CN114643046A - Preparation method of amidoxime microgel adsorbent and application of amidoxime microgel adsorbent in rapid uranium extraction - Google Patents
Preparation method of amidoxime microgel adsorbent and application of amidoxime microgel adsorbent in rapid uranium extraction Download PDFInfo
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Abstract
本发明属于吸附分离功能材料技术领域,涉及一种偕胺肟微凝胶吸附剂的制备方法及其快速提铀应用。步骤为:首先利用N’N‑二乙基丙烯酰胺DEA为骨架单体,制备富含羧基的微凝胶,然后利用酰胺化反应,修饰上二氨基马来腈,利用盐酸羟胺进一步将腈基反应成为偕胺肟基团。本发明由于采用了DEA为骨架单体合成了可以在有机溶剂中溶胀的微凝胶,使得水凝胶材料可以在有机溶剂中修饰偕胺肟基团,不需要合成特殊的偕胺肟单体,大大简化的材料制备方法;由于采用了微凝胶材料用于吸附铀,其溶胀速率远大于一般水凝胶,因此大大提高了吸附速率。
The invention belongs to the technical field of adsorption and separation functional materials, and relates to a preparation method of an amidoxime microgel adsorbent and its rapid uranium extraction application. The steps are: firstly using N'N-diethylacrylamide DEA as a backbone monomer to prepare a carboxyl-rich microgel, then using amidation reaction to modify diaminomaleonitrile, and using hydroxylamine hydrochloride to further convert the nitrile group. The reaction becomes an amidoxime group. In the present invention, DEA is used as the skeleton monomer to synthesize a microgel that can swell in an organic solvent, so that the hydrogel material can be modified with amidoxime groups in the organic solvent, and no special amidoxime monomer needs to be synthesized , a greatly simplified material preparation method; due to the use of microgel materials for uranium adsorption, the swelling rate is much higher than that of general hydrogels, so the adsorption rate is greatly improved.
Description
技术领域technical field
本发明属于吸附分离功能材料制备技术领域,具体涉及一种偕胺肟微凝胶吸附剂的制备方法及其快速提铀应用。The invention belongs to the technical field of preparation of functional materials for adsorption and separation, and in particular relates to a preparation method of an amidoxime microgel adsorbent and its application for rapid uranium extraction.
背景技术Background technique
核能是一种成熟的能源,可以持续不断地大规模提供电力,具有极高的能量密度和超低的温室气体排放量。因为核能的大规模使用,其偶然因素导致的核泄漏事故也时有发生。放射性元素不仅会污染海洋环境,还会在海洋生物体中蓄积,人类食用之后,对人体也会产生严重危害。铀是主要的核元素,于是我们需要一种能快速应急处理泄露的铀的吸附剂。Nuclear energy is a mature energy source that can continuously provide electricity on a large scale with extremely high energy density and ultra-low greenhouse gas emissions. Because of the large-scale use of nuclear energy, nuclear leakage accidents caused by accidental factors also occur from time to time. Radioactive elements will not only pollute the marine environment, but also accumulate in marine organisms. After human consumption, it will also cause serious harm to the human body. Uranium is the main nuclear element, so we need a sorbent that can quickly deal with leaked uranium.
高分子交联网络水凝胶由于其组成的通用性、制备的方便性和可调的物理性能,在多个应用领域引起了广泛关注。水凝胶在保持其化学结构的同时还能在水中溶胀并保持大量的水分。近些年来,将水凝胶材料运用至吸附金属离子上的报道逐渐增多,但是水凝胶材料吸附时,依然具有吸附速度速率慢的缺点急需解决。微凝胶是尺寸在0.5-10μm的水凝胶,它具有水凝胶的优良特性,同时由于水凝胶的溶胀速度与其尺寸成反比,所以微凝胶的溶胀吸水速率会远大于一般宏观水凝胶材料。将微凝胶材料运用于吸附铀能大大提高吸附速率。Polymer cross-linked network hydrogels have attracted extensive attention in many application fields due to their versatility in composition, ease of preparation, and tunable physical properties. The hydrogel swells in water and retains a large amount of water while maintaining its chemical structure. In recent years, reports on the application of hydrogel materials to the adsorption of metal ions have gradually increased. However, when hydrogel materials are adsorbed, they still have the disadvantage of slow adsorption rate, which needs to be solved urgently. Microgels are hydrogels with a size of 0.5-10 μm, which have the excellent characteristics of hydrogels. At the same time, since the swelling rate of hydrogels is inversely proportional to their size, the swelling and water absorption rate of microgels will be much higher than that of general macroscopic water. gel material. The application of microgel materials to adsorb uranium can greatly improve the adsorption rate.
