with a weight average molecular weight of 6000-15000 copolymer;

所述的无规共聚物中N-乙烯基咪唑结构单元的摩尔百分含量为20%-45%,2-巯基苯并噻唑衍生物结构单元的摩尔百分含量为55%-80%。The molar percentage of N-vinylimidazole structural units in the random copolymer is 20%-45%, and the molar percentage of 2-mercaptobenzothiazole derivative structural units is 55%-80%.

所述的功能性聚合物的制备方法,包括步骤:The preparation method of described functional polymer, comprises the steps:

以式M5所示的N-乙烯基咪唑单体和式M6所示的含双键的2-巯基苯并噻唑衍生物单体为原料,通过引发剂引发两单体的乙烯基双键发生共聚反应,制得无规共聚物;Using the N-vinylimidazole monomer represented by formula M5 and the double bond-containing 2-mercaptobenzothiazole derivative monomer represented by formula M6 as raw materials, the vinyl double bonds of the two monomers are initiated by an initiator to copolymerize Reaction, make random copolymer;

Figure BSA00000186548100022
Figure BSA00000186548100022

作为优选:As preferred:

所述的引发剂可选用本领域内常用自由基类引发剂,为了保证合成反应更好的效果,选用偶氮二异丁腈或过氧化苯甲酰。The initiator can be a free radical initiator commonly used in this field. In order to ensure a better effect of the synthesis reaction, azobisisobutyronitrile or benzoyl peroxide is selected.

所述的引发剂的用量可通过实验调整,一般为N-乙烯基咪唑单体和2-巯基苯并噻唑衍生物单体总重量的0.01%-5%,优选0.2%-3%。The amount of the initiator can be adjusted through experiments, and is generally 0.01%-5%, preferably 0.2%-3%, of the total weight of the N-vinylimidazole monomer and the 2-mercaptobenzothiazole derivative monomer.

所述的共聚反应条件为:在无氧条件下于无水溶剂中进行自由基共聚反应。The copolymerization reaction condition is: carry out free radical copolymerization reaction in anhydrous solvent under anaerobic condition.

所述的无氧条件可通过本领域常规的方法来实现,例如:对反应体系进行真空-氮气置换以除去其中的氧气,或者直接将反应在惰性气体氛围中进行。所述的惰性气体包括本领域广义范围的惰性气体,如氮气、氦气等中的一种。The oxygen-free condition can be realized by conventional methods in the art, for example: vacuum-nitrogen replacement of the reaction system to remove oxygen therein, or directly carry out the reaction in an inert gas atmosphere. The inert gas includes a wide range of inert gases in the art, such as one of nitrogen, helium and the like.

所述的无水溶剂可选用本领域内常用有机溶剂,如1,4-二氧六环或四氢呋喃。无水溶剂是将所用的溶剂在使用前采用通用的除水方法如经氢化钙和金属钠干燥,除去其中的微量水而得到的。The anhydrous solvent can be an organic solvent commonly used in this field, such as 1,4-dioxane or tetrahydrofuran. The anhydrous solvent is obtained by removing traces of water from the solvent by using a common water removal method such as drying over calcium hydride and metal sodium before use.

所述的共聚反应温度为60℃-90℃,共聚反应时间为12小时-24小时。The copolymerization reaction temperature is 60°C-90°C, and the copolymerization reaction time is 12 hours-24 hours.

所述的共聚反应完成后,可将反应产物进行纯化处理,具体纯化处理过程包括:After the completion of the copolymerization reaction, the reaction product can be purified, and the specific purification process includes:

将反应液冷却,经离心分离后去除反应液中悬浮的不溶性颗粒,上层浅黄色清液在大量丙酮中沉淀,再经离心分离得浅黄色沉淀,将沉淀干燥至恒重,制得功能性聚合物:聚(2-巯基苯并噻唑衍生物-co-N-乙烯基咪唑)无规共聚物(P(MBTVBC-co-VIM))。Cool the reaction liquid, remove the insoluble particles suspended in the reaction liquid after centrifugation, the upper layer of light yellow clear liquid is precipitated in a large amount of acetone, and then centrifuged to obtain a light yellow precipitate, and the precipitate is dried to constant weight to obtain a functional polymer Material: poly(2-mercaptobenzothiazole derivative-co-N-vinylimidazole) random copolymer (P(MBTVBC-co-VIM)).

所述的式M6所示的含双键的2-巯基苯并噻唑衍生物单体的制备方法,包括步骤:The preparation method of the 2-mercaptobenzothiazole derivative monomer containing a double bond shown in the formula M6 comprises the steps of:

将式M3所示的对氯甲基苯乙烯或对溴甲基苯乙烯与式M4所示的2-巯基苯并噻唑在氢化钠和四氢呋喃存在条件下进行反应,制得式M6所示的含双键的2-巯基苯并噻唑衍生物单体;Reaction of p-chloromethylstyrene or p-bromomethylstyrene shown in formula M3 with 2-mercaptobenzothiazole shown in formula M4 in the presence of sodium hydride and tetrahydrofuran to prepare the compound containing 2-mercaptobenzothiazole derivative monomer with double bond;

Figure BSA00000186548100031
Figure BSA00000186548100031

式M3中,X选自Cl或Br。In formula M3, X is selected from Cl or Br.

