[go: up one dir, main page]

CN101298039B - Preparation of chitosan molecular imprinting adsorbing agent - Google Patents

Preparation of chitosan molecular imprinting adsorbing agent Download PDF

Info

Publication number
CN101298039B
CN101298039B CN2008100563985A CN200810056398A CN101298039B CN 101298039 B CN101298039 B CN 101298039B CN 2008100563985 A CN2008100563985 A CN 2008100563985A CN 200810056398 A CN200810056398 A CN 200810056398A CN 101298039 B CN101298039 B CN 101298039B
Authority
CN
China
Prior art keywords
chitosan
pfos
adsorbent
solution
preparation
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Expired - Fee Related
Application number
CN2008100563985A
Other languages
Chinese (zh)
Other versions
CN101298039A (en
Inventor
邓述波
余强
余刚
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Tsinghua University
Original Assignee
Tsinghua University
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Tsinghua University filed Critical Tsinghua University
Priority to CN2008100563985A priority Critical patent/CN101298039B/en
Publication of CN101298039A publication Critical patent/CN101298039A/en
Application granted granted Critical
Publication of CN101298039B publication Critical patent/CN101298039B/en
Expired - Fee Related legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Images

Landscapes

  • Solid-Sorbent Or Filter-Aiding Compositions (AREA)
  • Polysaccharides And Polysaccharide Derivatives (AREA)

Abstract

The invention provides a preparation method for a print adsorbent of chitosan molecules, which relates to a preparation method for an adsorbent that can selectively remove perfluorooctane sulfonate (PFOS) in water. The preparation method adopts a molecular imprinting technique to construct a plurality of specific adsorption sites and the worthy adsorbent has remarkable selectivity adsorption to the PFOS in water. The method takes chitosan as raw material to prepare micro-cross linking chitosan beads; then the chitosan beads are printed with template molecules PFOS for 5 to 24 hours in an acid water solution, a mass ratio between the template molecules and the micro-cross linking chitosan beads is 0.005 to 0.06: 1, and reaction with a cross linker is carried out for 2 to12 hours after printing; the mass ratio between the volume of the cross linker and the micro-cross linking chitosan beads after being printed is 0.0125 to 0.119ml/g; finally, an organic solvent is used for eluting for 1 to 8 hours and the print adsorbent of chitosan molecules is obtained after freeze-drying. The adsorbent is suitable for adsorbing and removing PFOS in complicated water substances and is characterized by strong selectivity and being able to be reused.

Description

一种壳聚糖分子印迹吸附剂的制备方法 A kind of preparation method of chitosan molecularly imprinted adsorbent

技术领域technical field

本发明涉及一种壳聚糖分子印迹吸附剂的制备方法,该方法所制备的吸附剂能够在复杂的水体中选择性地吸附去除水体中全氟辛烷磺酸基化合物(PFOS),属于水处理吸附技术领域。The invention relates to a preparation method of a chitosan molecularly imprinted adsorbent. The adsorbent prepared by the method can selectively adsorb and remove perfluorooctane sulfonate (PFOS) in complex water bodies, and belongs to water Dealing with the field of adsorption technology.

背景技术Background technique

全氟辛烷磺酸基化合物(PFOS)是一类重要的全氟化合物,作为表面活性剂、防污剂、灭火泡沫和化学中间体等在诸多领域都有着广泛的应用。同时,PFOS也是多种全氟化合物的最终降解产物。近年来,越来越多的研究人员对PFOS的难降解性、生物蓄积性、内分泌干扰性、毒性以及全球分布状况进行了研究和报道。作为一种新的持续性有机污染物(POPs)的候选物质,PFOS在水中最大溶解度高达570mg/L,这使得它们相对于别的POPs物质对人体和环境具有更大的潜在危害。因此,研究出适当的技术来有效地去除水体中的PFOS就显得尤为重要。Perfluorooctane sulfonate (PFOS) is an important class of perfluorinated compounds, which are widely used in many fields as surfactants, antifouling agents, fire extinguishing foams and chemical intermediates. At the same time, PFOS is also the final degradation product of various perfluorinated compounds. In recent years, more and more researchers have studied and reported on the refractory, bioaccumulation, endocrine disrupting, toxicity and global distribution of PFOS. As a new candidate for persistent organic pollutants (POPs), PFOS has a maximum solubility of 570 mg/L in water, which makes them more potentially harmful to humans and the environment than other POPs. Therefore, it is particularly important to develop appropriate technology to effectively remove PFOS in water.

目前来说,仅有少数的几种方法报道了对PFOS的去除,包括超声降解(EnvironmentalScience and Technology,2005,39,3388-3392)、亚临界水中的零价铁还原(EnvironmentalScience and Technology,2006,40,1049-1054)、反渗透膜(Environmental Science and Technology,2006,40,7343-7349)和活性炭吸附(Organohalogen Compounds,2007,69,2820-2823)等。以上几种方法,除了存在价格昂贵、反应条件要求高或再生困难等缺点之外,它们也并不具有选择性去除PFOS的能力。然而,无论是在自然界天然水体中,还是在半导体、电镀等工业原水中,与PFOS同时存在于水体中的还有很多其他污染物质,它们会大大降低传统技术对于PFOS的去除效果。因此,选择性对于复杂水体中的PFOS去除有着至关重要的作用。At present, only a few methods have been reported for the removal of PFOS, including sonication (EnvironmentalScience and Technology, 2005, 39, 3388-3392), reduction of zero-valent iron in subcritical water (EnvironmentalScience and Technology, 2006, 40, 1049-1054), reverse osmosis membrane (Environmental Science and Technology, 2006, 40, 7343-7349) and activated carbon adsorption (Organohalogen Compounds, 2007, 69, 2820-2823), etc. In addition to the shortcomings of the above methods, such as high price, high requirements for reaction conditions, or difficult regeneration, they do not have the ability to selectively remove PFOS. However, whether it is in natural water bodies or in industrial raw water such as semiconductors and electroplating, there are many other pollutants that exist in water bodies at the same time as PFOS, which will greatly reduce the removal effect of traditional technologies on PFOS. Therefore, selectivity plays a crucial role in the removal of PFOS in complex water bodies.

分子印迹技术是指通过模板与单体间相互作用、交联、聚合以及模板分子的洗脱等步骤,最终制得一种能够在空间结构和吸附位点上对目标物进行识别的聚合物。通过分子印迹的方法制得的吸附剂,其最大的特点在于对目标物有着很高的吸附选择性。常规的吸附剂虽然对PFOS也有一定的吸附效果,但是在复杂的水体中,由于其它污染物质的干扰,其吸附效果往往会大大降低,而分子印迹吸附剂则正好可以弥补常规吸附剂的不足,可以选择性地去除水体中的PFOS。Molecular imprinting technology refers to the steps of interaction between template and monomer, cross-linking, polymerization, and elution of template molecules to finally prepare a polymer that can recognize the target in the spatial structure and adsorption site. The biggest feature of the adsorbent prepared by molecular imprinting method is that it has a high adsorption selectivity for the target substance. Although conventional adsorbents also have a certain adsorption effect on PFOS, in complex water bodies, due to the interference of other pollutants, their adsorption effect is often greatly reduced, and molecularly imprinted adsorbents can just make up for the shortcomings of conventional adsorbents. It can selectively remove PFOS in water.