偕胺肟基团由于其特有的空间构型,与U(VI)的尺寸匹配,通过配位作用可以实现对U(VI)的选择性吸附效果。基于此可以通过在材料中引入偕胺肟基团来赋予其选择性吸附U(VI)的能力。在修饰偕胺肟基团在材料上时,需要使用有机溶剂,但是常见水凝胶材料在有机溶剂中不能溶胀,属于皱缩状态,反应效率大大降低。所以亟待开发一种能在有机溶剂溶胀的水凝胶材料。The amidoxime group matches the size of U(VI) due to its unique steric configuration, and the selective adsorption of U(VI) can be achieved through coordination. Based on this, the ability to selectively adsorb U(VI) can be given to the material by introducing amidoxime groups. When modifying the amidoxime group on the material, it is necessary to use an organic solvent, but common hydrogel materials cannot swell in organic solvents and are in a shrunken state, and the reaction efficiency is greatly reduced. Therefore, it is urgent to develop a hydrogel material that can swell in organic solvents.
为了避免以上不足,有必要研究一种新型水凝胶材料既能在有机溶剂中溶胀便于修饰,又具有较快的吸附速率,应用于选择性提铀。In order to avoid the above deficiencies, it is necessary to develop a new type of hydrogel material that can swell in organic solvents for easy modification and has a fast adsorption rate, which can be used for selective uranium extraction.
发明内容SUMMARY OF THE INVENTION
针对现有技术的不足,本发明的目的在于克服水凝胶不易在有机溶剂中修饰和吸附速率较慢的问题,提供了一种偕胺肟基微凝胶的制备方法。以偕胺肟基团为选择性配体,以N’N-二乙基丙烯酰胺为微凝胶骨架单体,制备了偕胺肟功能化的微凝胶基吸附剂。In view of the deficiencies of the prior art, the purpose of the present invention is to overcome the problems that the hydrogel is not easy to be modified in an organic solvent and the adsorption rate is slow, and provides a preparation method of an amidoxime-based microgel. Amidoxime-functionalized microgel-based adsorbent was prepared with amidoxime group as selective ligand and N'N-diethylacrylamide as microgel backbone monomer.
为达到上述技术目的,本发明采用的技术方案如下:In order to achieve the above-mentioned technical purpose, the technical scheme adopted in the present invention is as follows:
(1)羧基功能化微凝胶(Microgel-COOH)的制备;(1) Preparation of carboxyl functionalized microgel (Microgel-COOH);
将一定量的N’N-二乙基丙烯酰胺(DEA)、N’N-二甲基双丙烯酰胺(Bis)、丙烯酸(AAc)和十二烷基硫酸钠(SDS)添加到一定体积的去离子水中,将混合溶液通气一段时间t1后,水浴搅拌加热至温度T1,再加入一定量的过硫酸钾(KPS),反应一段时间t2。所得溶液使用分子量为300000的透析袋进行透析,最后冷冻干燥得到产物羧基微凝胶。Add a certain amount of N'N-diethylacrylamide (DEA), N'N-dimethylbisacrylamide (Bis), acrylic acid (AAc) and sodium dodecyl sulfate (SDS) to a certain volume of In deionized water, the mixed solution is ventilated for a period of time t 1 , heated to a temperature T 1 with stirring in a water bath, and then a certain amount of potassium persulfate (KPS) is added to react for a period of time t 2 . The obtained solution was dialyzed using a dialysis bag with a molecular weight of 300,000, and finally freeze-dried to obtain a product carboxyl microgel.