所述的对氯甲基苯乙烯或对溴甲基苯乙烯单体,具有双键可以进行聚合反应,对位上的氯甲基或溴甲基可以实现功能化,可采用市售产品。The p-chloromethyl styrene or p-bromomethyl styrene monomer has a double bond and can be polymerized, and the chloromethyl or bromomethyl at the para position can be functionalized, and commercially available products can be used.

所述的式M6所示的含双键的2-巯基苯并噻唑衍生物单体的制备方法,包括步骤:The preparation method of the 2-mercaptobenzothiazole derivative monomer containing a double bond shown in the formula M6 comprises the steps of:

(1)将式M4所示的2-巯基苯并噻唑溶解于四氢呋喃中,加入氢化钠后,反应生成2-巯基苯并噻唑钠盐的四氢呋喃溶液;(1) Dissolving 2-mercaptobenzothiazole represented by formula M4 in tetrahydrofuran, adding sodium hydride, reacting to generate a tetrahydrofuran solution of 2-mercaptobenzothiazole sodium salt;

(2)将式M3所示的对氯甲基苯乙烯或对溴甲基苯乙烯溶解于四氢呋喃中形成透明溶液,与上述2-巯基苯并噻唑钠盐的四氢呋喃溶液混合,在50℃-60℃反应24小时-48小时,经后处理制得式M6所示的含双键的2-巯基苯并噻唑衍生物单体。(2) Dissolve p-chloromethylstyrene or p-bromomethylstyrene shown in formula M3 in tetrahydrofuran to form a transparent solution, mix it with the tetrahydrofuran solution of the above-mentioned 2-mercaptobenzothiazole sodium salt, and heat ℃ for 24 hours to 48 hours, and after post-treatment to prepare the double bond-containing 2-mercaptobenzothiazole derivative monomer represented by the formula M6.

所述的后处理过程包括:将反应液在氢氧化钠水溶液(如质量浓度为3‰的氢氧化钠水溶液)中沉淀析出,经抽滤干燥至恒重。The post-treatment process includes: precipitating the reaction solution in an aqueous sodium hydroxide solution (such as an aqueous sodium hydroxide solution with a mass concentration of 3‰), and drying to constant weight through suction filtration.

所述的聚合物带有既亲水又可以结合金属离子的咪唑环,又带有具有疏水性的2-巯基苯并噻唑衍生物结构单元,其中的S和N杂原子基团使其可以选择性结合金属离子,因而可用于识别和检测水中痕量重金属离子,还可用于制备化学传感器。The polymer has an imidazole ring that is both hydrophilic and can bind metal ions, and has a hydrophobic 2-mercaptobenzothiazole derivative structural unit, wherein the S and N heteroatom groups make it possible to select Therefore, it can be used to identify and detect trace heavy metal ions in water, and can also be used to prepare chemical sensors.

所述的重金属离子包括Cd2+、Pb2+、Zn2+、Cu2+等中的一种或多种,尤其是Cu2+The heavy metal ions include one or more of Cd 2+ , Pb 2+ , Zn 2+ , Cu 2+ , etc., especially Cu 2+ .

为了提高检测的灵敏度,功能性聚合物应用于水体中痕量重金属离子的识别、检测和化学传感器领域,均可结合石英晶体微天平技术来实现。例如:可将所述的功能性聚合物溶于有机溶剂(如氯仿)制成功能性聚合物溶液,将功能性聚合物溶液滴加到空白石英晶片的金电极表面,经匀胶机将功能性聚合物溶液在空白石英晶片的金电极表面旋涂成膜后烘干,即制得涂覆功能性聚合物薄膜的石英晶片。当含金属离子的溶液流经所述石英晶片表面的功能性聚合物薄膜,利用石英晶体微天平仪检测共振频率响应,来反映含金属离子的溶液中金属离子的浓度。In order to improve the sensitivity of detection, functional polymers are used in the field of identification, detection and chemical sensors of trace heavy metal ions in water, which can be realized by combining quartz crystal microbalance technology. For example: the functional polymer can be dissolved in an organic solvent (such as chloroform) to make a functional polymer solution, and the functional polymer solution is added dropwise to the gold electrode surface of a blank quartz wafer, and the functional A functional polymer solution is spin-coated on the gold electrode surface of a blank quartz wafer to form a film and then dried to obtain a quartz wafer coated with a functional polymer film. When the solution containing metal ions flows through the functional polymer film on the surface of the quartz wafer, the resonant frequency response is detected by a quartz crystal microbalance to reflect the concentration of metal ions in the solution containing metal ions.

所述的功能性聚合物薄膜的厚度可以通过控制功能性聚合物溶液的浓度来调节,功能性聚合物溶液的质量百分浓度为0.065%-0.5%比较理想,配制温度为10℃-20℃比较理想。The thickness of the functional polymer film can be adjusted by controlling the concentration of the functional polymer solution. The mass percent concentration of the functional polymer solution is ideally 0.065%-0.5%, and the preparation temperature is 10°C-20°C ideal.