壳聚糖是甲壳素脱去N-乙酰基后的产物,一般来说,脱去55%以上N-乙酰基的甲壳素即可称为壳聚糖。壳聚糖生产原料来源广泛,具有良好的生物相容性、无毒害性和生物可降解性。此外,壳聚糖同时含有羟基和氨基等多种官能团,可以很方便地进行交联、接枝等修饰,使其成为一种重要的环境友好功能材料。利用壳聚糖溶于稀酸而不溶于碱的特点,可以将壳聚糖溶于低浓度的醋酸、盐酸等溶液中,再将其滴入到碱性溶液中就可以得到水凝胶状的壳聚糖小球(Industrial and Engineering Chemistry Research,1998,37,1454-1463)。目前,这种材料在污染物去除、酶的固定化以及催化剂载体等领域已经有了一定的应用。(尽管如此,我们还没有发现有文献利用壳聚糖小球直接作为功能体来进行分子印迹吸附剂的制备,而本发明则利用壳聚糖小球作为原料,成功地利用分步交联的方法制备出了一种能选择性有效去除水中PFOS的分子印迹吸附剂)。Chitosan is the product of the removal of N-acetyl groups from chitin. Generally speaking, chitin with more than 55% of N-acetyl groups removed can be called chitosan. Chitosan has a wide range of raw materials for production, and has good biocompatibility, non-toxicity and biodegradability. In addition, chitosan contains a variety of functional groups such as hydroxyl and amino groups, which can be easily modified by cross-linking and grafting, making it an important environmentally friendly functional material. Utilizing the characteristic that chitosan is soluble in dilute acid but not in alkali, chitosan can be dissolved in low-concentration acetic acid, hydrochloric acid and other solutions, and then dropped into alkaline solution to obtain a hydrogel Chitosan pellets (Industrial and Engineering Chemistry Research, 1998, 37, 1454-1463). At present, this material has been applied in the fields of pollutant removal, enzyme immobilization and catalyst carrier. (In spite of this, we have not found that there are documents that use chitosan beads directly as functional bodies to prepare molecularly imprinted adsorbents, while the present invention utilizes chitosan beads as raw materials and successfully utilizes step-by-step cross-linked Methods A molecularly imprinted adsorbent capable of selectively and effectively removing PFOS from water was prepared.

发明内容Contents of the invention

本发明的目的是提供一种针对复杂水体中PFOS去除的壳聚糖分子印迹吸附剂的制备方法,通过模板分子和功能聚合物的相互作用、交联和洗脱,在壳聚糖小球上构造出大量的特异性吸附位点,从而使所制得的吸附剂对于PFOS有优良的吸附选择性。The purpose of the present invention is to provide a preparation method of chitosan molecularly imprinted adsorbent for removal of PFOS in complex water bodies, through the interaction, cross-linking and elution of template molecules and functional polymers, on chitosan beads A large number of specific adsorption sites are constructed, so that the prepared adsorbent has excellent adsorption selectivity for PFOS.

本发明的技术方案如下:Technical scheme of the present invention is as follows:

一种壳聚糖分子印迹吸附剂的制备方法,其特征在于该方法按如下步骤进行:A preparation method of chitosan molecularly imprinted adsorbent is characterized in that the method is carried out as follows:

1)将壳聚糖溶于稀酸中制得壳聚糖溶液,随后滴入到碱性溶液中造粒得到凝胶状的壳聚糖小球,在40~60℃下与环氧氯丙烷反应2~12h,所加环氧氯丙烷的体积与壳聚糖小球的质量之比为0.0125~0.0278ml/g,最后将微交联的壳聚糖小球洗净并存放在去离子水中备用;1) Dissolve chitosan in dilute acid to prepare chitosan solution, then drop into alkaline solution to granulate to obtain gelatinous chitosan pellets, mix with epichlorohydrin at 40-60°C React for 2-12 hours, the ratio of the volume of epichlorohydrin added to the mass of chitosan pellets is 0.0125-0.0278ml/g, and finally wash the micro-crosslinked chitosan pellets and store them in deionized water spare;

2)将微交联的壳聚糖小球加入到含有模板分子PFOS的酸性溶液中印迹5~24h,所加模板分子PFOS与微交联壳聚糖小球的质量比为0.005∶1~0.06∶1,溶液pH值始终保持在2~4;印迹结束后在40~60℃下与交联剂反应2~12h,所加交联剂的体积与印迹后的微交联壳聚糖小球的质量之比为0.0125~0.119ml/g;2) Add the micro-crosslinked chitosan beads to the acidic solution containing the template molecule PFOS for imprinting for 5-24 hours, the mass ratio of the added template molecule PFOS to the micro-crosslinked chitosan beads is 0.005:1-0.06 : 1, the pH value of the solution is always maintained at 2 to 4; after the blotting, react with the cross-linking agent at 40-60°C for 2-12 hours, the volume of the added cross-linking agent is the same as that of the micro-cross-linked chitosan beads after blotting The mass ratio is 0.0125~0.119ml/g;

3)将步骤2)得到的壳聚糖小球用洗脱液洗脱1~8h去除模板分子,再用去离子水反复冲洗,最后冷冻干燥至恒重,制得壳聚糖分子印迹吸附剂。3) Elute the chitosan beads obtained in step 2) with an eluent for 1 to 8 hours to remove template molecules, then repeatedly rinse with deionized water, and finally freeze-dry to constant weight to prepare chitosan molecularly imprinted adsorbent .

本发明所用的交联剂为环氧氯丙烷或戊二醛;模板分子全氟辛烷磺酸基化合物为全氟辛烷磺酸、全氟辛烷磺酸钾或全氟辛烷磺酸钠;洗脱液为丙酮/碱混合溶液、甲醇/碱混合溶液及其他对PFOS有良好溶解性的有机溶剂与碱的混合溶液。The crosslinking agent used in the present invention is epichlorohydrin or glutaraldehyde; the template molecule perfluorooctane sulfonate compound is perfluorooctane sulfonic acid, potassium perfluorooctane sulfonate or sodium perfluorooctane sulfonate ; The eluent is a mixed solution of acetone/alkali, methanol/alkali and other organic solvents with good solubility to PFOS and a mixed solution of alkali.

本发明与现有技术相比,具有以下优点及突出性效果:Compared with the prior art, the present invention has the following advantages and outstanding effects:

传统的分子印迹技术中,模板分子与单体的相互作用、聚合反应以及交联反应通常是同时进行的,大多数情况下所形成的大块聚合物还需要经过反复的研磨和筛分才能得到所需的分子印迹吸附剂,而研磨、筛分的过程则往往费时费力。本发明采用了一种天然高分子聚合物-壳聚糖作为功能体,利用其溶于酸而不溶于碱的特性制得壳聚糖小球直接用于印迹,成功地避免最后的研磨,是一种非常简便易行的分子印迹吸附剂制备方法。In traditional molecular imprinting technology, the interaction between template molecules and monomers, polymerization reaction and cross-linking reaction are usually carried out simultaneously, and in most cases the formed bulk polymer needs repeated grinding and sieving to obtain Molecularly imprinted adsorbents are required, and the process of grinding and sieving is often time-consuming and laborious. The present invention adopts a kind of natural macromolecular polymer-chitosan as the functional body, utilizes its property of being soluble in acid but not soluble in alkali to prepare chitosan pellets directly for imprinting, successfully avoiding final grinding, is A very simple and easy preparation method for molecularly imprinted adsorbent.