(2)腈基功能化微凝胶(Microgel-CN)的制备;(2) Preparation of nitrile functionalized microgel (Microgel-CN);
将一定量的步骤(1)中合成的Microgel-COOH、二氨基马来腈(DAMN)、1-乙基-(3-二甲基氨基丙基)碳酰二亚胺(EDC)和N-羟基琥珀酰亚胺(NHS)加入一定体积的乙醇中,温度控制为T2,搅拌反应是时间t3。所得溶液使用分子量为300000的透析袋进行透析,最后冷冻干燥得到Microgel-CN。A certain amount of Microgel-COOH, diaminomaleonitrile (DAMN), 1-ethyl-(3-dimethylaminopropyl)carbodiimide (EDC) and N- Hydroxysuccinimide (NHS) was added to a certain volume of ethanol, the temperature was controlled at T 2 , and the stirring reaction was at time t 3 . The obtained solution was dialyzed using a dialysis bag with a molecular weight of 300,000, and finally freeze-dried to obtain Microgel-CN.
(3)偕胺肟功能化微凝胶吸附剂(Microgel-AO)的制备:(3) Preparation of amidoxime functionalized microgel adsorbent (Microgel-AO):
将一定量的步骤(2)中合成的Microgel-CN、氢氧化钠和盐酸羟胺,加入到乙醇水的混合溶液中,加热至温度T3,搅拌反应时间t4。将反应完的溶液使用300000的透析袋进行透析,最后冷冻干燥得到偕胺肟基微凝胶。A certain amount of Microgel-CN, sodium hydroxide and hydroxylamine hydrochloride synthesized in step (2) was added to the mixed solution of ethanol water, heated to temperature T 3 , and stirred for reaction time t 4 . The reacted solution was dialyzed using a 300,000 dialysis bag, and finally freeze-dried to obtain amidoxime-based microgels.
优选的,步骤(1)中,所述DEA,Bis,AAc,SDS,去离子水和KPS的用量比例为:0.5-2.5g:0.01-0.08g:0.05-0.2g:0.005-0.02g:50-120mL;0.02-0.1g,反应温度T1为65-90℃,反应时间t1为10-60min,反应时间t2为2-8h。Preferably, in step (1), the dosage ratio of DEA, Bis, AAc, SDS, deionized water and KPS is: 0.5-2.5g: 0.01-0.08g: 0.05-0.2g: 0.005-0.02g: 50 -120mL; 0.02-0.1g, the reaction temperature T1 is 65-90°C, the reaction time t1 is 10-60min , and the reaction time t2 is 2-8h.
优选的,步骤(2)中,所述一定量步骤(1)中合成的Microgel-COOH,DAMN,EDC,NHS和乙醇的用量比例为0.5-2g:0.1-0.3g:0.2-0.53g:0.1-0.33g:80-150mL,反应温度T2为4-40℃,反应时间t3为6-24h。Preferably, in step (2), the proportion of the amount of Microgel-COOH, DAMN, EDC, NHS and ethanol synthesized in step (1) is 0.5-2g: 0.1-0.3g: 0.2-0.53g: 0.1 -0.33g: 80-150mL , the reaction temperature T2 is 4-40°C, and the reaction time t3 is 6-24h.
优选的,步骤(3)中,所述步骤(2)中合成的Microgel-CN、盐酸羟胺、NaOH和乙醇水的混合溶液的用量比为0.5-2g:0.5-10g:0.5-5g:80-150mL,乙醇水混合溶液中,乙醇和去离子水的体积比为7:3~9:1。反应温度T3为65-80℃,反应时间t4为2-12h。Preferably, in step (3), the dosage ratio of the mixed solution of Microgel-CN, hydroxylamine hydrochloride, NaOH and ethanol water synthesized in the step (2) is 0.5-2g: 0.5-10g: 0.5-5g: 80- In 150 mL of ethanol-water mixed solution, the volume ratio of ethanol and deionized water is 7:3 to 9:1. The reaction temperature T3 is 65-80°C, and the reaction time t4 is 2-12h .