所述的功能性聚合物薄膜在用于检测水中重金属离子浓度时,其厚度范围为200nm-550nm比较理想;在该厚度范围内,功能性聚合物薄膜对水中重金属离子Cu2+浓度的最低检测限是10ppm(质量百分浓度0.001%),对应的频率响应值为9Hz。When the functional polymer film is used to detect the concentration of heavy metal ions in water, its thickness range is ideally 200nm-550nm; within this thickness range, the minimum detection of the concentration of heavy metal ions Cu in water by the functional polymer film The limit is 10ppm (mass percentage concentration 0.001%), and the corresponding frequency response value is 9Hz.

所述的匀胶机的操作条件优选为低速4000转/分钟,转9s,高速3000转/分钟,转30s。The operating conditions of the homogenizer are preferably at a low speed of 4000 rpm for 9 seconds, and at a high speed of 3000 rpm for 30 seconds.

本发明的无规共聚物,可以通过红外和核磁等手段表征其分子结构。The molecular structure of the random copolymer of the present invention can be characterized by infrared, nuclear magnetic and other means.

本发明的原理是:含有式M1所示的N-乙烯基咪唑结构单元和式M2所示的2-巯基苯并噻唑衍生物结构单元的无规共聚物因侧链上有可结合重金属离子的咪唑环和S、N杂原子基团(统称为功能性基团),以一定浓度溶液的形式旋涂到石英晶片的金电极表面,由于无规共聚物分子链上含有S原子,与金发生强烈相互作用使薄膜能够稳定固定在金电极表面上;当旋涂聚合物薄膜的石英晶片与重金属离子溶液接触时,薄膜表面上的功能性基团就可以与重金属离子进行结合,使石英晶片表面的质量负载发生变化,进而导致晶片的频率响应发生变化,从而实时方便的对重金属离子进行识别和检测。The principle of the present invention is: the random copolymer containing the N-vinylimidazole structural unit shown in formula M1 and the 2-mercaptobenzothiazole derivative structural unit shown in formula M2 has the ability to bind heavy metal ions on the side chain. The imidazole ring and S, N heteroatom groups (collectively referred to as functional groups) are spin-coated on the surface of the gold electrode of the quartz wafer in the form of a certain concentration solution. The strong interaction enables the film to be stably fixed on the surface of the gold electrode; when the quartz wafer of the spin-coated polymer film is in contact with the heavy metal ion solution, the functional groups on the surface of the film can combine with the heavy metal ions, making the surface of the quartz wafer The mass load of the chip changes, which in turn causes the frequency response of the chip to change, so that the heavy metal ions can be identified and detected conveniently in real time.

本发明有如下优点:The present invention has following advantage:

1.本发明功能性聚合物结构中包含咪唑环与S、N杂原子基团两种易于重金属离子配位的结合点,因而本发明制备的聚合物及其薄膜可以选择性吸附和检测水中的重金属离子,尤其是Cu2+1. The structure of the functional polymer of the present invention contains two binding points that are easy to coordinate heavy metal ions, the imidazole ring and the S and N heteroatom groups, so the polymer and its film prepared by the present invention can selectively adsorb and detect Heavy metal ions, especially Cu 2+ .

2.本发明功能性聚合物薄膜呈现多孔结构,且孔径范围在100nm-400nm,平均孔深10nm-20nm,有效增大比表面积,能够吸附更多重金属离子。2. The functional polymer film of the present invention presents a porous structure, and the pore diameter ranges from 100nm to 400nm, and the average pore depth is 10nm to 20nm, which effectively increases the specific surface area and can absorb more heavy metal ions.

3.本发明所采用的制备方法中,首先合成了含双键的2-巯基苯并噻唑衍生物,再将其与N-乙烯基咪唑共聚反应得到共聚物,合成路线简洁明了。3. In the preparation method adopted in the present invention, the 2-mercaptobenzothiazole derivative containing a double bond is first synthesized, and then copolymerized with N-vinylimidazole to obtain a copolymer. The synthesis route is concise and clear.

4.本发明所采用的石英晶体微天平技术,由于具有高灵敏度质量效应而被用于重金属离子定量检测,涂有功能性聚合物薄膜的石英晶片对水中重金属离子的检测灵敏度高,选择性较好,其对Cu2+检测限可以达到10ppm(质量百分浓度0.001%)的浓度。4. The quartz crystal microbalance technology adopted in the present invention is used for quantitative detection of heavy metal ions due to the high-sensitivity mass effect, and the quartz wafer coated with functional polymer film has high detection sensitivity to heavy metal ions in water, and the selectivity is relatively high. Well, its detection limit for Cu 2+ can reach a concentration of 10 ppm (mass percentage concentration 0.001%).

5.本发明旋涂成膜的制备方法,工艺简单可控,适用于工业化生产。5. The preparation method of the spin-coating film of the present invention has a simple and controllable process and is suitable for industrial production.

可见,本发明功能性N-乙烯基咪唑和2-巯基苯并噻唑衍生物的共聚物薄膜的制备和石英晶体微天平技术的应用证明是一个不错的选择。本发明所制备的共聚物结构相对简单,合成路线短,共聚改性的方法可以赋予传感材料优异的性能,保证共聚物能够选择性吸附水中重金属离子;同时石英晶体微天平能对石英晶片表面上的微小质量变化产生响应,具有极高的灵敏性,实现了实时检测。It can be seen that the preparation of the copolymer film of functional N-vinylimidazole and 2-mercaptobenzothiazole derivatives and the application of the quartz crystal microbalance technology of the present invention prove to be a good choice. The copolymer structure prepared by the present invention is relatively simple, and the synthetic route is short, and the method for copolymerization modification can endow the sensing material with excellent performance, and ensure that the copolymer can selectively adsorb heavy metal ions in water; It responds to small mass changes on the surface, has extremely high sensitivity, and realizes real-time detection.