目前,文献报道过的几种PFOS去除技术对PFOS都没有专一性。在复杂水体中,它们并不能有效去除PFOS,而本发明所制得的壳聚糖分子印迹吸附剂则能够提供很好的选择性。在选择性吸附实验中,本发明利用此吸附剂在相同吸附条件下分别吸附等摩尔浓度的各种污染物。结果显示,壳聚糖分子印迹吸附剂对于PFOS的去除率达47.9%,而对于常见污染物2,4-二氯苯氧乙酸、全氟辛酸、十二烷基苯磺酸钠、五氯酚钠和苯酚的去除率则分别为4.7%、4.2%、17.0%、11.5%和5.1%,这充分说明了本发明所制得的吸附剂对于PFOS有着良好的吸附专一性和选择性。在再生实验中,通过丙酮/氢氧化钠混合溶液很容易地将PFOS洗掉,连续使用五次后,壳聚糖分子印迹吸附剂的吸附性能几乎没有下降。At present, several PFOS removal technologies reported in the literature are not specific for PFOS. In complex water bodies, they cannot effectively remove PFOS, but the chitosan molecularly imprinted adsorbent prepared by the present invention can provide good selectivity. In the selective adsorption experiment, the present invention utilizes the adsorbent to respectively adsorb various pollutants with equimolar concentration under the same adsorption condition. The results showed that the chitosan molecularly imprinted adsorbent had a removal rate of 47.9% for PFOS, while for the common pollutants 2,4-dichlorophenoxyacetic acid, perfluorooctanoic acid, sodium dodecylbenzenesulfonate, sodium pentachlorophenate and The removal rates of phenol are respectively 4.7%, 4.2%, 17.0%, 11.5% and 5.1%, which fully demonstrates that the adsorbent prepared by the present invention has good adsorption specificity and selectivity for PFOS. In the regeneration experiment, PFOS was easily washed off by the acetone/sodium hydroxide mixed solution, and the adsorption performance of the chitosan molecularly imprinted adsorbent hardly decreased after five consecutive uses.

综上所述,本发明的突出优点在于制备方法简便易行,所制备的壳聚糖分子印迹吸附剂对目标污染物具有高效的选择性和良好的再生性能。In summary, the outstanding advantages of the present invention are that the preparation method is simple and easy, and the prepared chitosan molecularly imprinted adsorbent has high selectivity to target pollutants and good regeneration performance.

附图说明Description of drawings

图1壳聚糖分子印迹吸附剂(MIP)与非印迹吸附剂(NIP)对水溶液中不同污染物的去除率。Fig. 1 Removal rate of different pollutants in aqueous solution by chitosan molecularly imprinted adsorbent (MIP) and non-imprinted adsorbent (NIP).

具体实施方式Detailed ways

本发明中,通过交联-印迹-再交联的多步反应来制备所需吸附剂。第一步交联反应的作用在于对壳聚糖小球进行轻微交联,赋予其不溶于酸的特性。在随后的印迹反应中,微交联的壳聚糖小球的氨基在酸性溶液中充分质子化,模板分子通过静电作用被吸附到氨基上。再次交联时,足量的交联剂可以使壳聚糖分子充分交联,从而将聚合物的空间结构固定下来。在最后的洗脱中,碱性溶液可以比较容易地使壳聚糖的氨基去质子化,从而使模板分子从壳聚糖上被洗脱出来,而甲醇、丙酮等对PFOS有良好溶解性的有机溶剂则可以增加洗脱效果。由于充分交联的缘故,洗脱后聚合物的空间结构仍然得以保持,模板分子脱去后所留下的空穴就对目标分子有了记忆性和识别作用,成为分子印迹吸附剂中的有效识别位点。In the present invention, the desired adsorbent is prepared through a multi-step reaction of crosslinking-imprinting-recrosslinking. The role of the first cross-linking reaction is to slightly cross-link the chitosan pellets, giving them the property of being insoluble in acids. In the subsequent imprinting reaction, the amino groups of the micro-crosslinked chitosan beads were fully protonated in the acidic solution, and the template molecules were adsorbed to the amino groups by electrostatic interaction. When cross-linking again, a sufficient amount of cross-linking agent can fully cross-link chitosan molecules, thereby fixing the spatial structure of the polymer. In the final elution, the alkaline solution can easily deprotonate the amino group of chitosan, so that the template molecule is eluted from chitosan, while methanol, acetone, etc. have good solubility for PFOS Organic solvents can increase the elution effect. Due to the sufficient cross-linking, the spatial structure of the polymer is still maintained after elution, and the cavities left after the removal of the template molecules have memory and recognition functions for the target molecules, and become effective molecularly imprinted adsorbents. recognition site.

本发明的具体制备方法如下:Concrete preparation method of the present invention is as follows:

1)将壳聚糖溶于稀酸中制得壳聚糖溶液,随后滴入到碱性溶液中造粒得到凝胶状的壳聚糖小球,在40~60℃下与环氧氯丙烷微交联反应2~12h,所加环氧氯丙烷的体积与壳聚糖小球的质量之比为0.0125~00278ml/g,最后将微交联的壳聚糖小球洗净并存放在去离子水中备用;1) Dissolve chitosan in dilute acid to prepare chitosan solution, then drop into alkaline solution to granulate to obtain gelatinous chitosan pellets, mix with epichlorohydrin at 40-60°C Micro-crosslinking reaction for 2-12 hours, the ratio of the volume of epichlorohydrin added to the mass of chitosan pellets is 0.0125-00278ml/g, and finally the micro-crosslinked chitosan pellets are washed and stored in a Deionized water for standby;

2)将微交联的壳聚糖小球加入到含有模板分子PFOS的酸性溶液中印迹5~24h,所加模板分子PFOS与微交联壳聚糖小球的质量比为0.005∶1~0.06∶1,溶液pH值始终保持在2~4;印迹结束后在40~60℃下与交联剂反应2~12h,所加交联剂的体积与印迹后的微交联壳聚糖小球的质量之比为0.0125~0.119ml/g,所用的交联剂为环氧氯丙烷或戊二醛;2) Add the micro-crosslinked chitosan beads to the acidic solution containing the template molecule PFOS for imprinting for 5-24 hours, the mass ratio of the added template molecule PFOS to the micro-crosslinked chitosan beads is 0.005:1-0.06 : 1, the pH value of the solution is always maintained at 2 to 4; after the blotting, react with the cross-linking agent at 40-60°C for 2-12 hours, the volume of the added cross-linking agent is the same as that of the micro-cross-linked chitosan beads after blotting The mass ratio is 0.0125~0.119ml/g, and the crosslinking agent used is epichlorohydrin or glutaraldehyde;

3)将步骤2)得到的壳聚糖小球用洗脱液洗脱1~8h去除模板分子,再用去离子水反复冲洗,最后冷冻干燥至恒重,制得壳聚糖分子印迹吸附剂;洗脱液可采用丙酮/碱混合溶液、甲醇/碱混合溶液及其他对PFOS有良好溶解性的有机溶剂与碱的混合溶液。3) Elute the chitosan beads obtained in step 2) with an eluent for 1 to 8 hours to remove template molecules, then repeatedly rinse with deionized water, and finally freeze-dry to constant weight to prepare chitosan molecularly imprinted adsorbent ; The eluent can be a mixed solution of acetone/alkali, methanol/alkali and other organic solvents with good solubility to PFOS and a mixed solution of alkali.

