CN107213877B - Synthetic method of imprinted mesoporous material with high selectivity to bisphenol A - Google Patents
Synthetic method of imprinted mesoporous material with high selectivity to bisphenol A Download PDFInfo
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- IISBACLAFKSPIT-UHFFFAOYSA-N bisphenol A Chemical compound C=1C=C(O)C=CC=1C(C)(C)C1=CC=C(O)C=C1 IISBACLAFKSPIT-UHFFFAOYSA-N 0.000 title claims abstract description 137
- 239000013335 mesoporous material Substances 0.000 title claims abstract description 117
- 238000010189 synthetic method Methods 0.000 title claims description 3
- SNEFVJQHWBOIMY-UHFFFAOYSA-M hexadecyl(trimethoxy)azanium;bromide Chemical compound [Br-].CCCCCCCCCCCCCCCC[N+](OC)(OC)OC SNEFVJQHWBOIMY-UHFFFAOYSA-M 0.000 claims abstract description 27
- 238000003756 stirring Methods 0.000 claims abstract description 25
- HEMHJVSKTPXQMS-UHFFFAOYSA-M Sodium hydroxide Chemical compound [OH-].[Na+] HEMHJVSKTPXQMS-UHFFFAOYSA-M 0.000 claims abstract description 24
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- 239000000178 monomer Substances 0.000 claims abstract description 20
- BOTDANWDWHJENH-UHFFFAOYSA-N Tetraethyl orthosilicate Chemical compound CCO[Si](OCC)(OCC)OCC BOTDANWDWHJENH-UHFFFAOYSA-N 0.000 claims abstract description 13
- 238000000034 method Methods 0.000 claims abstract description 12
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J20/00—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
- B01J20/22—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising organic material
- B01J20/26—Synthetic macromolecular compounds
- B01J20/268—Polymers created by use of a template, e.g. molecularly imprinted polymers
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J20/00—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
- B01J20/28—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof characterised by their form or physical properties
- B01J20/28054—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof characterised by their form or physical properties characterised by their surface properties or porosity
- B01J20/28078—Pore diameter
- B01J20/28083—Pore diameter being in the range 2-50 nm, i.e. mesopores
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/28—Treatment of water, waste water, or sewage by sorption
- C02F1/285—Treatment of water, waste water, or sewage by sorption using synthetic organic sorbents
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2101/00—Nature of the contaminant
- C02F2101/30—Organic compounds
- C02F2101/34—Organic compounds containing oxygen
- C02F2101/345—Phenols
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Abstract
本发明提供一种对双酚A具有高选择性的印迹介孔材料的合成方法,包括以下步骤:(1)将模版分子双酚A和功能单体均匀混合,获得预作用溶液;(2)将十六烷基三甲氧基溴化铵溶于水中,用氢氧化钠溶液调节pH值至10.5‑11.5,搅拌50‑70分钟;向溶液中加入正硅酸乙酯,搅拌20‑40分钟;向溶液中加入所述预作用溶液,搅拌100‑140分钟;将其进行水热晶化,获得混合物;(3)将所述混合物烘干,再除去模版分子双酚A。本发明易于实施;所得的印迹介孔材料,不仅对双酚A具有高选择性,而且具有很大的吸附容量、较好的循环使用性能和重现性。
The invention provides a method for synthesizing an imprinted mesoporous material with high selectivity to bisphenol A, comprising the following steps: (1) uniformly mixing template molecule bisphenol A and functional monomers to obtain a preaction solution; (2) Dissolve cetyltrimethoxyammonium bromide in water, adjust the pH to 10.5-11.5 with sodium hydroxide solution, and stir for 50-70 minutes; add ethyl orthosilicate to the solution, and stir for 20-40 minutes; The preaction solution is added to the solution and stirred for 100-140 minutes; it is subjected to hydrothermal crystallization to obtain a mixture; (3) the mixture is dried, and then the template molecule bisphenol A is removed. The invention is easy to implement; the obtained imprinted mesoporous material not only has high selectivity to bisphenol A, but also has large adsorption capacity, good recycling performance and reproducibility.
Description
技术领域technical field
本发明属于分子印迹技术领域,主要涉及一种分子印迹介孔材料合成方法。The invention belongs to the technical field of molecular imprinting, and mainly relates to a method for synthesizing molecularly imprinted mesoporous materials.
背景技术Background technique
双酚A(BPA)是世界上广泛使用的工业原料之一,主要用于生产多种高分子材料及精细化工产品。目前,在水、沉积物、土壤、大气环境和生物体内均已检出双酚A。双酚A属低毒性化学物,也是一种环境雌激素;微量甚至痕量的双酚A即可对动物的生理状况、生殖系统以及胎儿发育造成不良影响,会对生物体的内分泌、生殖和神经系统产生广泛的不良作用。国内外政府已针对双酚A在消费领域的安全性陆续采取措施,包括限制减少双酚A用量,及禁止其用于婴儿奶品等部分产品生产。因此,开发对双酚A具有高选择性的新型吸附材料成为了研究的热点。Bisphenol A (BPA) is one of the most widely used industrial raw materials in the world, mainly used to produce various polymer materials and fine chemical products. At present, bisphenol A has been detected in water, sediment, soil, atmospheric environment and organisms. Bisphenol A is a low toxicity chemical and is also an environmental estrogen; trace or even trace amounts of bisphenol A can have adverse effects on the physiological status, reproductive system and fetal development of animals, and can adversely affect the endocrine, reproductive and fetal development of organisms. Nervous system produces a wide range of adverse effects. Governments at home and abroad have successively taken measures against the safety of bisphenol A in the consumption field, including restricting and reducing the amount of bisphenol A, and prohibiting its use in the production of some products such as baby milk. Therefore, the development of novel adsorbents with high selectivity to bisphenol A has become a research hotspot.
1994年,Sellergren首次报道了在国相萃取中使用分子印迹聚合物作为吸附剂的研究,此后,分子印迹-固相萃取技术迅速发展。分子印迹聚合物对目标分子具有“记忆”效应,能够高选择性地识别复杂样品中的目标分子。有关研究结果显示,分子印迹聚合物作为国相萃取吸附剂,不仅选择性高,而且具有结合力强、可重复利用和成本低的优点。In 1994, Sellergren first reported the use of molecularly imprinted polymers as adsorbents in national phase extraction. Since then, molecularly imprinted-solid phase extraction technology has developed rapidly. Molecularly imprinted polymers have a "memory" effect on target molecules and can recognize target molecules in complex samples with high selectivity. Relevant research results show that molecularly imprinted polymers, as adsorbents for national phase extraction, not only have high selectivity, but also have the advantages of strong binding force, reusability and low cost.