附图说明Description of drawings

图1为实施例1中制备的聚2-巯基苯并噻唑衍生物均聚物(PMBTVBC)、聚(2-巯基苯并噻唑衍生物-co-N-乙烯基咪唑)无规共聚物(P(MBTVBC-co-VIM))及聚乙烯基咪唑均聚物(PVIM)的红外谱图;Fig. 1 is poly 2-mercaptobenzothiazole derivative homopolymer (PMBTVBC), poly (2-mercaptobenzothiazole derivative-co-N-vinylimidazole) random copolymer (P (MBTVBC-co-VIM)) and the infrared spectrum of polyvinylimidazole homopolymer (PVIM);

图2为实施例2在吸附40ppm Cu2+溶液中的Cu2+前后共聚物薄膜的原子力显微镜表面形貌图;Fig. 2 is the atomic force microscope surface topography figure of the copolymer film before and after Cu in the adsorption 40ppm Cu solution of embodiment 2 ;

图3为共聚物薄膜对水中不同浓度铜离子的吸附曲线;Fig. 3 is the adsorption curve of copolymer film to copper ion of different concentrations in water;

图4为共聚物薄膜对水中不同重金属离子的选择性吸附。Figure 4 shows the selective adsorption of different heavy metal ions in water by the copolymer film.

具体实施方式Detailed ways

实施例1:Example 1:

取6.0777g 2-巯基苯并噻唑加入到聚合瓶中,用15ml四氢呋喃完全溶解,再向瓶中加入1.5302g氢化钠,反应过程中形成大量气泡,待气泡完全消失后在室温下再充分反应半小时形成2-巯基苯并噻唑钠盐。用针筒将反应瓶中上层钠盐清液取出,随后加到10.2ml含有5.20ml对氯甲基苯乙烯的四氢呋喃溶液中继续于50℃反应24h。将反应液滴加到大量质量浓度为3‰氢氧化钠水溶液里沉淀,经抽滤形成滤饼,再用质量百分浓度为3‰氢氧化钠水溶液清洗后分离,真空干燥至恒重,制得2-巯基苯并噻唑衍生物。Take 6.0777g of 2-mercaptobenzothiazole and add it to the polymerization bottle, dissolve it completely with 15ml of tetrahydrofuran, then add 1.5302g of sodium hydride into the bottle, a large number of bubbles will be formed during the reaction, and fully react for half a day at room temperature after the bubbles completely disappear. hours to form 2-mercaptobenzothiazole sodium salt. Take out the supernatant sodium salt clear solution in the reaction flask with a syringe, then add it to 10.2ml of tetrahydrofuran solution containing 5.20ml of p-chloromethylstyrene and continue to react at 50°C for 24h. The reaction solution was added dropwise to a large amount of 3‰ sodium hydroxide aqueous solution to precipitate, and a filter cake was formed by suction filtration, then washed with a 3‰ sodium hydroxide aqueous solution and separated, vacuum-dried to constant weight, and prepared In 2-mercaptobenzothiazole derivatives.

将1ml N-乙烯基咪唑单体和0.5073g上述制备的2-巯基苯并噻唑衍生物溶于15ml二氧六环,在氮气氛围条件下搅拌使其充分溶解,再加入19.4mg偶氮二异丁腈,充分搅拌,在氮气氛围条件下于70℃油浴中恒温反应24小时后,取出自然冷却至室温。反应完成后为微浑浊略黄溶液,在3500转/分钟的速率中离心10min后去除反应液中悬浮的不溶性颗粒;上层浅黄色清液在大量丙酮中沉淀,同样在3500转/分钟的速率中离心10min后得到浅黄色沉淀,将沉淀在真空烘箱60℃干燥至恒重,制得1.10g功能性聚合物:聚(2-巯基苯并噻唑衍生物-co-N-乙烯基咪唑)无规共聚物。该无规共聚物的重均分子量为6200;该无规共聚物中N-乙烯基咪唑结构单元的摩尔百分含量为44.8%,2-巯基苯并噻唑衍生物结构单元的摩尔百分含量为55.2%。Dissolve 1ml of N-vinylimidazole monomer and 0.5073g of the above-prepared 2-mercaptobenzothiazole derivative in 15ml of dioxane, stir to fully dissolve under nitrogen atmosphere, and then add 19.4mg of azobisiso Butyronitrile, fully stirred, reacted at a constant temperature in a 70°C oil bath for 24 hours under a nitrogen atmosphere, then took it out and cooled it to room temperature naturally. After the reaction was completed, it was a slightly turbid slightly yellow solution, which was centrifuged at a rate of 3500 rpm for 10 minutes to remove insoluble particles suspended in the reaction solution; A light yellow precipitate was obtained after centrifugation for 10 min, and the precipitate was dried in a vacuum oven at 60°C to constant weight to obtain 1.10 g of a functional polymer: poly(2-mercaptobenzothiazole derivative-co-N-vinylimidazole) random copolymer. The weight-average molecular weight of this random copolymer is 6200; The molar percentage of N-vinylimidazole structural unit in this random copolymer is 44.8%, and the molar percentage of 2-mercaptobenzothiazole derivative structural unit is 55.2%.