将本发明制备的偕胺肟微凝胶吸附剂用于溶液中六价铀的选择性吸附与分离的用途。具体用法为:在15-50℃下,将该材料放置于铀浓度为0.1-200mg/L,pH值为4-9的溶液中,经过1-2880min后,完成吸附。The use of the amidoxime microgel adsorbent prepared by the invention for selective adsorption and separation of hexavalent uranium in solution. The specific usage is as follows: at 15-50 ℃, the material is placed in a solution with a uranium concentration of 0.1-200 mg/L and a pH of 4-9, and the adsorption is completed after 1-2880 min.
本发明的有益效果:Beneficial effects of the present invention:
(1)本发明选择偕胺肟集团为U(VI)的选择性功能单元,以尺寸较小的微凝胶为基底,制备了偕胺肟功能化微凝胶基吸附剂,实现了对U(VI)的快速特异性吸附。(1) The present invention selects the amidoxime group as the selective functional unit of U (VI), and uses the microgel with a smaller size as the substrate to prepare the amidoxime functionalized microgel-based adsorbent, and realizes the utilization of U (VI). (VI) Rapid specific adsorption.
(2)本发明通过自由基沉淀聚合,然后进一步修饰得到了富含偕胺肟基团的微凝胶,由于凝胶溶胀速度与其粒径成反比,所以粒径较小的微凝胶吸附剂,大大了提高吸附速率;由于微凝胶骨架单体为DEA,其合成的水凝胶在部分有机溶剂中也可溶胀,为材料进一步修饰偕胺肟基团提供了便利,避免合成较为复杂的单体,简化了材料合成步骤。(2) the present invention obtains the microgel rich in amidoxime groups by further modification through radical precipitation polymerization, because the gel swelling speed is inversely proportional to its particle size, so the microgel adsorbent with smaller particle size , greatly improving the adsorption rate; since the monomer of the microgel backbone is DEA, the synthesized hydrogel can also swell in some organic solvents, which provides convenience for the further modification of amidoxime groups and avoids complex synthesis. Monomer, simplifying material synthesis steps.
附图说明Description of drawings
图1为实施例1中的Microgel-AO的SEM图像(a、b)和DLS数据图(c)。FIG. 1 is SEM images (a, b) and DLS data graph (c) of Microgel-AO in Example 1. FIG.
图2为实施例1中Microgel-CN与Microgel-AO的FI-IR数据图。FIG. 2 is a graph of FI-IR data of Microgel-CN and Microgel-AO in Example 1. FIG.
图3为pH值对实施例1中制备得到的偕胺肟基微凝胶对铀酰根离子吸附容量的影响。Figure 3 shows the effect of pH on the uranyl ion adsorption capacity of the amidoxime-based microgel prepared in Example 1.
图4为实施例1中制备得到的Microgel-AO对铀酰根离子的吸附动力学及其模型拟合曲线。FIG. 4 is the adsorption kinetics of the Microgel-AO prepared in Example 1 for uranyl ions and its model fitting curve.
图5为温度对实施例1中制备得到的Microgel-AO对铀酰根离子的吸附平衡的影响及其模型拟合曲线。5 shows the effect of temperature on the adsorption equilibrium of Microgel-AO prepared in Example 1 on the uranyl ion and its model fitting curve.
图6为实施例1中制备得到的Microgel-AO的吸附选择性。Figure 6 shows the adsorption selectivity of the Microgel-AO prepared in Example 1.