本发明对于壳聚糖分子印迹吸附剂的评价方法主要通过与非印迹吸附剂的PFOS吸附量进行比较。非印迹吸附剂在制备中没有加入模板分子,其他制备方法与分子印迹吸附剂完全一样。The evaluation method of the chitosan molecularly imprinted adsorbent in the present invention mainly compares with the PFOS adsorption capacity of the non-imprinted adsorbent. Non-imprinted adsorbents do not add template molecules in the preparation, and other preparation methods are exactly the same as molecularly imprinted adsorbents.

本发明测定吸附剂对PFOS吸附量的实验方法如下:在250mL三角瓶中加入一定量的PFOS溶液,调整溶液初始pH,然后加入吸附剂,加瓶塞后将三角瓶放在25℃的恒温摇床中以130rpm的转速吸附36h(已到达吸附平衡),然后用0.22μm的膜过滤,测定滤液中剩余PFOS的含量,用下式计算吸附剂对污染物的去除率:The present invention measures adsorbent to the experimental method of PFOS adsorption capacity as follows: add a certain amount of PFOS solution in 250mL conical flask, adjust initial pH of solution, then add adsorbent, after adding bottle stopper, triangular flask is placed on 25 ℃ constant temperature shaking Adsorb in the bed at a speed of 130rpm for 36h (adsorption equilibrium has been reached), then filter with a 0.22μm membrane, measure the remaining PFOS content in the filtrate, and use the following formula to calculate the removal rate of pollutants by the adsorbent:

R=(C0-Ce)/C0×100%R=(C 0 -C e )/C 0 ×100%

其中:R为去除率(%);C0为污染物的初始浓度(mg/L);Ce为吸附后PFOS的平衡浓度(mg/L)。Among them: R is the removal rate (%); C 0 is the initial concentration of pollutants (mg/L); C e is the equilibrium concentration of PFOS after adsorption (mg/L).

实施例1:将1.5g壳聚糖溶于50ml的醋酸溶液中(体积百分比2%),待完全溶解后滴入到200ml的氢氧化钠(0.5M)溶液中造粒,得到的壳聚糖小球约为36g,在60℃下与1ml环氧氯丙烷反应12h后洗净并存放在去离子水中备用。取9g微交联壳聚糖小球加入到500mL全氟辛烷磺酸钾的酸性水溶液(400mg/L)中印迹5h,溶液pH值始终保持在4左右。印迹结束后将壳聚糖小球加入环氧氯丙烷溶液中在60℃下反应12h,环氧氯丙烷溶液含有0.3mL环氧氯丙烷和10ml去离子水。随后以甲醇/0.5M氢氧化钾溶液洗脱1h以去除模板分子,最后用去离子水反复冲洗,冷冻干燥至恒重,得到壳聚糖分子印迹吸附剂。非印迹吸附剂以同样方法制备,但是没有加入模板分子。将0.05g印迹和非印迹吸附剂放入250mL三角瓶中,再加入100mL浓度为200mg/L的PFOS溶液(pH=5),在转速为130rpm的摇床中吸附36h(达到平衡)。计算得到印迹吸附剂对PFOS的去除率为62%,非印迹吸附剂对PFOS的去除率则为52%。Embodiment 1: 1.5g chitosan is dissolved in the acetic acid solution of 50ml (volume percentage 2%), after treating to dissolve completely, drop in the sodium hydroxide (0.5M) solution of 200ml and granulate, the chitosan obtained The pellet is about 36g, washed with 1ml epichlorohydrin at 60°C for 12h, and stored in deionized water for later use. Take 9g of micro-crosslinked chitosan beads and add them to 500mL of perfluorooctane potassium sulfonate acidic aqueous solution (400mg/L) for blotting for 5h, and the pH value of the solution is always kept at about 4. After the blotting, the chitosan pellets were added into the epichlorohydrin solution and reacted at 60° C. for 12 h. The epichlorohydrin solution contained 0.3 mL of epichlorohydrin and 10 ml of deionized water. Then, it was eluted with methanol/0.5M potassium hydroxide solution for 1 h to remove template molecules, and finally washed repeatedly with deionized water, and freeze-dried to constant weight to obtain chitosan molecularly imprinted adsorbent. Non-imprinted sorbents were prepared in the same way, but without the addition of template molecules. Put 0.05g of imprinted and non-imprinted adsorbents into a 250mL Erlenmeyer flask, then add 100mL of PFOS solution (pH=5) with a concentration of 200mg/L, and adsorb on a shaker at 130rpm for 36h (to reach equilibrium). The calculated removal rate of PFOS by imprinted adsorbent was 62%, and that of non-imprinted adsorbent was 52%.

实施例2:将3g壳聚糖溶于100ml的醋酸溶液中(体积百分比2%),待完全溶解后滴入到400ml的氢氧化钠(0.5M)溶液中造粒,得到的壳聚糖小球约为72g,在40℃下与0.9ml环氧氯丙烷反应2h后洗净并存放在去离子水中备用。取4g微交联的壳聚糖小球加入到125mL全氟辛烷磺酸钾的酸性水溶液(400mg/L)中印迹5h,溶液pH值始终保持在4左右。印迹结束后将壳聚糖小球加入环氧氯丙烷溶液中在60℃下反应5h,环氧氯丙烷溶液含有0.15mL环氧氯丙烷和10ml去离子水。随后以丙酮/0.5M氢氧化钠溶液洗脱3h以去除模板分子,最后用去离子水反复冲洗,冷冻干燥至恒重,得到壳聚糖分子印迹吸附剂。非印迹吸附剂以同样方法制备,但是没有加入模板分子。将0.05g印迹和非印迹吸附剂放入250mL三角瓶中,再加入100mL浓度为200mg/L的PFOS溶液(pH=5),在转速为130rpm的摇床中吸附36h(达到平衡)。计算得到印迹吸附剂对PFOS的去除率为60%,非印迹吸附剂对PFOS的去除率则为42%。Embodiment 2: 3g chitosan is dissolved in the acetic acid solution of 100ml (volume percentage 2%), after treating to dissolve completely, drop in the sodium hydroxide (0.5M) solution of 400ml and granulate, the chitosan obtained is small The ball is about 72g. After reacting with 0.9ml epichlorohydrin at 40°C for 2h, it is washed and stored in deionized water for later use. Take 4g of micro-crosslinked chitosan pellets and add them to 125mL of potassium perfluorooctane sulfonate in an acidic aqueous solution (400mg/L) for blotting for 5h, and the pH value of the solution is always kept at around 4. After the blotting, the chitosan pellets were added into the epichlorohydrin solution and reacted at 60° C. for 5 h. The epichlorohydrin solution contained 0.15 mL of epichlorohydrin and 10 ml of deionized water. Then, it was eluted with acetone/0.5M sodium hydroxide solution for 3 hours to remove the template molecules, and finally washed repeatedly with deionized water, and freeze-dried to constant weight to obtain chitosan molecularly imprinted adsorbent. Non-imprinted sorbents were prepared in the same way, but without the addition of template molecules. Put 0.05g of imprinted and non-imprinted adsorbents into a 250mL Erlenmeyer flask, then add 100mL of PFOS solution (pH=5) with a concentration of 200mg/L, and adsorb on a shaker at 130rpm for 36h (to reach equilibrium). The calculated removal rate of PFOS by imprinted adsorbent was 60%, and that of non-imprinted adsorbent was 42%.