图1中显示了聚2-巯基苯并噻唑衍生物均聚物(PMBTVBC)、聚(2-巯基苯并噻唑衍生物-co-N-乙烯基咪唑)共聚物(P(MBTVBC-co-VIM))、聚乙烯基咪唑均聚物(PVIM)的红外谱图。Figure 1 shows poly 2-mercaptobenzothiazole derivative homopolymer (PMBTVBC), poly(2-mercaptobenzothiazole derivative-co-N-vinylimidazole) copolymer (P(MBTVBC-co-VIM )), the infrared spectrum of polyvinylimidazole homopolymer (PVIM).

称取51.9mg P(MBTVBC-co-VIM)共聚物完全溶于10ml氯仿中搅拌一天,配成质量分数为5.19‰的溶液。将溶液滴加到匀胶机上空白石英晶片的金电极表面,设置低速400转/分钟,时间9s,高速3000转/分钟,时间30s。在晶片金电极表面旋涂成膜后放真空烘箱抽半小时,使氯仿完全挥发干净,制得表面负载共聚物薄膜的石英晶片,该共聚物薄膜的厚度为522.8nm。Weigh 51.9mg of P(MBTVBC-co-VIM) copolymer and completely dissolve it in 10ml of chloroform and stir for one day to prepare a solution with a mass fraction of 5.19‰. Add the solution dropwise to the gold electrode surface of the blank quartz wafer on the homogenizer, set the low speed to 400 rpm for 9 s, and the high speed to 3000 rpm for 30 s. After spin-coating the gold electrode surface of the wafer to form a film, put it in a vacuum oven for half an hour to completely volatilize the chloroform to obtain a quartz wafer with a copolymer film on the surface. The thickness of the copolymer film is 522.8nm.

使用石英晶体微天平仪来测试空白晶片和表面负载共聚物薄膜的石英晶片的共振频率响应,得到共聚物薄膜负载下当石英晶片泛频共振阶数n=3时所对应的频率变化ΔF3,其为实时频率响应值与基线频率响应值的净差值;向装有石英晶片的样品池以100μL/min流速通入二蒸水,得到稳定的频率响应基线后再通入Cu2+浓度为10ppm(质量百分浓度0.001%)Cu2+水溶液,铜离子与共聚物薄膜表面的功能性基团配位结合,采用石英晶体微天平实时检测吸附过程中的石英晶片的共振频率变化,结果表明该共聚物薄膜能有效吸附水中的Cu2+。结果如图3所示。Use a quartz crystal microbalance to test the resonant frequency response of a blank wafer and a quartz wafer with a copolymer film loaded on the surface, and obtain the corresponding frequency change ΔF 3 when the overtone resonance order n=3 of the quartz wafer under the load of the copolymer film, It is the net difference between the real-time frequency response value and the baseline frequency response value; the distilled water is passed into the sample cell equipped with a quartz wafer at a flow rate of 100 μL/min, and then the Cu 2+ concentration is passed after a stable frequency response baseline is obtained. 10ppm (mass percentage concentration 0.001%) Cu 2+ aqueous solution, copper ions are coordinated with the functional groups on the surface of the copolymer film, and the resonance frequency of the quartz wafer in the adsorption process is detected in real time by a quartz crystal microbalance. The results show that The copolymer film can effectively absorb Cu 2+ in water. The result is shown in Figure 3.

实施例2:Example 2:

将0.5ml N-乙烯基咪唑单体和1g实施例1制备的2-巯基苯并噻唑衍生物溶于15ml二氧六环,在氮气氛围条件下搅拌使其充分溶解,再加入10mg偶氮二异丁腈,充分搅拌,在氮气氛围条件下于80℃油浴中恒温反应24小时后,取出自然冷却至室温。反应完成后为微浑浊略黄溶液,经3500转/分钟离心10min后去除反应液中悬浮的不溶性颗粒;上层浅黄色清液在大量丙酮里沉淀,同样在3500转/分钟的速率中离心10min得到浅黄色沉淀,将沉淀在真空烘箱60℃干燥至恒重,制得0.85g功能性聚合物:聚(2-巯基苯并噻唑衍生物-co-N-乙烯基咪唑)无规共聚物。该无规共聚物的重均分子量为11900;该无规共聚物中N-乙烯基咪唑结构单元的摩尔百分含量为24.9%,2-巯基苯并噻唑衍生物结构单元的摩尔百分含量为75.1%。Dissolve 0.5ml of N-vinylimidazole monomer and 1g of the 2-mercaptobenzothiazole derivative prepared in Example 1 in 15ml of dioxane, stir under a nitrogen atmosphere to fully dissolve, then add 10mg of azobis Isobutyronitrile, fully stirred, reacted at a constant temperature in an oil bath of 80°C under nitrogen atmosphere for 24 hours, then took it out and cooled it to room temperature naturally. After the reaction is completed, it is a slightly turbid slightly yellow solution, which is centrifuged at 3500 rpm for 10 minutes to remove the suspended insoluble particles in the reaction solution; the upper layer of light yellow supernatant is precipitated in a large amount of acetone, and is also centrifuged at 3500 rpm for 10 minutes to obtain A light yellow precipitate was dried in a vacuum oven at 60° C. to a constant weight to obtain 0.85 g of a functional polymer: poly(2-mercaptobenzothiazole derivative-co-N-vinylimidazole) random copolymer. The weight-average molecular weight of this random copolymer is 11900; In this random copolymer, the molar percentage of N-vinylimidazole structural unit is 24.9%, and the molar percentage of 2-mercaptobenzothiazole derivative structural unit is 75.1%.