现有技术中有以磁性材料为载体制备出磁性分子印迹聚合物。然而,磁性分子印迹聚合物的部分印迹位点包埋于聚合物本体之中,造成模板分子洗脱不彻底。另外,现有技术中的分子印迹聚合物在水相中对双酚A的选择吸附性和吸附容量明显较低。In the prior art, magnetic molecularly imprinted polymers are prepared by using magnetic materials as carriers. However, some of the imprinted sites of the magnetic molecularly imprinted polymer are embedded in the polymer body, resulting in incomplete elution of the template molecule. In addition, the molecularly imprinted polymers in the prior art have significantly lower selective adsorption and adsorption capacity for bisphenol A in the aqueous phase.
可见,开发一种能制备出对双酚A具有高选择性、且吸附容量大的分子印迹材料的方法实属必要。It can be seen that it is necessary to develop a method for preparing molecularly imprinted materials with high selectivity to bisphenol A and large adsorption capacity.
发明内容SUMMARY OF THE INVENTION
为了克服现有技术缺陷,本发明提供了一种对双酚A具有高选择性印迹介孔材料的合成方法;所制备出的印迹介孔材料,不仅对双酚A具有高选择性,且吸附容量很大。In order to overcome the defects of the prior art, the present invention provides a method for synthesizing an imprinted mesoporous material with high selectivity to bisphenol A; the prepared imprinted mesoporous material not only has high selectivity to bisphenol A, but also adsorbs bisphenol A. Great capacity.
为了解决上述问题,本发明按以下技术方案予以实现的:In order to solve the above problems, the present invention is realized according to the following technical solutions:
一种对双酚A具有高选择性的印迹介孔材料的合成方法,包括以下步骤:A method for synthesizing an imprinted mesoporous material with high selectivity to bisphenol A, comprising the following steps:
(1)将模版分子双酚A和功能单体混合,搅拌100-140分钟,获得预作用溶液;(1) mixing template molecule bisphenol A and functional monomer, stirring for 100-140 minutes to obtain a preaction solution;
(2)将十六烷基三甲氧基溴化铵(CTAB)溶于水中,用氢氧化钠溶液调节pH值为10.5-11.5,搅拌50-70分钟;向溶液中加入正硅酸乙酯(TEOS),搅拌20-40分钟;向溶液中加入所述预作用溶液,搅拌100-140分钟;将其进行水热晶化,获得混合物;(2) Dissolve hexadecyl trimethoxy ammonium bromide (CTAB) in water, adjust the pH value with sodium hydroxide solution to be 10.5-11.5, stir for 50-70 minutes; add ethyl orthosilicate ( TEOS), stirring for 20-40 minutes; adding the preaction solution to the solution, stirring for 100-140 minutes; subjecting it to hydrothermal crystallization to obtain a mixture;
(3)将所述混合物烘干,再除去模版分子双酚A。(3) drying the mixture, and then removing the template molecule bisphenol A.
优选的,在温度为35-45℃的条件下进行所述步骤(1)至(3)。Preferably, the steps (1) to (3) are carried out at a temperature of 35-45°C.
特别优选的,在温度为40℃的条件下进行所述步骤(1)至(3)。本申请发明人发现,在当反应温度为40℃时,可以提高各步骤的反应效率。Particularly preferably, the steps (1) to (3) are carried out at a temperature of 40°C. The inventors of the present application found that when the reaction temperature is 40°C, the reaction efficiency of each step can be improved.
优选的,所述功能单体的制备方法,包括以下步骤:将2-巯基-4-甲基-5-噻唑乙酸(MMTA)和KH-570溶于乙醇中,用三乙胺溶液调节pH值至7.5-8.5,在温度为35-45℃的条件下,搅拌50-70分钟,获得功能单体。Preferably, the preparation method of the functional monomer includes the following steps: dissolving 2-mercapto-4-methyl-5-thiazole acetic acid (MMTA) and KH-570 in ethanol, and adjusting the pH value with triethylamine solution To 7.5-8.5, under the condition of temperature of 35-45 ℃, stirring for 50-70 minutes to obtain functional monomer.
特别优选的,所述功能单体的制备方法,包括以下步骤:将2-巯基-4-甲基-5-噻唑乙酸(MMTA)和KH-570溶于乙醇中,用三乙胺溶液调节pH值至8,在温度为40℃的条件下,搅拌60分钟,获得功能单体。Particularly preferably, the preparation method of the functional monomer includes the following steps: dissolving 2-mercapto-4-methyl-5-thiazole acetic acid (MMTA) and KH-570 in ethanol, and adjusting the pH with triethylamine solution value to 8, and stirring for 60 minutes at a temperature of 40° C. to obtain a functional monomer.
优选的,所述2-巯基-4-甲基-5-噻唑乙酸(MMTA)和KH-570的摩尔比为1-2∶1-2。Preferably, the molar ratio of the 2-mercapto-4-methyl-5-thiazole acetic acid (MMTA) to KH-570 is 1-2:1-2.
特别优选的,所述2-巯基-4-甲基-5-噻唑乙酸(MMTA)和KH-570的摩尔比为1∶1。Particularly preferably, the molar ratio of the 2-mercapto-4-methyl-5-thiazole acetic acid (MMTA) and KH-570 is 1:1.
优选的,所述2-巯基-4-甲基-5-噻唑乙酸(MMTA)和乙醇的摩尔体积比mol∶L为1∶4.5-5.5。Preferably, the molar volume ratio mol:L of the 2-mercapto-4-methyl-5-thiazoleacetic acid (MMTA) and ethanol is 1:4.5-5.5.
特别优选的,所述2-巯基-4-甲基-5-噻唑乙酸(MMTA)和乙醇的摩尔体积比mol∶L为1∶5。Particularly preferably, the molar volume ratio mol:L of the 2-mercapto-4-methyl-5-thiazole acetic acid (MMTA) and ethanol is 1:5.
优选的,所述步骤(1)包括,将模版分子双酚A和功能单体混合,剧烈搅拌2小时,获得预作用溶液。所述剧烈搅拌,在转速为150-200rpm的条件下搅拌;能使模版分子双酚A与功能单体之间进一步形成氢键和π-π相互作用。Preferably, the step (1) includes mixing the template molecule bisphenol A and the functional monomer, and vigorously stirring for 2 hours to obtain a preaction solution. The vigorous stirring is carried out under the condition that the rotating speed is 150-200 rpm, which can further form hydrogen bonds and π-π interaction between the template molecule bisphenol A and the functional monomer.