具体实施方式Detailed ways
本发明具体实施方式中识别性能评价按照下述方法进行:利用静态吸附实验完成。将5.0mg Microgel-AO在pH 4.0-9.0范围内对U(VI)的吸附容量进行测试,吸附后U(VI)的含量用电感耦合等离子体发射光谱仪测定,并根据结果确定最佳吸附pH;其次研究了吸附时间对Microgel-AO吸附容量的影响,分别用Pseudo first-order模型和Pseudosecond-order模型等对数据进行了拟合计算与分析;为研究Microgel-AO的最大吸附容量,我们在U(VI)浓度为10-60ppm范围内进行了吸附平衡试验,采用Langmuir模型和Freundlich模型进行了拟合,根据结果计算吸附容量;并选择其他几种与铀酰根离子有相同结构的物质作为竞争吸附物,参与研究Microgel-AO的选择性吸附性能。In the specific embodiment of the present invention, the recognition performance evaluation is carried out according to the following method: it is completed by using a static adsorption experiment. The adsorption capacity of 5.0 mg Microgel-AO for U(VI) in the range of pH 4.0-9.0 was tested, the content of U(VI) after adsorption was measured by inductively coupled plasma emission spectrometer, and the optimal adsorption pH was determined according to the results ; Secondly, the effect of adsorption time on the adsorption capacity of Microgel-AO was studied, and the Pseudo first-order model and Pseudo second-order model were used to fit and analyze the data respectively. In order to study the maximum adsorption capacity of Microgel-AO, we used The adsorption equilibrium test was carried out in the range of U(VI) concentration of 10-60 ppm. The Langmuir model and the Freundlich model were used for fitting, and the adsorption capacity was calculated according to the results. Several other substances with the same structure as the uranyl ion were selected as Competing adsorbate, participating in the study of the selective adsorption performance of Microgel-AO.
下面结合具体实施实例对本发明做进一步说明。The present invention will be further described below in conjunction with specific implementation examples.
实施例1:Example 1:
(1)Microgel-COOH的制备;(1) Preparation of Microgel-COOH;
在烧瓶中,将1.66g DEA、0.0432g Bis、0.101g AAc和0.0115g SDS添加到100mL去离子水中,通N2 30min后,使用磁力搅拌加热至70℃,加入0.081g KPS,反应5h。反应结束后,将反应完的溶液使用300000的透析袋进行透析,纯水中进行透析7天,每天换三次水用于去除未完全反应掉的单体,最后冷冻干燥得到羧基微凝胶。In a flask, 1.66g DEA, 0.0432g Bis, 0.101g AAc and 0.0115g SDS were added to 100mL deionized water, and after passing N 2 for 30min, heated to 70°C using magnetic stirring, 0.081g KPS was added, and the reaction was continued for 5h. After the reaction, the reacted solution was dialyzed using a 300,000 dialysis bag, and dialyzed with pure water for 7 days. The water was changed three times a day to remove incompletely reacted monomers, and finally lyophilized to obtain carboxyl microgels.
(2)Microgel-CN的制备;(2) Preparation of Microgel-CN;
将1.5g步骤(1)中得到的Microgel-COOH、0.151g DAMN、0.268g EDC和0.163g NHS加入100mL乙醇中。磁力搅拌加热至40℃,反应12h。反应结束后,将反应完的溶液使用300000的透析袋进行透析,于纯水中进行透析7天,每天换三次水用于去除未完全反应掉的单体,最后冷冻干燥得到Microgel-CN。1.5 g of Microgel-COOH obtained in step (1), 0.151 g of DAMN, 0.268 g of EDC and 0.163 g of NHS were added to 100 mL of ethanol. Magnetic stirring was heated to 40 ° C, and the reaction was carried out for 12 h. After the reaction, the reacted solution was dialyzed using a 300,000 dialysis bag, and dialyzed in pure water for 7 days. The water was changed three times a day to remove incompletely reacted monomers, and finally Microgel-CN was obtained by freeze-drying.
(3)Microgel-AO的制备:(3) Preparation of Microgel-AO:
在烧瓶中,将1.5g步骤(2)中得到的Microgel-CN、5g盐酸羟胺和2.2g NaOH加入至含有乙醇水比例为9:1的100mL溶液中,使用浓度为1M的氢氧化钠溶液调节pH至8,搅拌加热至80度,反应6h。应结束后,将反应完的溶液使用300000的透析袋进行透析,于纯水中进行透析7天,每天换三次水用于去除未完全反应掉的单体,最后冷冻干燥得到偕胺肟基微凝胶。In a flask, add 1.5 g of Microgel-CN obtained in step (2), 5 g of hydroxylamine hydrochloride and 2.2 g of NaOH to 100 mL of a solution containing 9:1 ethanol and water, and adjust it with 1 M sodium hydroxide solution. pH to 8, heated to 80 degrees with stirring, and reacted for 6h. After the completion of the reaction, the reacted solution was dialyzed using a dialysis bag of 300,000, and dialyzed in pure water for 7 days. gel.