称取25.0mg上述共聚物完全溶于10ml氯仿中搅拌1天,配成质量分数为2.5‰的溶液。将溶液滴加到匀胶机上空白石英晶片的金电极表面,设置低速400转/分钟,时间9s,高速3000转/分钟,时间30s。在晶片金电极表面旋涂成膜后放真空烘箱抽半小时,使氯仿完全挥发干净,制得表面负载共聚物薄膜的石英晶片,该共聚物薄膜的厚度为303.1nm。Weigh 25.0 mg of the above copolymer and completely dissolve it in 10 ml of chloroform and stir for 1 day to prepare a solution with a mass fraction of 2.5‰. Add the solution dropwise to the gold electrode surface of the blank quartz wafer on the homogenizer, set the low speed to 400 rpm for 9 s, and the high speed to 3000 rpm for 30 s. After spin-coating the gold electrode surface of the wafer to form a film, put it in a vacuum oven for half an hour to completely volatilize the chloroform to obtain a quartz wafer with a copolymer film on the surface. The thickness of the copolymer film is 303.1 nm.

使用石英晶体微天平仪来测试空白晶片和表面负载聚合物薄膜的石英晶片的频率响应,得到薄膜负载对应的频率变化ΔF3;向装有石英晶片的样品池以100μL/min流速通入二蒸水,得到稳定的频率响应基线后再通入Cu2+浓度为40ppm(质量百分浓度0.004%)Cu2+水溶液,铜离子与聚合物薄膜表面的功能性基团配位结合,石英晶体微天平实时检测吸附过程中的频率变化和耗散变化。图2为在吸附40ppm Cu2+前后共聚物薄膜的原子力显微镜的形貌图,可以看到吸附前薄膜表面为多孔结构,吸附后变化不大。Use a quartz crystal microbalance to test the frequency response of a blank wafer and a quartz wafer loaded with a polymer film on the surface, and obtain the frequency change ΔF 3 corresponding to the film load; water, after obtaining a stable frequency response baseline, the Cu 2+ concentration is 40ppm (mass percentage concentration 0.004%) Cu 2+ aqueous solution, the copper ions are coordinated with the functional groups on the surface of the polymer film, and the quartz crystal micro The balance detects frequency changes and dissipation changes during the adsorption process in real time. Figure 2 is the atomic force microscope topography of the copolymer film before and after adsorption of 40ppm Cu 2+ . It can be seen that the surface of the film is porous before adsorption, and there is little change after adsorption.

实施例3:Example 3:

将0.5ml N-乙烯基咪唑单体和0.5073g实施例1制备的2-巯基苯并噻唑衍生物溶于10ml二氧六环,在氮气氛围条件下搅拌使其充分溶解,再加入8mg偶氮二异丁腈,充分搅拌,在氮气氛围条件下于80℃油浴中恒温反应24小时后,取出自然冷却至室温。反应完成后为微浑浊略黄溶液,经3500转/分钟离心10min后去除反应液中悬浮不溶性颗粒;上层浅黄色清液在大量丙酮里沉淀,同样3500转/分钟离心10min,得到浅黄色沉淀,将沉淀在真空烘箱60℃干燥至恒重,制得0.75g功能性聚合物:聚(2-巯基苯并噻唑衍生物-co-N-乙烯基咪唑)无规共聚物。该无规共聚物的重均分子量为15000;该无规共聚物中N-乙烯基咪唑结构单元的摩尔百分含量为35.1%,2-巯基苯并噻唑衍生物结构单元的摩尔百分含量为64.9%。Dissolve 0.5ml of N-vinylimidazole monomer and 0.5073g of the 2-mercaptobenzothiazole derivative prepared in Example 1 in 10ml of dioxane, stir under nitrogen atmosphere to fully dissolve, then add 8mg of azo Diisobutyronitrile, fully stirred, reacted at a constant temperature in an oil bath of 80°C for 24 hours under a nitrogen atmosphere, then took it out and cooled it naturally to room temperature. After the reaction was completed, it was a slightly turbid slightly yellow solution, which was centrifuged at 3500 rpm for 10 minutes to remove suspended insoluble particles in the reaction solution; the light yellow supernatant liquid in the upper layer was precipitated in a large amount of acetone, and centrifuged at 3500 rpm for 10 minutes to obtain a light yellow precipitate. The precipitate was dried in a vacuum oven at 60° C. to a constant weight to obtain 0.75 g of a functional polymer: poly(2-mercaptobenzothiazole derivative-co-N-vinylimidazole) random copolymer. The weight-average molecular weight of this random copolymer is 15000; In this random copolymer, the molar percentage of N-vinylimidazole structural unit is 35.1%, and the molar percentage of 2-mercaptobenzothiazole derivative structural unit is 64.9%.