优选的,所述步骤(2)包括,在温度为40℃的条件下,将十六烷基三甲氧基溴化铵(CTAB)溶于水中,用氢氧化钠溶液调节pH值为11,搅拌60分钟;向溶液中逐滴加入正硅酸乙酯,搅拌30分钟;向溶液中逐滴加入所述预作用溶液,搅拌120分钟;将其进行水热晶化,获得产物。Preferably, the step (2) includes, at a temperature of 40°C, dissolving cetyltrimethoxyammonium bromide (CTAB) in water, adjusting the pH to 11 with sodium hydroxide solution, stirring 60 minutes; add ethyl orthosilicate dropwise to the solution and stir for 30 minutes; add the preaction solution dropwise to the solution and stir for 120 minutes; perform hydrothermal crystallization to obtain the product.
优选的,所述模版分子双酚A和功能单体的摩尔比为1∶4.5-5.5。Preferably, the molar ratio of the template molecule bisphenol A to the functional monomer is 1:4.5-5.5.
特别优选的,所述模版分子双酚A和功能单体的摩尔比为1∶5。Particularly preferably, the molar ratio of the template molecule bisphenol A and the functional monomer is 1:5.
优选的,所述模版分子双酚A、十六烷基三甲氧基溴化铵(CTAB)和正硅酸乙酯(TEOS)的摩尔比为1∶2.5-3.0∶21.6-26.4。Preferably, the molar ratio of the template molecule bisphenol A, cetyltrimethoxyammonium bromide (CTAB) and ethyl orthosilicate (TEOS) is 1:2.5-3.0:21.6-26.4.
特别优选的,所述模版分子双酚A、十六烷基三甲氧基溴化铵(CTAB)和正硅酸乙酯(TEOS)的摩尔比为1∶2.74∶24。Particularly preferably, the molar ratio of the template molecule bisphenol A, cetyltrimethoxyammonium bromide (CTAB) and ethyl orthosilicate (TEOS) is 1:2.74:24.
优选的,所述十六烷基三甲氧基溴化铵(CTAB)和水的质量体积比g∶ml比为1∶35-45。Preferably, the mass-to-volume ratio g:ml of the hexadecyltrimethoxyammonium bromide (CTAB) and water is 1:35-45.
特别优选的,所述十六烷基三甲氧基溴化铵(CTAB)和水的质量体积比g∶ml比为1∶40。Particularly preferably, the mass-to-volume ratio g:ml of the hexadecyltrimethoxyammonium bromide (CTAB) and water is 1:40.
优选的,步骤(2)中所述水为去离子水。Preferably, the water in step (2) is deionized water.
优选的,所述氢氧化钠溶液的摩尔浓度为8-12mol/L。Preferably, the molar concentration of the sodium hydroxide solution is 8-12 mol/L.
特别优选的,所述氢氧化钠溶液的摩尔浓度为10mol/L。Particularly preferably, the molar concentration of the sodium hydroxide solution is 10 mol/L.
优选的,所述水热晶化为在温度为80-90℃的条件下,水热晶化70-74小时。Preferably, the hydrothermal crystallization is hydrothermal crystallization at a temperature of 80-90° C. for 70-74 hours.
特别优选的,所述水热晶化为在温度为85℃的条件下,水热晶化72小时。Particularly preferably, the hydrothermal crystallization is hydrothermal crystallization at a temperature of 85° C. for 72 hours.
优选的,所述除去模版分子双酚A的步骤为用盐酸和乙醇的混合溶液进行索氏提取。Preferably, the step of removing the template molecule bisphenol A is to perform Soxhlet extraction with a mixed solution of hydrochloric acid and ethanol.
优选的,所述索氏提取时间为88-104小时。Preferably, the Soxhlet extraction time is 88-104 hours.
特别优选的,所述索氏提取时间为96小时。Particularly preferably, the Soxhlet extraction time is 96 hours.
优选的,所述盐酸和乙醇的体积比为1∶8.1-9.9。Preferably, the volume ratio of the hydrochloric acid and ethanol is 1:8.1-9.9.
特别优选的,所述盐酸和乙醇的体积比为1∶9。Particularly preferably, the volume ratio of the hydrochloric acid and ethanol is 1:9.
本发明具有以下有益效果:The present invention has the following beneficial effects:
1、本发明所制备的印迹介孔材料具有高度有序并紧密排列的六边形孔道结构的形貌,且颗粒分布较均匀;印迹介孔材料的平均孔径为3.6nm,孔容为1.58cm3g-1。1. The imprinted mesoporous material prepared by the present invention has the morphology of a highly ordered and closely arranged hexagonal channel structure, and the particle distribution is relatively uniform; the average pore diameter of the imprinted mesoporous material is 3.6 nm, and the pore volume is 1.58 cm. 3 g -1 .
2、在pH值为6.5时,印迹介孔材料对双酚A具有最大的吸附量。在双酚A溶液浓度为700mg/L时,印迹介孔材料可达到饱和吸附平衡,其吸附量为88.6mg/g;可见,本发明所制备的印迹介孔材料具有很大的吸附容量。2. When the pH value is 6.5, the imprinted mesoporous material has the maximum adsorption capacity for bisphenol A. When the concentration of bisphenol A solution is 700mg/L, the imprinted mesoporous material can reach saturated adsorption equilibrium, and its adsorption capacity is 88.6 mg/g; it can be seen that the imprinted mesoporous material prepared by the present invention has a large adsorption capacity.
3、本发明所制备的印迹介孔材料对双酚A存在具有选择性的印迹位点,拥有对双酚A良好的选择性识别能力。3. The imprinted mesoporous material prepared by the present invention has selective imprinting sites for bisphenol A, and has good selective recognition ability for bisphenol A.
4、本发明所制备的印迹介孔材料(MIPs)经过5次重复使用后,回收率能保持在98.0%以上,说明印迹介孔材料(MIPs)有较好的循环使用性能。4. The recovery rate of the imprinted mesoporous materials (MIPs) prepared by the present invention can be kept above 98.0% after repeated use for 5 times, indicating that the imprinted mesoporous materials (MIPs) have good recycling performance.
5、本发明所制备的印迹介孔材料(MIPs)具有很好的重现性。在不同时间,使用本发明技术方案合成的5个批次印迹介孔材料(MIPs)进行吸附试验,5个批次的印迹介孔材料(MIPs)的对双酚A的吸附量的相对标准偏差(RSD)仅为1.1%。5. The imprinted mesoporous materials (MIPs) prepared by the present invention have good reproducibility. At different times, 5 batches of imprinted mesoporous materials (MIPs) synthesized by the technical solution of the present invention were used for adsorption experiments, and the relative standard deviation of the adsorption amount of bisphenol A by 5 batches of imprinted mesoporous materials (MIPs) (RSD) was only 1.1%.