如图1所示,在步骤(1)中所合成的微凝胶基本成球状,可单分散;从图1c DLS数据图可看出,该材料在水溶液环境下粒径均一,粒径在735-765nm之间,单分散系数较小,为0.065;As shown in Figure 1, the microgel synthesized in step (1) is basically spherical and can be monodispersed; from the DLS data map in Figure 1c, it can be seen that the particle size of the material is uniform in the aqueous environment, with a particle size of 735 Between -765nm, the monodispersity coefficient is small, 0.065;
如图2所示,在FI-IR数据图中,Microgel-AO与Microgel-CN相比,在2230-2240nm左右的消失了腈基的特征峰,证明腈基已经基本反应成为偕胺肟基团。As shown in Figure 2, in the FI-IR data, compared with Microgel-CN, the characteristic peak of the nitrile group disappears around 2230-2240 nm in Microgel-AO, which proves that the nitrile group has basically reacted into an amidoxime group .
综上所述,该材料已经合成成功。In summary, the material has been synthesized successfully.
实施例2:Example 2:
(1)Microgel-COOH的制备;(1) Preparation of Microgel-COOH;
在烧瓶中,将0.5g DEA、0.01g Bis、0.05g AAc和0.005g SDS添加到100mL去离子水中,通N2 30min后,使用磁力搅拌加热至70℃,加入0.02g KPS,反应2h。反应结束后,将反应完的溶液使用300000的透析袋进行透析,纯水中进行透析7天,每天换三次水用于去除未完全反应掉的单体,最后冷冻干燥得到羧基微凝胶。In a flask, add 0.5g DEA, 0.01g Bis, 0.05g AAc and 0.005g SDS to 100mL deionized water, pass N 2 for 30min, heat to 70°C with magnetic stirring, add 0.02g KPS, and react for 2h. After the reaction, the reacted solution was dialyzed using a 300,000 dialysis bag, and dialyzed with pure water for 7 days. The water was changed three times a day to remove incompletely reacted monomers, and finally lyophilized to obtain carboxyl microgels.
(2)Microgel-CN的制备;(2) Preparation of Microgel-CN;
将0.5g步骤(1)中得到的Microgel-COOH、0.1g DAMN、0.2g EDC和0.1g NHS加入100mL乙醇中。磁力搅拌加热至4℃,反应6h。反应结束后,将反应完的溶液使用300000的透析袋进行透析,于纯水中进行透析7天,每天换三次水用于去除未完全反应掉的单体,最后冷冻干燥得到Microgel-CN。0.5 g of Microgel-COOH obtained in step (1), 0.1 g of DAMN, 0.2 g of EDC and 0.1 g of NHS were added to 100 mL of ethanol. Magnetic stirring was heated to 4 ℃, and the reaction was carried out for 6 h. After the reaction, the reacted solution was dialyzed using a 300,000 dialysis bag, and dialyzed in pure water for 7 days. The water was changed three times a day to remove incompletely reacted monomers, and finally Microgel-CN was obtained by freeze-drying.
(3)Microgel-AO的制备:(3) Preparation of Microgel-AO:
在烧瓶中,将0.5g步骤(2)中得到的Microgel-CN、0.5g盐酸羟胺和0.5g NaOH加入至含有乙醇水比例为8:2的100mL溶液中,使用浓度为1M的氢氧化钠溶液调节pH至8,搅拌加热至65度,反应2h。应结束后,将反应完的溶液使用300000的透析袋进行透析,于纯水中进行透析7天,每天换三次水用于去除未完全反应掉的单体,最后冷冻干燥得到偕胺肟基微凝胶。In a flask, add 0.5 g of Microgel-CN obtained in step (2), 0.5 g of hydroxylamine hydrochloride and 0.5 g of NaOH to 100 mL of solution containing ethanol and water in a ratio of 8:2, using a 1M sodium hydroxide solution Adjust pH to 8, stir and heat to 65 degrees, and react for 2h. After the completion of the reaction, the reacted solution was dialyzed using a 300,000 dialysis bag, and dialyzed in pure water for 7 days. gel.