称取35.0mg上述共聚物完全溶于10ml氯仿中搅拌1天,配成质量分数为3.5‰的溶液。将溶液滴加到匀胶机上空白石英晶片的金电极表面,设置低速400转/分钟,时间9s,高速3000转/分钟,时间30s。在晶片金电极表面旋涂成膜后放真空烘箱抽半小时,使氯仿完全挥发干净,制得表面负载共聚物薄膜的石英晶片,该共聚物薄膜的厚度为344.3nm。Weigh 35.0 mg of the above copolymer and completely dissolve it in 10 ml of chloroform and stir for 1 day to prepare a solution with a mass fraction of 3.5‰. Add the solution dropwise to the gold electrode surface of the blank quartz wafer on the homogenizer, set the low speed to 400 rpm for 9 s, and the high speed to 3000 rpm for 30 s. After spin-coating the gold electrode surface of the wafer to form a film, put it in a vacuum oven for half an hour to completely volatilize the chloroform to obtain a quartz wafer with a copolymer film on the surface. The thickness of the copolymer film is 344.3nm.

使用石英晶体微天平来测试空白晶片和表面负载聚合物薄膜的石英晶片的频率响应,得到薄膜负载对应的归一化频率变化ΔF3;向装有石英晶片的样品池以100μL/min流速通入二蒸水,得到稳定的频率响应基线后再通入Cu2+浓度为136.5ppm(质量百分浓度0.01365%)Cu2+水溶液,铜离子与聚合物薄膜表面的功能性基团配位结合,石英晶体微天平实时检测吸附过程中的频率变化和耗散变化。结果如图3。Use a quartz crystal microbalance to test the frequency response of a blank wafer and a quartz wafer loaded with a polymer film on the surface, and obtain the normalized frequency change ΔF 3 corresponding to the film load; Distilled water, after obtaining a stable frequency response baseline, pass into Cu 2+ concentration and be 136.5ppm (mass percentage concentration 0.01365%) Cu 2+ aqueous solution, copper ions are coordinated with the functional groups on the surface of the polymer film, A quartz crystal microbalance detects frequency changes and dissipation changes during the adsorption process in real time. The result is shown in Figure 3.

图3为共聚物薄膜对水溶液中不同铜离子浓度的吸附曲线,即频率响应随时间的变化,可以看到较高铜离子浓度条件下,共聚物薄膜表面可以结合更多的铜离子,具有较高的频率响应值,用二蒸水清洗后曲线不会回到原点,说明共聚物薄膜表面上的功能性基团与铜离子形成稳定的结合。Figure 3 is the adsorption curve of the copolymer film to different concentrations of copper ions in the aqueous solution, that is, the change of the frequency response with time. It can be seen that under the condition of higher copper ion concentration, the surface of the copolymer film can bind more copper ions, and has a relatively high copper ion concentration. High frequency response value, the curve will not return to the original point after washing with distilled water, indicating that the functional groups on the surface of the copolymer film form a stable combination with copper ions.

实施例4:Example 4:

共聚物合成与共聚物薄膜制备同以上实施例1,使用石英晶体微天平来测试空白晶片和表面负载聚合物薄膜的石英晶片的频率响应,得到共聚物薄膜负载对应的归一化频率变化ΔF3;向装有石英晶片的样品池以100μL/min流速通入二蒸水,得到稳定的频率响应基线后再通入Pb2+浓度为40ppm(质量百分浓度0.004%)Pb2+水溶液、Zn2+浓度为40ppm(质量百分浓度0.004%)Zn2+水溶液、Cd2+浓度为40ppm(质量百分浓度0.004%)Cd2+水溶液、Ni2+浓度为40ppm(质量百分浓度0.004%)Ni2+水溶液、Co2+浓度为40ppm(质量百分浓度0.004%)Co2+水溶液或Cu2+浓度为40ppm(质量百分浓度0.004%)Cu2+水溶液,石英晶体微天平实时检测吸附过程中的频率变化和耗散变化。结果如图4。The copolymer synthesis and the preparation of the copolymer film are the same as the above Example 1, using a quartz crystal microbalance to test the frequency response of the blank wafer and the quartz wafer with the polymer film on the surface, and obtain the normalized frequency change ΔF3 corresponding to the copolymer film load ; Pass into distilled water with 100 μ L/min flow rate to the sample cell that quartz wafer is housed, pass into Pb again after obtaining stable frequency response baseline and concentration is 40ppm (mass percentage concentration 0.004%) Pb 2+ aqueous solution, Zn 2+ concentration is 40ppm (mass percentage concentration 0.004%) Zn 2+ aqueous solution, Cd 2+ concentration is 40ppm (mass percentage concentration 0.004%) Cd 2+ aqueous solution, Ni 2+ concentration is 40ppm (mass percentage concentration 0.004%) ) Ni 2+ aqueous solution, Co 2+ concentration of 40ppm (mass percent concentration 0.004%) Co 2+ aqueous solution or Cu 2+ concentration of 40ppm (mass percent concentration 0.004%) Cu 2+ aqueous solution, real-time detection by quartz crystal microbalance Frequency change and dissipation change during adsorption. The result is shown in Figure 4.