附图说明Description of drawings
图1是本发明的合成路线图;Fig. 1 is the synthetic route diagram of the present invention;
图2是本发明实施例1制备的印迹介孔材料(MIPs)索氏提取前后的红外光谱图;Fig. 2 is the infrared spectrum before and after Soxhlet extraction of imprinted mesoporous materials (MIPs) prepared in Example 1 of the present invention;
图3是本发明实施例1制备的印迹介孔材料(MIPs)的小角XRD衍射图;3 is a small-angle XRD diffractogram of the imprinted mesoporous material (MIPs) prepared in Example 1 of the present invention;
图4是本发明实施例1制备的印迹介孔材料(MIPs)的扫描电子显微镜(SEM)图;4 is a scanning electron microscope (SEM) image of the imprinted mesoporous materials (MIPs) prepared in Example 1 of the present invention;
图5是本发明实施例1制备的印迹介孔材料(MIPs)的透视电子显微镜(TEM)图;5 is a perspective electron microscope (TEM) image of the imprinted mesoporous materials (MIPs) prepared in Example 1 of the present invention;
图6是本发明实施例1制备的印迹介孔材料(MIPs)的氮气吸附脱附曲线图;6 is a graph of nitrogen adsorption and desorption curves of imprinted mesoporous materials (MIPs) prepared in Example 1 of the present invention;
图7是本发明实施例1制备的印迹介孔材料(MIPs)的孔径分布图;7 is a pore size distribution diagram of the imprinted mesoporous materials (MIPs) prepared in Example 1 of the present invention;
图8是pH对本发明实施例1制备的印迹介孔材料(MIPs)吸附量的影响图;8 is a graph showing the effect of pH on the adsorption capacity of the imprinted mesoporous materials (MIPs) prepared in Example 1 of the present invention;
图9是本发明实施例1制备的印迹介孔材料(MIPs)的吸附曲线图;9 is an adsorption curve diagram of the imprinted mesoporous materials (MIPs) prepared in Example 1 of the present invention;
图10是本发明实施例1制备的印迹介孔材料(MIPs)吸附动力曲线图;10 is a graph showing the adsorption kinetics of the imprinted mesoporous materials (MIPs) prepared in Example 1 of the present invention;
图11是本发明实施例1制备的印迹介孔材料(MIPs)重复性实验数据图。FIG. 11 is a graph of the repeatability experimental data of the imprinted mesoporous materials (MIPs) prepared in Example 1 of the present invention.
具体实施方式Detailed ways
下面结合实施例对本发明的技术方案做进一步说明:Below in conjunction with embodiment, the technical scheme of the present invention is further described:
实施例1:Example 1:
1)功能单体的制备:1) Preparation of functional monomers:
在10ml烧瓶中将1.0mmol的2-巯基-4-甲基-5-噻唑乙酸(MMTA)和1.0mmol的KH-570溶于5ml乙醇中,用三乙胺调节溶液pH值至8。在温度为40℃的条件下,搅拌2小时;获得淡黄色液体为功能单体,将其密封保存。In a 10 ml flask, 1.0 mmol of 2-mercapto-4-methyl-5-thiazole acetic acid (MMTA) and 1.0 mmol of KH-570 were dissolved in 5 ml of ethanol, and the pH of the solution was adjusted to 8 with triethylamine. Under the condition of temperature of 40°C, stirring was carried out for 2 hours; the light yellow liquid was obtained as functional monomer, which was sealed and stored.
2)对双酚A具有高选择性的印迹介孔材料的制备:2) Preparation of imprinted mesoporous materials with high selectivity to bisphenol A:
(1)取0.25mol的模板分子双酚A和1.0mmol的功能单体混合,在水浴温度为40℃的条件下,剧烈搅拌2小时,获得预作用溶液。(1) Mix 0.25 mol of template molecule bisphenol A with 1.0 mmol of functional monomer, and stir vigorously for 2 hours under the condition of a water bath temperature of 40° C. to obtain a preaction solution.
(2)在水浴温度为40℃的条件下,另取1.0g的十六烷基三甲氧基溴化铵(CTAB)溶解于40mL的去离子水中,用10mol/L的氢氧化钠溶液调节pH值至11.0,搅拌1小时。向溶液中逐滴加入5.2g的正硅酸乙酯(TEOS),搅拌30分钟;再向溶液中逐滴加入预作用溶液,搅拌2h;将其移至水热反应釜中,在温度为85℃条件下,水热晶化72小时,获得混合物。(2) Under the condition that the temperature of the water bath is 40°C, take another 1.0g of cetyltrimethoxyammonium bromide (CTAB) and dissolve it in 40mL of deionized water, and adjust the pH with 10mol/L sodium hydroxide solution value to 11.0 and stir for 1 hour. Add 5.2g of tetraethyl orthosilicate (TEOS) dropwise to the solution and stir for 30 minutes; add the preaction solution dropwise to the solution and stir for 2h; move it to a hydrothermal reaction kettle, at a temperature of 85 Under the condition of °C, hydrothermal crystallization was carried out for 72 hours to obtain a mixture.
(3)混合物经过抽滤烘干后,用体积比为1∶9的盐酸和乙醇混合溶液,在水浴温度为40℃的条件下,进行索氏提取96小时,除去模板分子双酚A,同时也除去十六烷基三甲氧基溴化铵(CTAB),将所得产物烘干,即得印迹介孔材料(MIPs)。(3) after the mixture is dried by suction filtration, use a hydrochloric acid and ethanol mixed solution with a volume ratio of 1:9, under the condition that the water bath temperature is 40 ° C, carry out Soxhlet extraction for 96 hours, remove the template molecule bisphenol A, and simultaneously Cetyltrimethoxyammonium bromide (CTAB) was also removed, and the resulting product was dried to obtain imprinted mesoporous materials (MIPs).
附:Attached:
1)合成路线图,见图1;1) synthetic route map, see Fig. 1;
2)实验试剂和实验仪器,见表1和表2。2) Experimental reagents and experimental instruments, see Table 1 and Table 2.