实施例3:Example 3:
(1)Microgel-COOH的制备;(1) Preparation of Microgel-COOH;
在烧瓶中,将2.5g DEA、0.08g Bis、0.2g AAc和0.02g SDS添加到100mL去离子水中,通N2 30min后,使用磁力搅拌加热至70℃,加入0.1g KPS,反应12h。反应结束后,将反应完的溶液使用300000的透析袋进行透析,纯水中进行透析7天,每天换三次水用于去除未完全反应掉的单体,最后冷冻干燥得到Microgel-COOH。In a flask, 2.5g DEA, 0.08g Bis, 0.2g AAc and 0.02g SDS were added to 100mL deionized water, and after 30min of N 2 was used, it was heated to 70°C using magnetic stirring, 0.1g KPS was added, and the reaction was continued for 12h. After the reaction, the reacted solution was dialyzed using a 300,000 dialysis bag, and dialysis was performed in pure water for 7 days. The water was changed three times a day to remove incompletely reacted monomers, and finally Microgel-COOH was obtained by freeze-drying.
(2)Microgel-CN的制备;(2) Preparation of Microgel-CN;
将2g步骤(1)中得到的Microgel-COOH、0.3g DAMN、0.53g EDC和0.33g NHS加入100mL乙醇中。磁力搅拌加热至40℃,反应24h。反应结束后,将反应完的溶液使用300000的透析袋进行透析,于纯水中进行透析7天,每天换三次水用于去除未完全反应掉的单体,最后冷冻干燥得到Microgel-CN。2 g of Microgel-COOH obtained in step (1), 0.3 g of DAMN, 0.53 g of EDC and 0.33 g of NHS were added to 100 mL of ethanol. Magnetic stirring was heated to 40 ° C, and the reaction was carried out for 24 h. After the reaction, the reacted solution was dialyzed using a 300,000 dialysis bag, and dialyzed in pure water for 7 days. The water was changed three times a day to remove incompletely reacted monomers, and finally Microgel-CN was obtained by freeze-drying.
(3)Microgel-AO的制备:(3) Preparation of Microgel-AO:
在烧瓶中,将2g步骤(2)中得到的腈基微凝胶、10g盐酸羟胺和5g NaOH加入至含有乙醇水比例为8:2的100mL溶液中,使用浓度为1M的氢氧化钠溶液调节pH至8,搅拌加热至90度,反应2h。应结束后,将反应完的溶液使用300000的透析袋进行透析,于纯水中进行透析7天,每天换三次水用于去除未完全反应掉的单体,最后冷冻干燥得到Microgel-AO。In the flask, 2g of the nitrile-based microgel obtained in step (2), 10g of hydroxylamine hydrochloride and 5g of NaOH were added to a 100mL solution containing ethanol-water in a ratio of 8:2, and adjusted with a 1M sodium hydroxide solution. pH to 8, heated to 90 degrees with stirring, and reacted for 2h. After the reaction, the reacted solution was dialyzed using a 300,000 dialysis bag, and dialyzed in pure water for 7 days. The water was changed three times a day to remove incompletely reacted monomers. Finally, Microgel-AO was obtained by freeze-drying.