实施例3:将3g壳聚糖溶于100ml的醋酸溶液中(体积百分比2%),待完全溶解后滴入到500ml的氢氧化钠(0.5M)溶液中造粒,得到的壳聚糖小球约为72g,在40℃下与2ml环氧氯丙烷反应12h后洗净并存放在去离子水中备用。取3.36g微交联的壳聚糖小球加入到125mL全氟辛烷磺酸的酸性水溶液(500mg/L)中印迹13.5h,溶液pH值始终保持在4左右。印迹结束后将壳聚糖小球加入环氧氯丙烷溶液中在40℃下反应12h,环氧氯丙烷溶液含有0.4mL环氧氯丙烷和10ml去离子水。随后以甲醇/0.5M氢氧化钠溶液洗脱3h以去除模板分子,最后用去离子水反复冲洗,冷冻干燥至恒重,得到壳聚糖分子印迹吸附剂。非印迹吸附剂以同样方法制备,但是没有加入模板分子。将0.05g印迹和非印迹吸附剂放入250mL三角瓶中,再加入100mL浓度为200mg/L的PFOS溶液(pH=5),在转速为130rpm的摇床中吸附36h(达到平衡)。计算得到印迹吸附剂对PFOS的去除率为50%,非印迹吸附剂对PFOS的去除率则为31%。Embodiment 3: 3g chitosan is dissolved in the acetic acid solution of 100ml (volume percentage 2%), after treating to dissolve completely, drop in the sodium hydroxide (0.5M) solution of 500ml and granulate, the chitosan obtained is small The ball is about 72g. After reacting with 2ml epichlorohydrin at 40°C for 12h, it is washed and stored in deionized water for later use. Take 3.36g of micro-crosslinked chitosan pellets and add them to 125mL of perfluorooctane sulfonate acidic aqueous solution (500mg/L) for imprinting for 13.5h, and the pH value of the solution is always maintained at about 4. After the blotting, the chitosan pellets were added into the epichlorohydrin solution and reacted at 40° C. for 12 h. The epichlorohydrin solution contained 0.4 mL of epichlorohydrin and 10 ml of deionized water. Then, it was eluted with methanol/0.5M sodium hydroxide solution for 3 hours to remove template molecules, and finally washed repeatedly with deionized water, and freeze-dried to constant weight to obtain chitosan molecularly imprinted adsorbent. Non-imprinted sorbents were prepared in the same way, but without the addition of template molecules. Put 0.05g of imprinted and non-imprinted adsorbents into a 250mL Erlenmeyer flask, then add 100mL of PFOS solution (pH=5) with a concentration of 200mg/L, and adsorb on a shaker at 130rpm for 36h (to reach equilibrium). The calculated removal rate of PFOS by imprinted adsorbent was 50%, and that of non-imprinted adsorbent was 31%.

实施例4:将3g壳聚糖溶于100ml的醋酸溶液中(体积百分比2%),待完全溶解后滴入到500ml的氢氧化钠(0.5M)溶液中造粒,得到的壳聚糖小球约为72g,在40℃下与2ml环氧氯丙烷反应12h后洗净并存放在去离子水中备用。取4g微交联的壳聚糖小球加入到50mL全氟辛烷磺酸钾的酸性水溶液(400mg/L)中印迹24h,溶液pH值始终保持在4左右。印迹结束后将壳聚糖小球加入环氧氯丙烷溶液中在40℃下反应12h,环氧氯丙烷溶液含有0.05mL环氧氯丙烷和10ml去离子水。随后以丙酮/0.5M氢氧化钠溶液交替洗脱8h以去除模板分子,最后用去离子水反复冲洗,冷冻干燥至恒重,得到壳聚糖分子印迹吸附剂。非印迹吸附剂以同样方法制备,但是没有加入模板分子。将0.05g印迹和非印迹吸附剂放入250mL三角瓶中,再加入100mL浓度为200mg/L的PFOS溶液(pH=5),在转速为130rpm的摇床中吸附36h(达到平衡)。计算得到印迹吸附剂对PFOS的去除率为62%,非印迹吸附剂对PFOS的去除率则为42%。Embodiment 4: 3g chitosan is dissolved in the acetic acid solution of 100ml (volume percentage 2%), after treating to dissolve completely, drop in the sodium hydroxide (0.5M) solution of 500ml and granulate, the chitosan obtained is small The ball is about 72g. After reacting with 2ml epichlorohydrin at 40°C for 12h, it is washed and stored in deionized water for later use. Take 4 g of micro-crosslinked chitosan pellets and add them to 50 mL of an acidic aqueous solution of potassium perfluorooctane sulfonate (400 mg/L) for blotting for 24 hours, and the pH of the solution is always maintained at around 4. After the blotting, the chitosan pellets were added into the epichlorohydrin solution and reacted at 40° C. for 12 h. The epichlorohydrin solution contained 0.05 mL of epichlorohydrin and 10 ml of deionized water. Then alternately eluted with acetone/0.5M sodium hydroxide solution for 8 hours to remove template molecules, and finally rinsed repeatedly with deionized water, and freeze-dried to constant weight to obtain chitosan molecularly imprinted adsorbent. Non-imprinted sorbents were prepared in the same way, but without the addition of template molecules. Put 0.05g of imprinted and non-imprinted adsorbents into a 250mL Erlenmeyer flask, then add 100mL of PFOS solution (pH=5) with a concentration of 200mg/L, and adsorb on a shaker at 130rpm for 36h (to reach equilibrium). The calculated removal rate of PFOS by imprinted adsorbent was 62%, and that of non-imprinted adsorbent was 42%.