表1 实验试剂Table 1 Experimental reagents
表2 实验仪器Table 2 Experimental equipment
实施1所制备出的印迹材料的结构表征:Structural characterization of the imprinted material prepared in Example 1:
A.红外光谱表征:A. Infrared Spectral Characterization:
由图2可见,1040cm-1、960cm-1、791cm-1,三个吸收峰是介孔材料(硅基材料)的特征峰。索氏提取前的印迹介孔材料(MIPs)在2800-3000cm-1区域存在代表C-H的对称和非对称振动的尖锐的吸收峰,这是由于致孔剂十六烷基三甲氧基溴化铵(CTAB)的存在。经乙醇∶盐酸(9∶1=V/V)索氏提取后,C-H特征吸收峰消失,说明CTAB已洗脱干净。洗脱前后印迹介孔材料(MIPs)在1640cm-1处的吸收峰为C=O的伸缩振动吸收峰,说明功能单体已成功参与介孔材料的骨架合成。It can be seen from FIG. 2 that the three absorption peaks at 1040 cm -1 , 960 cm -1 , and 791 cm -1 are characteristic peaks of the mesoporous material (silicon-based material). Imprinted mesoporous materials (MIPs) before Soxhlet extraction have sharp absorption peaks in the 2800-3000 cm -1 region representing the symmetric and asymmetric vibrations of CH, which is due to the porogen cetyltrimethoxyammonium bromide (CTAB) presence. After Soxhlet extraction with ethanol:hydrochloric acid (9:1=V/V), the characteristic absorption peak of CH disappeared, indicating that CTAB had been eluted. The absorption peaks at 1640 cm -1 of the imprinted mesoporous materials (MIPs) before and after elution are the stretching vibration absorption peaks of C=O, indicating that the functional monomers have successfully participated in the framework synthesis of mesoporous materials.
B.小角度XRD表征:B. Small angle XRD characterization:
由图3可见,三个明显的特征峰,分别为(100),(110)和(200)晶面,小角XRD的表征结果说明印迹介孔材料(MIPs)具有高度有序的MCM-41介孔的特征结构。It can be seen from Figure 3 that three distinct characteristic peaks are (100), (110) and (200) crystal planes, respectively. The characterization results of small-angle XRD indicate that the imprinted mesoporous materials (MIPs) have highly ordered MCM-41 mesoporous materials. The characteristic structure of the hole.
C.电镜表征:C. Electron Microscopy Characterization:
由图4可见,所合成的印迹介孔材料(MIPs)颗粒分布较均匀。It can be seen from Figure 4 that the synthesized imprinted mesoporous materials (MIPs) have relatively uniform particle distribution.
由图5可见,印迹介孔材料(MIPs)具有高度有序并紧密排列的六边形孔道结构的形貌。It can be seen from Fig. 5 that the imprinted mesoporous materials (MIPs) have the morphology of highly ordered and closely arranged hexagonal channel structure.
D.氮气吸附脱附表征:D. Characterization of nitrogen adsorption and desorption:
用氮气吸附脱附实验测定了印迹介孔材料(MIPs)的孔径、孔容。The pore size and pore volume of imprinted mesoporous materials (MIPs) were determined by nitrogen adsorption and desorption experiments.
由图6所示,印迹介孔材料(MIPs)的氮吸附-脱附等温线是一种IV型曲线,是介孔材料典型的氮吸附-脱附等温线。采用Bnmauer-Enunett-Teller(BET)方法计算出该材料的比表面积为960.5m2g-1,孔容为1.58cm3g-1,这一数值表明该印迹介孔材料(MIPs)具有较大的比表面积和孔容,有利于印迹位点的大量分布和再吸附过程。As shown in Figure 6, the nitrogen adsorption-desorption isotherm of imprinted mesoporous materials (MIPs) is a type IV curve, which is a typical nitrogen adsorption-desorption isotherm of mesoporous materials. Using the Bnmauer-Enunett-Teller (BET) method, the specific surface area of the material was calculated to be 960.5m 2 g -1 , and the pore volume was 1.58cm 3 g -1 , which indicated that the imprinted mesoporous materials (MIPs) had larger The specific surface area and pore volume are favorable for the mass distribution of imprinted sites and the resorption process.
由图7可知,该印迹介孔材料(MIPs)的孔径分布均一,有较为集中而尖锐的峰型分布,主要集中在3.4-3.9nm之间,证明材料具有高度有序性。采用Barrett-Joyner-Halenda(BJH)方法得到了该材料的平均孔径为3.6nm。It can be seen from Figure 7 that the pore size distribution of the imprinted mesoporous materials (MIPs) is uniform, with a relatively concentrated and sharp peak distribution, mainly between 3.4-3.9 nm, which proves that the material has a high degree of order. The average pore size of the material obtained by the Barrett-Joyner-Halenda (BJH) method is 3.6 nm.
考察实施1所制备出的印迹材料吸附性能的实验:Experiments to investigate the adsorption properties of the imprinted materials prepared in Implementation 1:
为了考察印迹材料的吸附性能,可用吸附量和吸附速率两个物理量来表征。吸附量反应了吸附剂对一定浓度底物的吸附能力的大小,是一个非常重要的热力学参数。In order to investigate the adsorption properties of the imprinted materials, two physical quantities, the adsorption amount and the adsorption rate, can be used to characterize them. The adsorption capacity reflects the adsorption capacity of the adsorbent to a certain concentration of substrate, and is a very important thermodynamic parameter.
吸附量的计算公式(1-1)如下:The calculation formula (1-1) of the adsorption capacity is as follows:
Q=(CO-Ct)V/M (1-1)Q=(C O -C t )V/M (1-1)
式中,Q——t时刻的吸附量(mg/g);In the formula, Q—the amount of adsorption at time t (mg/g);
CO——待吸附物质的初始浓度(mg/L); CO ——the initial concentration of the substance to be adsorbed (mg/L);
Ct——待吸附物质t时刻的浓度(mg/L);C t ——the concentration of the substance to be adsorbed at time t (mg/L);
M——吸附剂质量(mg);M - adsorbent mass (mg);
V——反应溶液体积(mL)。V—volume of reaction solution (mL).
A.pH值对印迹介孔材料(MIPs)吸附性能A的影响:A. Effect of pH value on adsorption performance A of imprinted mesoporous materials (MIPs):
探究不同pH值条件下(pH=5-8),印迹介孔材料(MIPs)对目标分子双酚A的吸附作用。在不同pH条件(pH=5-8)的体积为3mL、浓度为200mg/L的双酚A溶液中,分别加入10mg的印迹介孔材料(MIPs),室温震荡4h后,离心分离,再用高效液相色谱法检测滤液中双酚A的浓度。代入公式1-1中算出印迹介孔材料(MIPs)的吸附量,从而得出pH对吸附量的影响。The adsorption effect of imprinted mesoporous materials (MIPs) on the target molecule bisphenol A was investigated under different pH conditions (pH=5-8). 10 mg of imprinted mesoporous materials (MIPs) were added to the bisphenol A solution with a volume of 3 mL and a concentration of 200 mg/L under different pH conditions (pH=5-8), and after shaking at room temperature for 4 h, centrifuged, and then used The concentration of bisphenol A in the filtrate was detected by high performance liquid chromatography. Substitute into Equation 1-1 to calculate the adsorption capacity of the imprinted mesoporous materials (MIPs), thereby obtaining the effect of pH on the adsorption capacity.