性能测试:Performance Testing:
环境pH值对金属离子吸附行为有巨大影响;因此研究了Microgel-AO在pH 4.0-9.0范围内对U(VI)的吸附容量的影响。如图3所示,在pH值不高于6.0时Microgel-AO的吸附容量均随着pH的增大呈现逐渐上升趋势,在pH值高于6.0后其吸附容量随着pH值的升高而降低。Ambient pH has a huge impact on the metal ion adsorption behavior; therefore, the effect of Microgel-AO on the adsorption capacity of U(VI) in the pH range of 4.0-9.0 was investigated. As shown in Figure 3, when the pH value is not higher than 6.0, the adsorption capacity of Microgel-AO shows a gradual upward trend with the increase of pH value. When the pH value is higher than 6.0, the adsorption capacity increases with the increase of pH value. reduce.
Microgel-AO对不同浓度U(VI)的吸附动力学如图4所示。由图可见,Microgel-AO的吸附容量在最初的5min内快速增加,在10min内达到最大吸附容量,并分别用Pseudofirst-order模型和Pseudo second-order模型对数据进行了拟合计算与分析。The adsorption kinetics of Microgel-AO for different concentrations of U(VI) are shown in Fig. 4. It can be seen from the figure that the adsorption capacity of Microgel-AO increased rapidly within the first 5 minutes and reached the maximum adsorption capacity within 10 minutes. The Pseudo first-order model and the Pseudo second-order model were used to fit, calculate and analyze the data respectively.
为研究Microgel-AO的最大吸附容量,我们在U(VI)浓度为10-60mg·L-1范围内进行了吸附平衡试验,采用Langmuir模型和Freundlich模型对吸附数据进行了拟合,并探索了温度对吸附容量的影响。如图5所示,在测试温度范围内,吸附容量随着温度的升高而增加。In order to study the maximum adsorption capacity of Microgel-AO, we carried out adsorption equilibrium experiments in the range of U(VI) concentration of 10-60 mg·L -1 , fitted the adsorption data with Langmuir model and Freundlich model, and explored The effect of temperature on adsorption capacity. As shown in Figure 5, the adsorption capacity increases with increasing temperature in the tested temperature range.
干扰离子与偕胺肟基团的结合可能对偕胺肟基微凝胶吸附U(VI)的吸附容量有巨大影响,我们选取VO3-,Co2+,Ni+,Zn2+,Pb2+,Ca2+,Mg2+,K+和Na+作为U(VI)的竞争离子,研究了吸附剂在VO3-,Co2+,Ni+,Zn2+,Pb2+,Ca2+,Mg2+,K+,Na+和U(VI)的混合溶液中的吸附行为。如图6所示,在众多的干扰离子存在下,Microgel-AO对U(VI)仍具有最高的吸附容量,远大于VO3-,Co2+,Ni+,Cu2+,Zn2+,Pb2+等低浓度金属离子相应的吸附容量。The combination of interfering ions and amidoxime groups may have a huge impact on the adsorption capacity of amidoxime-based microgels for U(VI) adsorption. We selected VO 3- , Co 2+ , Ni + , Zn 2+ , Pb 2 + , Ca 2+ , Mg 2+ , K + and Na + were used as competing ions for U(VI ) . Adsorption behavior in mixed solutions of + , Mg 2+ , K + , Na + and U(VI). As shown in Figure 6, in the presence of numerous interfering ions, Microgel-AO still has the highest adsorption capacity for U(VI), which is much larger than that of VO 3- , Co 2+ , Ni + , Cu 2+ , Zn 2+ , The corresponding adsorption capacity of low-concentration metal ions such as Pb 2+ .
说明:以上实施例仅用以说明本发明而并非限制本发明所描述的技术方案;因此,尽管本说明书参照上述的各个实施例对本发明已进行了详细的说明,但是本领域的普通技术人员应当理解,仍然可以对本发明进行修改或等同替换;而一切不脱离本发明的精神和范围的技术方案及其改进,其均应涵盖在本发明的权利要求范围内。Explanation: The above embodiments are only used to illustrate the present invention and not to limit the technical solutions described in the present invention; therefore, although this specification has described the present invention in detail with reference to the above-mentioned various embodiments, those of ordinary skill in the art should It should be understood that the present invention can still be modified or equivalently replaced; and all technical solutions and improvements that do not depart from the spirit and scope of the present invention should be covered within the scope of the claims of the present invention.
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