实施例5:将3g壳聚糖溶于100ml的醋酸溶液中(体积百分比2%),待完全溶解后滴入到500ml的氢氧化钠(0.5M)溶液中造粒,得到的壳聚糖小球约为72g,在40℃下与2ml环氧氯丙烷反应12h后洗净并存放在去离子水中备用。取4g微交联的壳聚糖小球加入到500mL全氟辛烷磺酸钾的酸性水溶液(400mg/L)中印迹24h,溶液pH值始终保持在3左右。印迹结束后将壳聚糖小球加入戊二醛溶液中在40℃下反应12h,戊二醛溶液含有0.2mL戊二醛和10ml去离子水。随后以丙酮/0.5M氢氧化钠溶液洗脱8h以去除模板分子,最后用去离子水反复冲洗,冷冻干燥至恒重,得到壳聚糖分子印迹吸附剂。非印迹吸附剂以同样方法制备,但是没有加入模板分子。将0.05g印迹和非印迹吸附剂放入250mL三角瓶中,再加入100mL浓度为200mg/L的PFOS溶液(pH=5),在转速为130rpm的摇床中吸附36h(达到平衡)。计算得到印迹吸附剂对PFOS的去除率为55%,非印迹吸附剂对PFOS的去除率则为54%。Embodiment 5: 3g chitosan is dissolved in the acetic acid solution of 100ml (volume percentage 2%), after treating to dissolve completely, drop in the sodium hydroxide (0.5M) solution of 500ml and granulate, the chitosan obtained is small The ball is about 72g. After reacting with 2ml epichlorohydrin at 40°C for 12h, it is washed and stored in deionized water for later use. Take 4 g of micro-crosslinked chitosan beads and add them to 500 mL of perfluorooctane potassium sulfonate acidic aqueous solution (400 mg/L) for 24 hours, and the pH value of the solution is always maintained at about 3. After the blotting, the chitosan pellets were added into the glutaraldehyde solution and reacted at 40° C. for 12 h. The glutaraldehyde solution contained 0.2 mL of glutaraldehyde and 10 ml of deionized water. Then, it was eluted with acetone/0.5M sodium hydroxide solution for 8 hours to remove template molecules, and finally washed repeatedly with deionized water, and freeze-dried to constant weight to obtain chitosan molecularly imprinted adsorbent. Non-imprinted sorbents were prepared in the same way, but without the addition of template molecules. Put 0.05g of imprinted and non-imprinted adsorbents into a 250mL Erlenmeyer flask, then add 100mL of PFOS solution (pH=5) with a concentration of 200mg/L, and adsorb on a shaker at 130rpm for 36h (to reach equilibrium). The calculated removal rate of PFOS by imprinted adsorbent was 55%, and that of non-imprinted adsorbent was 54%.

实施例6:将3g壳聚糖溶于100ml的醋酸溶液中(体积百分比2%),待完全溶解后滴入到500ml的氢氧化钠(0.5M)溶液中造粒,得到的壳聚糖小球约为72g,在40℃下与2ml环氧反应12h后洗净并存放在去离子水中备用。取2g微交联的壳聚糖小球加入到250mL全氟辛烷磺酸钾的酸性水溶液(480mg/L)中印迹24h,溶液pH值始终保持在2左右。印迹结束后将壳聚糖小球加入环氧氯丙烷溶液中在40℃下反应12h,环氧氯丙烷溶液含有0.1mL环氧氯丙烷和5ml去离子水。随后以纯丙酮/0.5M氢氧化钠溶液洗脱8h以去除模板分子,最后用去离子水反复冲洗,冷冻干燥至恒重,得到壳聚糖分子印迹吸附剂。非印迹吸附剂以同样方法制备,但是没有加入模板分子。将0.05g印迹和非印迹吸附剂放入250mL三角瓶中,再加入100mL浓度为200mg/L的PFOS溶液(pH=5),在转速为130rpm的摇床中吸附36h(达到平衡)。计算得到印迹吸附剂对PFOS的去除率为75%,非印迹吸附剂对PFOS的去除率则为29%。Embodiment 6: 3g chitosan is dissolved in the acetic acid solution of 100ml (volume percentage 2%), after being completely dissolved, be dripped in the sodium hydroxide (0.5M) solution of 500ml to granulate, the chitosan obtained is small The ball is about 72g, washed and stored in deionized water after reacting with 2ml epoxy for 12h at 40°C. Take 2g of micro-crosslinked chitosan pellets and add them to 250mL acidic aqueous solution of potassium perfluorooctane sulfonate (480mg/L) for 24h, and the pH value of the solution is always kept at about 2. After the blotting, the chitosan pellets were added into the epichlorohydrin solution and reacted at 40° C. for 12 h. The epichlorohydrin solution contained 0.1 mL of epichlorohydrin and 5 ml of deionized water. Then, it was eluted with pure acetone/0.5M sodium hydroxide solution for 8 hours to remove template molecules, and finally washed repeatedly with deionized water, and freeze-dried to constant weight to obtain chitosan molecularly imprinted adsorbent. Non-imprinted sorbents were prepared in the same way, but without the addition of template molecules. Put 0.05g of imprinted and non-imprinted adsorbents into a 250mL Erlenmeyer flask, then add 100mL of PFOS solution (pH=5) with a concentration of 200mg/L, and adsorb on a shaker at 130rpm for 36h (to reach equilibrium). The calculated removal rate of PFOS by imprinted adsorbent was 75%, while that of non-imprinted adsorbent was 29%.

实施例7:将3g壳聚糖溶于100ml的醋酸溶液中(体积百分比2%),待完全溶解后滴入到500ml的氢氧化钠(0.5M)溶液中造粒,得到的壳聚糖小球约为72g,在40℃下与2ml交联剂反应12h后洗净并存放在去离子水中备用。取4g微交联壳聚糖小球加入到400mL全氟辛烷磺酸钾的酸性水溶液(450mg/L)中印迹12h,溶液pH值始终保持在2左右。印迹结束后将壳聚糖小球加入环氧氯丙烷溶液中在40℃下反应12h,环氧氯丙烷溶液含有0.2mL环氧氯丙烷和10ml去离子水。随后以丙酮/0.5M氢氧化钠溶液洗脱8h以去除模板分子,最后用去离子水反复冲洗,冷冻干燥至恒重,得到壳聚糖分子印迹吸附剂。非印迹吸附剂以同样方法制备,但是没有加入模板分子。Embodiment 7: 3g chitosan is dissolved in the acetic acid solution of 100ml (volume percentage 2%), after treating to dissolve completely, drop in the sodium hydroxide (0.5M) solution of 500ml and granulate, the chitosan obtained is small The ball is about 72g, washed and stored in deionized water after reacting with 2ml of cross-linking agent at 40°C for 12h. Take 4g of micro-crosslinked chitosan pellets and add them to 400mL of perfluorooctane potassium sulfonate acidic aqueous solution (450mg/L) for 12h, and the pH value of the solution is always kept at about 2. After the blotting, the chitosan pellets were added into the epichlorohydrin solution and reacted at 40° C. for 12 h. The epichlorohydrin solution contained 0.2 mL of epichlorohydrin and 10 ml of deionized water. Then, it was eluted with acetone/0.5M sodium hydroxide solution for 8 hours to remove template molecules, and finally washed repeatedly with deionized water, and freeze-dried to constant weight to obtain chitosan molecularly imprinted adsorbent. Non-imprinted sorbents were prepared in the same way, but without the addition of template molecules.

将实施例7所得到的印迹和非印迹吸附剂0.01g放入250mL三角瓶中,再加入100mL浓度为50mg/L的PFOS溶液(pH=5),在转速为130rpm的摇床中吸附36h(达到平衡)。吸附前后溶液中的PFOS浓度通过岛津高效液相色谱分离并用电导检测器进行测定。计算得到印迹吸附剂对PFOS的去除率为60%,非印迹吸附剂对PFOS的去除率则为28%。Put 0.01 g of imprinted and non-imprinted adsorbents obtained in Example 7 into a 250 mL Erlenmeyer flask, then add 100 mL of PFOS solution (pH=5) with a concentration of 50 mg/L, and adsorb in a shaker at 130 rpm for 36 h ( Achieve balance). The concentration of PFOS in the solution before and after adsorption was separated by Shimadzu high performance liquid chromatography and measured with a conductivity detector. The calculated removal rate of PFOS by imprinted adsorbent was 60%, and that of non-imprinted adsorbent was 28%.