由图8所示,印迹介孔材料(MIPs)的吸附量随pH的变化曲线pH=5.5-6.5时,随着pH的变大,印迹介孔材料(MIPs)的吸附量也随之增加,这可能是因为酸度过强会使芳环上负电子的π电子云密度降低,从而减弱环与环之间的π-π相互作用,导致吸附量减小。在pH=6.5-8时,随着溶液碱性增强,双酚A中的羟基和功能单体的羧基部分去质子化,导致分子间氢键作用力减小,进一步导致吸附量减小。因此,当pH=6.5时,模板分子双酚A和功能单体之间的作用力最强,对应的吸附量达到最大。最大的吸附量为15.6mg/g。As shown in Fig. 8, the adsorption amount of imprinted mesoporous materials (MIPs) changed with pH. When pH=5.5-6.5, as the pH increased, the adsorption amount of imprinted mesoporous materials (MIPs) also increased. This may be because too strong acidity will reduce the π-electron cloud density of the negative electrons on the aromatic ring, thereby weakening the π-π interaction between the rings and reducing the adsorption capacity. At pH=6.5-8, with the increasing alkalinity of the solution, the hydroxyl groups in bisphenol A and the carboxyl groups of functional monomers are partially deprotonated, resulting in a decrease in the intermolecular hydrogen bond force, which further leads to a decrease in the adsorption capacity. Therefore, when pH=6.5, the interaction force between the template molecule bisphenol A and the functional monomer is the strongest, and the corresponding adsorption amount reaches the maximum. The maximum adsorption amount was 15.6 mg/g.
B.饱和吸附曲线的测定:B. Determination of saturation adsorption curve:
将10mg的印迹介孔材料(MIPs)、非印迹介孔材料(NIPs)和介孔材料(MCM-41)分别加入到pH值为6.5、体积为10mL的一系列浓度为50-1000mg/L双酚A溶液中,震荡4h后,离心分离,再用高效液相色谱仪检测滤液中双酚A的浓度,代入公式1-1中分别计算出印迹介孔材料(MIPs)、非印迹介孔材料(NIPs)和介孔材料(MCM-41)的吸附量。10 mg of imprinted mesoporous materials (MIPs), non-imprinted mesoporous materials (NIPs) and mesoporous materials (MCM-41) were added to a series of concentrations of 50-1000 mg/L bilayer in a volume of 10 mL at pH 6.5. In the phenol A solution, after shaking for 4 hours, centrifuge separation, and then use high performance liquid chromatography to detect the concentration of bisphenol A in the filtrate, and substitute it into formula 1-1 to calculate the imprinted mesoporous materials (MIPs) and non-imprinted mesoporous materials respectively. (NIPs) and mesoporous materials (MCM-41).
如图9所示,印迹介孔材料(MIPs)、非印迹介孔材料(NIPs)和介孔材料(MCM-41)在一系列浓度为50-1000mg/L的双酚A溶液的吸附曲线;印迹介孔材料(MIPs)与非印迹介孔材料(NIPs)和介孔材料(MCM-41)相比,表现出更大的吸附容量。印迹介孔材料(MIPs)在双酚A溶液浓度为700mg/L时达到饱和吸附平衡,吸附量为88.6mg/g。相同双酚A溶液浓度下,非印迹介孔材料(NIPs)和介孔材料(MCM-41)的吸附量分别为39.3mg/g和30.2mg/g。印迹介孔材料(MIPs)的吸附量最大说明印迹效果增加了介孔材料的比表面积和孔容。这有利于增加双酚A分子与聚合物中印迹空穴的接触机会以及作用的时间,加强了印迹介孔材料(MIPs)对双酚A的吸附。As shown in Figure 9, the adsorption curves of imprinted mesoporous materials (MIPs), non-imprinted mesoporous materials (NIPs) and mesoporous materials (MCM-41) in a series of bisphenol A solutions with a concentration of 50-1000 mg/L; The imprinted mesoporous materials (MIPs) exhibited larger adsorption capacity compared with the non-imprinted mesoporous materials (NIPs) and mesoporous materials (MCM-41). The imprinted mesoporous materials (MIPs) reached saturated adsorption equilibrium when the concentration of bisphenol A solution was 700 mg/L, and the adsorption capacity was 88.6 mg/g. At the same concentration of bisphenol A solution, the adsorption capacities of non-imprinted mesoporous materials (NIPs) and mesoporous materials (MCM-41) were 39.3 mg/g and 30.2 mg/g, respectively. The maximum adsorption amount of the imprinted mesoporous materials (MIPs) indicated that the imprinting effect increased the specific surface area and pore volume of the mesoporous materials. This is beneficial to increase the contact opportunity and time of action between bisphenol A molecules and imprinted holes in the polymer, and enhance the adsorption of bisphenol A by imprinted mesoporous materials (MIPs).
附:Attached:
1)非印迹介孔材料(NIPs)的合成方法:其与印迹介孔材料(MIPs)的合成方法基本相同,唯一的区别在于步骤(1)中不加入模版分子双酚A。1) Synthesis method of non-imprinted mesoporous materials (NIPs): It is basically the same as the synthetic method of imprinted mesoporous materials (MIPs), the only difference is that the template molecule bisphenol A is not added in step (1).
2)介孔材料(MCM-41)的合成方法:取1.0g十六烷基三甲氧基溴化铵(CTAB)溶于40mL去离子水中,在温度为40℃条件下,搅拌1小时,用10mol/L的Na0H溶液调节pH至11.0;搅拌1.0小时后,逐滴滴加5.2g正硅酸乙酯,搅拌24小时,将其转入到水热反应釜中,在温度为85℃条件下,水热晶化72小时,产物经过抽滤烘干后,用盐酸:乙醇(v:v=1∶9)的混合溶液索氏提取7天,除去十六烷基三甲氧基溴化铵(CTAB),将所得产物烘干,即得介孔材料(MCM-41)。2) Synthesis method of mesoporous material (MCM-41): Dissolve 1.0 g of cetyltrimethoxyammonium bromide (CTAB) in 40 mL of deionized water, stir for 1 hour at a temperature of 40 °C, and use The NaOH solution of 10mol/L was adjusted to pH 11.0; after stirring for 1.0 hours, 5.2g of ethyl orthosilicate was added dropwise, stirred for 24 hours, and transferred to the hydrothermal reactor, at a temperature of 85°C , hydrothermally crystallized for 72 hours, the product was dried by suction filtration, extracted with a mixed solution of hydrochloric acid: ethanol (v:v=1:9) Soxhlet for 7 days, removed hexadecyltrimethoxyammonium bromide ( CTAB), drying the obtained product to obtain mesoporous material (MCM-41).