图4为同样膜厚范围内的共聚物薄膜在浓度为40ppm(质量百分浓度0.004%)的不同重金属离子水溶液中,对不同种类重金属离子的选择性吸附结果。可以看到同样的离子浓度条件下,共聚物薄膜表面可以结合更多的铜离子,具有较高的频率响应值,其次为Co2+和Cd2+,接着是pb2+和Ni2+,吸附响应值最小的Zn2+。共聚物分子链上的咪唑环和S、N杂原子基团有效捕捉到了重金属离子,分子链上的S、N等原子能以一对孤对电子与金属离子空轨道形成配位键,构成与小分子螯合物相似的稳定结构,具有很好的配位络合能力。相对其他重金属离子,显示出对Cu2+较强的配位络合性能,吸附效果明显。Figure 4 shows the results of selective adsorption of different types of heavy metal ions by copolymer films in the same film thickness range in different heavy metal ion aqueous solutions with a concentration of 40ppm (0.004% by mass). It can be seen that under the same ion concentration conditions, more copper ions can be bound to the surface of the copolymer film, which has a higher frequency response value, followed by Co 2+ and Cd 2+ , followed by pb 2+ and Ni 2+ , Zn 2+ with the smallest adsorption response value. The imidazole ring and S, N heteroatom groups on the molecular chain of the copolymer can effectively capture heavy metal ions, and the S, N and other atoms on the molecular chain can form a coordination bond with the empty orbital of the metal ion with a pair of lone pairs of electrons. Molecular chelates have a similar stable structure and have good coordination and complexation capabilities. Compared with other heavy metal ions, it shows strong coordination and complexation performance for Cu 2+ , and the adsorption effect is obvious.

以上所述仅为本发明的若干个具体实施方式,应当指出,对于本领域的普通技术人员来说,还可以做出许多变型和改进,所有未超出权利要求所述的变型或改进均应视为本发明的保护范围。The above descriptions are only some specific implementations of the present invention, and it should be pointed out that many variations and improvements can be made by those skilled in the art, and all variations or improvements that do not exceed the claims described should be considered as Be the protection scope of the present invention.

Claims (10)

1. functional polymer, the weight-average molecular weight of being made up of the 2-mercaptobenzothiazole derivant structure unit shown in N-vinyl imidazole structural unit shown in the following formula M1 and the formula M2 is the random copolymers of 6000-15000;
Figure FSA00000186548000011
The molar content of N-vinyl imidazole structural unit is 20%-45% in the described random copolymers, and the unitary molar content of 2-mercaptobenzothiazole derivant structure is 55%-80%.
2. the preparation method of functional polymer as claimed in claim 1 comprises step:
With the double bond containing 2-mercaptobenzothiazole derivatives monomer shown in N-vinyl imidazole monomer shown in the formula M5 and the formula M6 is raw material, causes two monomeric vinyl double bond generation copolyreaction by initiator, makes random copolymers;
Figure FSA00000186548000012
3. the preparation method of functional polymer as claimed in claim 2 is characterized in that, described initiator is selected from Diisopropyl azodicarboxylate or benzoyl peroxide.
4. the preparation method of functional polymer as claimed in claim 2 is characterized in that, the consumption of described initiator is the 0.01%-5% of N-vinyl imidazole monomer and 2-mercaptobenzothiazole derivatives monomer gross weight.
5. the preparation method of functional polymer as claimed in claim 2 is characterized in that, described copolyreaction condition is: carry out free radicals copolymerization reaction under oxygen free condition in anhydrous solvent.
6. the preparation method of functional polymer as claimed in claim 5 is characterized in that, described anhydrous solvent is selected from 1,4-dioxane or tetrahydrofuran (THF).
7. the preparation method of functional polymer as claimed in claim 2 is characterized in that, described copolyreaction temperature is 60 ℃-90 ℃, and the copolyreaction time is 12 hours-24 hours.
8. the preparation method of functional polymer as claimed in claim 1 is characterized in that, the preparation method of the double bond containing 2-mercaptobenzothiazole derivatives monomer shown in the described formula M6 comprises step:
React under sodium hydride and tetrahydrofuran (THF) existence condition with the p-chloromethyl styrene shown in the formula M3 or to the 2-mercaptobenzothiazole shown in brooethyl vinylbenzene and the formula M4, make the double bond containing 2-mercaptobenzothiazole derivatives monomer shown in the formula M6;
Figure FSA00000186548000021
Among the formula M3, X is selected from Cl or Br.
9. the preparation method of functional polymer as claimed in claim 7 is characterized in that, the preparation method of the double bond containing 2-mercaptobenzothiazole derivatives monomer shown in the described formula M6 comprises step:
(1) 2-mercaptobenzothiazole shown in the formula M4 is dissolved in the tetrahydrofuran (THF), behind the adding sodium hydride, reaction generates the tetrahydrofuran solution of 2-mercaptobenzothiazole sodium salt;
(2) be dissolved in the p-chloromethyl styrene shown in the formula M3 or to brooethyl vinylbenzene and form clear solution in the tetrahydrofuran (THF), mix with the tetrahydrofuran solution of above-mentioned 2-mercaptobenzothiazole sodium salt, 50 ℃-60 ℃ reactions 24 hours-48 hours, make the double bond containing 2-mercaptobenzothiazole derivatives monomer shown in the formula M6 through aftertreatment.
10. the application of functional polymer as claimed in claim 1 in identification underwater trace heavy metal ion, detection underwater trace heavy metal ion or preparation chemical sensor.
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