将实施例7所得到的印迹吸附剂0.01g放入250mL三角瓶中,再分别加入100mL浓度为100μmol/L的PFOS、2,4-二氯苯氧乙酸、全氟辛酸、十二烷基苯磺酸钠、五氯酚钠或苯酚溶液(pH=6),在转速为130rpm的摇床中吸附36h(达到平衡)。计算得到印迹吸附剂对于PFOS的去除率达47.9%,而对于2,4-二氯苯氧乙酸(2,4-D)、全氟辛酸(PFOA)、十二烷基苯磺酸钠(SDBS)、五氯酚钠(PCP)和苯酚(Phenol)等其它常见污染物的去除率则分别为4.7%、4.2%、17.0%、11.5%和5.1%,远低于对PFOS的去除率(图1)。Put 0.01 g of the imprinted adsorbent obtained in Example 7 into a 250 mL Erlenmeyer flask, and then add 100 mL of PFOS, 2,4-dichlorophenoxyacetic acid, perfluorooctanoic acid, and dodecylbenzenesulfonic acid at a concentration of 100 μmol/L Sodium, sodium pentachlorophenate or phenol solution (pH = 6), adsorbed in a shaking table with a rotation speed of 130rpm for 36h (to reach equilibrium). The calculated removal rate of imprinted adsorbent for PFOS was 47.9%, while for 2,4-dichlorophenoxyacetic acid (2,4-D), perfluorooctanoic acid (PFOA), sodium dodecylbenzenesulfonate (SDBS), The removal rates of other common pollutants such as sodium pentachlorophenate (PCP) and phenol (Phenol) were 4.7%, 4.2%, 17.0%, 11.5% and 5.1%, respectively, far below the removal rate of PFOS (Fig. 1) .

Claims (3)

1. chitosan molecule trace preparation of adsorbent method is characterized in that this method carries out as follows:
1) shitosan is dissolved in makes chitosan solution in the diluted acid, splash into subsequently that granulation obtains gelatinous shitosan bead in the alkaline solution, at 40~60 ℃ of following and little cross-linking reaction 2~12h of epoxychloropropane, add epoxychloropropane the ratio of volume and the quality of shitosan bead be 0.0125~0.0278ml/g, at last little crosslinked shitosan bead is cleaned and is left in the deionized water standby;
2) little crosslinked shitosan bead is joined trace 5~24h in the acid solution that contains template molecule PFOS based compound, add template molecule PFOS based compound and little cross-linked chitosan bead mass ratio be 0.005: 1~0.06: 1, the pH value of solution value remains at 2~4; Trace finishes the back and reacts 2~12h with crosslinking agent down at 40~60 ℃, add crosslinking agent volume and trace after the ratio of quality of little cross-linked chitosan bead be 0.0125~0.119ml/g; Used crosslinking agent is epoxychloropropane or glutaraldehyde; Used template molecule PFOS based compound is PFOS, PFOS potassium or PFOS sodium;
3) with step 2) the shitosan bead that obtains removes template molecule with eluent wash-out 1~8h, washes repeatedly with deionized water again, and last freeze drying makes chitosan molecule trace adsorbent to constant weight.
2. chitosan molecule trace preparation of adsorbent method according to claim 1, it is characterized in that: used eluent is for to have the organic solvent of good solubility and the mixed solution of alkali to template molecule.
3. chitosan molecule trace preparation of adsorbent method according to claim 2 is characterized in that: described organic solvent adopts acetone or methyl alcohol.
CN2008100563985A 2008-01-18 2008-01-18 Preparation of chitosan molecular imprinting adsorbing agent Expired - Fee Related CN101298039B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN2008100563985A CN101298039B (en) 2008-01-18 2008-01-18 Preparation of chitosan molecular imprinting adsorbing agent

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN2008100563985A CN101298039B (en) 2008-01-18 2008-01-18 Preparation of chitosan molecular imprinting adsorbing agent

Publications (2)

Publication Number Publication Date
CN101298039A CN101298039A (en) 2008-11-05
CN101298039B true CN101298039B (en) 2010-06-23

Family

ID=40078069

Family Applications (1)

Application Number Title Priority Date Filing Date
CN2008100563985A Expired - Fee Related CN101298039B (en) 2008-01-18 2008-01-18 Preparation of chitosan molecular imprinting adsorbing agent

Country Status (1)

Country Link
CN (1) CN101298039B (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US12410071B1 (en) 2020-10-19 2025-09-09 Wm Intellectual Property Holdings, L.L.C. System and method for removal of PFAS and other emerging contaminant micro-constituents from landfill leachate and other impacted liquids

Families Citing this family (22)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101724097B (en) * 2009-12-14 2011-12-14 武汉理工大学 Chitosan and metal copper ion complex protein-imprinted polymer and preparation method thereof
US8877907B2 (en) 2010-06-07 2014-11-04 The Johns Hopkins University Molecularly imprinted polymers
CN102019213B (en) * 2010-11-30 2013-03-27 浙江工业大学 Method for preparing strongly-acid ion exchange medium
CN102516456B (en) * 2011-11-28 2014-04-09 江苏大学 Yeast surface atom transfer imprinted adsorbent, and preparation method and application thereof
CN102872832A (en) * 2012-09-28 2013-01-16 河海大学 Preparation method of titanium dioxide loaded chitosan molecular imprinting adsorbent
CN102951754A (en) * 2012-11-21 2013-03-06 中国科学院生态环境研究中心 Method for removing PFOS (Perfluorooctane sulfonate)-based compound from drinking water
CN103204955A (en) * 2013-04-06 2013-07-17 青岛农业大学 Modification of chitosan and chelation for heavy metal of chitosan
CN103506089A (en) * 2013-10-22 2014-01-15 四川大学 Urea adsorbent based on molecular imprinting technology and preparation method thereof
CN105001371B (en) * 2014-04-18 2017-03-29 南开大学 A kind of method that utilization molecular imprinting prepares PFOA sorbing materials
CN104069838A (en) * 2014-07-10 2014-10-01 南京理工大学 Magnetic polybenzimidazole molecular imprinted adsorbing agent, preparation and use thereof
CN105085765B (en) * 2015-06-24 2017-03-08 浙江农林大学 A preparation method of dimethyl phthalate molecularly imprinted microspheres
CN105601846B (en) * 2015-09-10 2018-01-12 河北科技师范学院 Chitosan surface molecule print club-shaped material
CN105080504B (en) * 2015-09-13 2017-08-04 衢州学院 A kind of fluoride ion surface imprinted polymer and its treatment method for fluorine-containing water
CN106220786B (en) * 2016-02-26 2018-03-09 中国环境科学研究院 The preparation method of typical perfluorochemical adsorbent in a kind of removal water environment
CN105903452B (en) * 2016-05-26 2018-10-23 东南大学 A kind of preparation method of aromatic sulphonic acid selective ion exchange resin
CN107907522B (en) * 2017-12-25 2020-01-21 东莞理工学院 Perfluorinated compound molecularly imprinted fluorescent probe and use method and application thereof
CN108854986A (en) * 2018-06-29 2018-11-23 成都纺织高等专科学校 A kind of epoxychloropropane modified chitosan and preparation method thereof for adsorbing heavy metal ion
CN112354524A (en) * 2020-11-16 2021-02-12 榆林学院 Molecularly imprinted chitosan/titanium dioxide composite hydrogel and application thereof in treating high-concentration phenolic wastewater
CN115196710A (en) * 2022-01-20 2022-10-18 中国科学院烟台海岸带研究所 Application of chitosan crosslinked product
CN116550302A (en) * 2023-05-31 2023-08-08 江苏大学 A kind of preparation method and application of chitosan imprinted sponge with high recognition selectivity
CN117599762A (en) * 2023-12-20 2024-02-27 云南省烟草质量监督检测站 Preparation method of nicotine molecularly imprinted composite material
CN119735715B (en) * 2025-03-04 2025-07-22 中国科学院烟台海岸带研究所 Cross-linked amino chitosan and preparation and application thereof

Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US6582971B1 (en) * 2000-08-21 2003-06-24 Lynntech, Inc. Imprinting large molecular weight compounds in polymer composites
US20050016923A1 (en) * 2003-07-22 2005-01-27 Kraft Foods Holdings, Inc. Molecular imprinting of solute on cellulose/silica composite, and products and uses thereof
CN1786120A (en) * 2005-11-22 2006-06-14 南京工业大学 Benzothiophene sulfur component molecularly imprinted solid phase extracting agent and preparation method thereof
CN1843598A (en) * 2006-03-20 2006-10-11 天津大学 Preparation Method of Molecularly Imprinted CS/TEOS Hybrid Membrane for Separation of Phenylalanine Isomers

Patent Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US6582971B1 (en) * 2000-08-21 2003-06-24 Lynntech, Inc. Imprinting large molecular weight compounds in polymer composites
US20050016923A1 (en) * 2003-07-22 2005-01-27 Kraft Foods Holdings, Inc. Molecular imprinting of solute on cellulose/silica composite, and products and uses thereof
CN1786120A (en) * 2005-11-22 2006-06-14 南京工业大学 Benzothiophene sulfur component molecularly imprinted solid phase extracting agent and preparation method thereof
CN1843598A (en) * 2006-03-20 2006-10-11 天津大学 Preparation Method of Molecularly Imprinted CS/TEOS Hybrid Membrane for Separation of Phenylalanine Isomers

Non-Patent Citations (6)

* Cited by examiner, † Cited by third party
Title
Bibiana M.Espinosa-Garcia et al..Molecularly Imprinted Chitosan-Genipin Hydrogelswith Recognition Capacity toward o-Xylene.Biomacromolecules 8.2007,(8),3355-3364.
Bibiana M.Espinosa-Garcia et al..Molecularly Imprinted Chitosan-Genipin Hydrogelswith Recognition Capacity toward o-Xylene.Biomacromolecules 8.2007,(8),3355-3364. *
JP特开2007-50333A 2007.03.01
T.Y.Guo et al..Adsorptive separation of hemoglobin by molecularlyimprinted chitosan beads.Biomaterials25.2004,255905-5912. *
马豫峰等.壳聚糖与牛清血蛋白分子印迹聚合物的制备与表征.高分子材料科学与工程23 2.2007,23(2),235-238.
马豫峰等.壳聚糖与牛清血蛋白分子印迹聚合物的制备与表征.高分子材料科学与工程23 2.2007,23(2),235-238. *

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US12410071B1 (en) 2020-10-19 2025-09-09 Wm Intellectual Property Holdings, L.L.C. System and method for removal of PFAS and other emerging contaminant micro-constituents from landfill leachate and other impacted liquids

Also Published As

Publication number Publication date
CN101298039A (en) 2008-11-05

Similar Documents

Publication Publication Date Title
CN101298039B (en) Preparation of chitosan molecular imprinting adsorbing agent
Rahangdale et al. Chitosan as a substrate for simultaneous surface imprinting of salicylic acid and cadmium
US8932983B1 (en) Chitosan based adsorbent
CN100509142C (en) Macroporous adsorption resin special for extracting cephalosporin C and preparation method thereof
US10508046B2 (en) Use and regeneration of an adsorbent to remove dyes from water
CN102872836B (en) A kind of cyclodextrin-immobilized polymer and its preparation method and application
CN106040194A (en) Chitosan magnetic composite spherule adsorbent with core-brush structure as well as preparation method and application thereof
CN107434852A (en) A kind of method of amino benzenes compounds in the super crosslinked resin and its adsorption recovery industrial wastewater of cyclo-dextrin-modified
CN101298040A (en) Mercapto-functionalized polyvinyl alcohol-gelatine composite crosslinked microsphere adsorbing agent and preparation thereof
CN102350316A (en) Preparation method of ultra-high crosslinking type adsorptive resin modified by N-methyl acetamido
CN110327901B (en) Preparation method of thiourea modified chitosan-based copper ion imprinted nano-fiber
CN107233871B (en) Chloromethyl polystyrene resin-immobilized 1-aminoethyl-3-methylimidazolium bromide solid-phase extractant and its preparation method and application
CN108816204A (en) A kind of preparation method of copper ion imprinted crosslinked chitosan microballoon
Liu et al. Efficient and rapid removal of typical phenolic compounds from water with biobased porous organic polymers
CN104927063A (en) Method for adsorbing and recycling phenolic compounds in industrial wastewater and method for manufacturing adsorption materials
CN103908955B (en) The preparation method of the superhigh cross-linking type polymeric adsorbent that a kind of acetamido is modified and application thereof
CN114014966B (en) An amide group modified ultra-high cross-linked adsorption resin and its preparation method and application
CN107081133B (en) Application of Porous Organic Matter as Antibiotic Adsorbent
Wang et al. Preparation of a multifunctional and multipurpose chitosan/cyclodextrin/MIL-68 (Al) foam column and examining its adsorption properties for anionic and cationic dyes and sulfonamides
CN105440208A (en) Preparation method and application of acephate molecularly imprinted polymer
CN105295059A (en) Immobilized cationized beta-cyclodextrin chloromethylated polystyrene polymer and method for adsorbing and recovering phenols in industrial wastewater
CN104549172A (en) Method for preparing sulfydryl-modified chitosan short hole microspheres
CN106111086B (en) A kind of absorption Pd2+Ionic polymeric sorbent of metal ion and preparation method thereof
CN115845809A (en) Tetraethylenepentamine modified chitosan gel ball and preparation method and application thereof
CN101775083B (en) Preparation method, using method for modified chitosan and application thereof

Legal Events

Date Code Title Description
C06 Publication
PB01 Publication
C10 Entry into substantive examination
SE01 Entry into force of request for substantive examination
C14 Grant of patent or utility model
GR01 Patent grant
CF01 Termination of patent right due to non-payment of annual fee

Granted publication date: 20100623

Termination date: 20150118

EXPY Termination of patent right or utility model