C.吸附动力学实验:C. Adsorption kinetics experiment:
向浓度分别为60mg/L、800mg/L,pH值为6.5,体积为3mL的双酚A溶液中加入10mg的印迹介孔材料(MIPs),室温下震荡。每隔5分钟,离心分离固体,并用高效液相色谱仪检测滤液中双酚A的浓度,代入公式1-1中计算出印迹介孔材料(MIPs)对双酚A的吸附量,进而来研究其动力学情况。10 mg of imprinted mesoporous materials (MIPs) were added to the bisphenol A solution with a concentration of 60 mg/L, 800 mg/L, pH value of 6.5, and a volume of 3 mL, and shaken at room temperature. Every 5 minutes, the solid was centrifuged, and the concentration of bisphenol A in the filtrate was detected by high performance liquid chromatography, and the adsorption amount of bisphenol A by imprinted mesoporous materials (MIPs) was calculated by substituting into formula 1-1, and then to study its dynamics.
图10所示,印迹介孔材料(MIPs)的吸附动力曲线图为该印迹介孔材料(MIPs)动力学吸附实验结果。本实验选择两种不同浓度的双酚A溶液,分别为60mg/L和800mg/L。溶液pH值为6.5,随着溶液中双酚A浓度的增加,吸附达到平衡的时间也随之增加,分别为15和25min。可见,实施例1制备的印迹介孔材料(MIPs)的吸附动力学时间远远快于普通分子印迹材料,得益于印迹介孔材料大的孔径和比表面积。As shown in FIG. 10 , the adsorption kinetic curve of the imprinted mesoporous material (MIPs) is the result of the kinetic adsorption experiment of the imprinted mesoporous material (MIPs). In this experiment, two different concentrations of bisphenol A solutions were selected, 60 mg/L and 800 mg/L, respectively. The pH value of the solution was 6.5. With the increase of the concentration of bisphenol A in the solution, the time for the adsorption to reach equilibrium also increased, which were 15 and 25 min, respectively. It can be seen that the adsorption kinetic time of the imprinted mesoporous materials (MIPs) prepared in Example 1 is much faster than that of ordinary molecularly imprinted materials, benefiting from the large pore size and specific surface area of the imprinted mesoporous materials.
D.印迹介孔材料(MIPs)的选择性分析:D. Selectivity Analysis of Imprinted Mesoporous Materials (MIPs):
印迹介孔材料(MIPs)的选择性实验,采用4-肉桂苯酚、双酚F、邻苯二酚和苯酚作为结构类似物。配制摩尔浓度为0.6mmol/L的双酚A、4-肉桂苯酚、苯酚、双酚F和邻苯二酚溶液,将10mg的印迹介孔材料(MIPs)和非印迹介孔材料(NIPs)分别加入到体积为10mL的上述溶液中。室温震荡4h后,用离心法分离印迹介孔材料(MIPs)和非印迹介孔材料(NIPs),再用高校液相色谱法检测双酚A、4-肉桂苯酚、双酚F、邻苯二酚和苯酚的浓度,代入公式1-1中计算出印迹介孔材料(MIPs)和非印迹介孔材料(NIPs)的吸附量。印迹介孔材料(MIPs)和非印迹介孔材料(NIPs)对五种化合物得相对选择性系数示于表3。Selectivity experiments on imprinted mesoporous materials (MIPs) using 4-cinnamylphenol, bisphenol F, catechol, and phenol as structural analogs. Prepare bisphenol A, 4-cinnamyl phenol, phenol, bisphenol F, and catechol solutions with molar concentrations of 0.6 mmol/L, and mix 10 mg of imprinted mesoporous materials (MIPs) and non-imprinted mesoporous materials (NIPs), respectively Add to the above solution in a volume of 10 mL. After shaking at room temperature for 4 h, the imprinted mesoporous materials (MIPs) and non-imprinted mesoporous materials (NIPs) were separated by centrifugation, and then bisphenol A, 4-cinnamic phenol, bisphenol F, phthalate were detected by university liquid chromatography. The concentrations of phenol and phenol were substituted into Equation 1-1 to calculate the adsorption capacity of imprinted mesoporous materials (MIPs) and non-imprinted mesoporous materials (NIPs). The relative selectivity coefficients of imprinted mesoporous materials (MIPs) and non-imprinted mesoporous materials (NIPs) for the five compounds are shown in Table 3.
K代表分配系数、RIF代表相对影响因子,计算公式如下:K represents the distribution coefficient, R IF represents the relative impact factor, and the calculation formula is as follows:
K=Q/Ce,K=Q/Ce,
RIF=RMPs/KNIPs。R IF =R MPs /K NIPs .
其中Q是印迹介孔材料(MIPs)或非印迹介孔材料(NIPs)对模板分子或其类似物的吸附量;where Q is the adsorption amount of template molecules or their analogs by imprinted mesoporous materials (MIPs) or non-imprinted mesoporous materials (NIPs);
Ce是被吸附溶液中模板分子或其类似物的剩余浓度;Ce is the remaining concentration of template molecules or their analogs in the adsorbed solution;
KMIPs是印迹介孔材料(MIPs)的分配系数;KNIPs是非印迹介孔材料(NIPs)的分配系数。K MIPs is the partition coefficient of imprinted mesoporous materials (MIPs); K NIPs is the partition coefficient of non-imprinted mesoporous materials (NIPs).
表3 印迹介孔材料(MIPs)和非印迹介孔材料(NIPs)对五种化合物得相对选择性系数Table 3 Relative selectivity coefficients of imprinted mesoporous materials (MIPs) and non-imprinted mesoporous materials (NIPs) for five compounds
从表3-1中可以看到,相对印迹因子从1.06到3.20不等,这个结果表明MIPs对双酚A具有较好的选择性识别能力,对BPA存在具有选择性的印迹位点。KNIPs的值较小且都比较相近,这一结果说明NIPs对BPA的吸附不具备特异选择性,这是因为它不存在对BPA具有选择性识别的印迹位点。It can be seen from Table 3-1 that the relative imprinting factor ranges from 1.06 to 3.20, which indicates that MIPs have better selective recognition ability for bisphenol A, and there are selective imprinting sites for BPA. The values of K NIPs are relatively small and relatively similar, which indicates that NIPs do not have specific selectivity for the adsorption of BPA, because there is no imprinting site that can selectively recognize BPA.
E.印迹介孔材料(MIPs)的重复吸附性和重现性能研究:E. Repeated adsorption and reproducible performance studies of imprinted mesoporous materials (MIPs):
为了考察印迹介孔材料(MIPs)的重复使用性,将10mg印迹介孔材料(MIPs)加入到体积为3mL、浓度为200mg/L、pH值为6.5的双酚A溶液中,室温震荡25min,离心分离,用体积为2mL的盐酸对印迹介孔材料(MIPs)进行洗脱、分离,用高效液相色谱法检测滤液中双酚A的浓度,计算回收率。用去离子水洗涤印迹介孔材料(MIPs)数次,烘干后用于下次的使用。将印迹介孔材料(MIPs)循环使用5次。In order to investigate the reusability of imprinted mesoporous materials (MIPs), 10 mg of imprinted mesoporous materials (MIPs) were added to a bisphenol A solution with a volume of 3 mL, a concentration of 200 mg/L, and a pH value of 6.5, and the solution was shaken at room temperature for 25 min. After centrifugation, the imprinted mesoporous materials (MIPs) were eluted and separated with a volume of 2 mL of hydrochloric acid, and the concentration of bisphenol A in the filtrate was detected by high performance liquid chromatography, and the recovery rate was calculated. The imprinted mesoporous materials (MIPs) were washed several times with deionized water and dried for the next use. The imprinted mesoporous materials (MIPs) were recycled 5 times.
图11所示,将印迹介孔材料(MIPs)经过5次重复使用后,随着循环使用次数的增加,其吸附量有一定程度的降低,但印迹介孔材料(MIPs)的回收率还能保持在98.0%以上,说明材料有较好的循环使用性能。As shown in Figure 11, after the imprinted mesoporous materials (MIPs) were reused for 5 times, the adsorption capacity decreased to a certain extent with the increase of the number of cycles, but the recovery rate of the imprinted mesoporous materials (MIPs) was still It is maintained above 98.0%, indicating that the material has good recycling performance.
为了测试MIPs的重现性,使用不同时间,实例1的合成方法合成的5个批次印迹介孔材料(MIPs)进行吸附试验。实验数据见表4。To test the reproducibility of MIPs, adsorption experiments were performed using 5 batches of imprinted mesoporous materials (MIPs) synthesized by the synthesis method of Example 1 at different times. The experimental data are shown in Table 4.
表4 印迹介孔材料(MIPs)重现性实验Table 4 Reproducibility experiments of imprinted mesoporous materials (MIPs)
表4所示,5个批次的印迹介孔材料(MIPs)的对双酚A的吸附量。根据该数据,计算出5个批次的印迹介孔材料(MIPs)的对双酚A的吸附量的相对标准偏差(RSD)为1.1%,证明实施例1所制备的印迹介孔材料(MIPs)具有非常好的重现性。Table 4 shows the adsorption capacity of bisphenol A for 5 batches of imprinted mesoporous materials (MIPs). According to this data, the relative standard deviation (RSD) of the adsorption amount of bisphenol A for 5 batches of imprinted mesoporous materials (MIPs) was calculated to be 1.1%, which proved that the imprinted mesoporous materials (MIPs) prepared in Example 1 had a relative standard deviation (RSD) of 1.1%. ) with very good reproducibility.
F.实际样品吸附实验:F. Actual sample adsorption experiment:
选取广东佛山高明区杨梅水厂水作为样品溶液,对印迹介孔材料(MIPs)进行实际样品吸附能力进行测试。样品溶液先用0.45微米滤膜进行过滤,除去固体杂质。用高校液相色谱法测定样品中双酚A的含量,含量为0.031mg/L。在体积为30ml的样品溶液中,分别加入20mg、40mg、60mg、80mg、100mg的印迹介孔材料(MIPs),室温下震荡4小时,离心分离印迹介孔材料(MIPs),用高效液相法测定滤液中双酚A的浓度,代入公式1-1中计算出印迹介孔材料(MIPs)的吸附量,实验结果见表5。The water of Yangmei Water Plant in Gaoming District, Foshan, Guangdong was selected as the sample solution to test the actual sample adsorption capacity of imprinted mesoporous materials (MIPs). The sample solution was first filtered with a 0.45-micron filter to remove solid impurities. The content of bisphenol A in the samples was determined by liquid chromatography in colleges and universities, and the content was 0.031 mg/L. In the sample solution with a volume of 30ml, 20mg, 40mg, 60mg, 80mg, 100mg of imprinted mesoporous materials (MIPs) were added respectively, shaken at room temperature for 4 hours, and the imprinted mesoporous materials (MIPs) were centrifuged to separate the imprinted mesoporous materials (MIPs). The concentration of bisphenol A in the filtrate was measured and substituted into formula 1-1 to calculate the adsorption amount of imprinted mesoporous materials (MIPs). The experimental results are shown in Table 5.
表5 不同量的印迹介孔材料(MIPs)对实际样品的吸附性Table 5 Adsorption of different amounts of imprinted mesoporous materials (MIPs) to real samples
由表5所示,通过投入不同量的印迹介孔材料(MIPs)对实际样品进行吸附研究,当加入120mg印迹介孔材料(MIPs),BPA浓度降低到0.008mg/L,低于国家排放标准(GB5749-2006,0.01mg/L)。因此,处理杨梅水厂水需要MIPs的量约为4.0g/L。As shown in Table 5, the adsorption study was carried out on the actual samples by inputting different amounts of imprinted mesoporous materials (MIPs). (GB5749-2006, 0.01mg/L). Therefore, the amount of MIPs required to treat Yangmei water plant water is about 4.0 g/L.
以上所述,仅是本发明的较佳实施例而已,并非对本发明做任何形式上的限制,故凡未脱离本发明技术方案的内容,依据本发明的技术实质对以上实施例所做的任何简单修改、等同变化与修饰,均仍属于本发明技术方案的范围内。The above are only preferred embodiments of the present invention, and are not intended to limit the present invention in any form. Therefore, without departing from the content of the technical solutions of the present invention, any changes made to the above embodiments according to the technical essence of the present invention Simple modifications, equivalent changes and modifications still fall within the scope of the technical solutions of the present invention.
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