CN110368911A - A kind of preparation method of pyridine functional chitosan absorbent - Google Patents
A kind of preparation method of pyridine functional chitosan absorbent Download PDFInfo
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Abstract
本发明公开了一种吡啶功能化壳聚糖吸附剂的制备方法,包括以下步骤:S1:将5‑100 g/L质量浓度的聚乙烯亚胺、2.5‑100 g/L质量浓度的2‑氯甲基吡啶盐酸盐及10‑100 g/L质量浓度的碳酸钠溶解于体积浓度为5‑80%的乙醇的水溶液中。本发明的吡啶功能化壳聚糖吸附剂可应用于宽泛pH范围下的畜禽养殖废水中重金属和抗生素的同步去除等领域,解决协同吸附重金属及抗生素时,吸附量小和吸附速率慢,在工程上需要树脂量大,操作时间长,在强酸条件下吸附量小甚至不吸附等技术问题,经济效益和环境效益显著。The invention discloses a preparation method of a pyridine functionalized chitosan adsorbent, comprising the following steps: S1: mixing polyethyleneimine with a mass concentration of 5-100 g/L and 2-2-2 with a mass concentration of 2.5-100 g/L Chloromethylpyridine hydrochloride and sodium carbonate with a mass concentration of 10-100 g/L are dissolved in an aqueous solution of ethanol with a volume concentration of 5-80%. The pyridine functionalized chitosan adsorbent of the present invention can be applied to fields such as the simultaneous removal of heavy metals and antibiotics in livestock and poultry wastewater under a wide pH range, and solves the problem of small adsorption capacity and slow adsorption rate when synergistically adsorbing heavy metals and antibiotics. Engineering requires a large amount of resin, long operating time, small or even no adsorption under strong acid conditions and other technical problems, and the economic and environmental benefits are remarkable.
Description
技术领域technical field
本发明涉及改性树脂合成领域,尤其涉及一种吡啶功能化壳聚糖吸附剂的制备方法。The invention relates to the field of modified resin synthesis, in particular to a preparation method of a pyridine functionalized chitosan adsorbent.
背景技术Background technique
为能够促进动物生长、提高饲料效率和治疗控制疾病,兽用抗生素和微量的重金属元素在集约化畜禽养殖业中得到了广泛应用,随之产生的畜禽养殖业废水中存在的抗生素和微量重金属往往混合共存进入土壤、水体,均对环境和人体健康构成了巨大的潜在危害。常见的处理畜禽养殖废水的处理方法为生化法,但其中的重金属和抗生素难以去除。国内外针对重金属和抗生素复合污染物的去除方法有膜过滤法、催化氧化还原法、离子交换和吸附法、植物修复技术或组合工艺。基于物理化学吸附原理去除水体中污染物具有简单、快速、绿色等优势,是养殖废水重金属和抗生素复合污染物去除的优选技术。其中基于高效的生物质吸附剂的吸附法因其操作简便、高效可靠、可再生利用和环境友好性等优点而成为优选工艺。In order to promote animal growth, improve feed efficiency, and treat and control diseases, veterinary antibiotics and trace heavy metal elements have been widely used in intensive livestock and poultry farming. Heavy metals often mix and coexist in soil and water, which pose a huge potential hazard to the environment and human health. The common treatment method for livestock and poultry wastewater is biochemical method, but the heavy metals and antibiotics are difficult to remove. The removal methods for complex pollutants of heavy metals and antibiotics at home and abroad include membrane filtration method, catalytic redox method, ion exchange and adsorption method, phytoremediation technology or combined process. The removal of pollutants in water based on the principle of physical and chemical adsorption has the advantages of simplicity, speed, and greenness. It is the preferred technology for the removal of heavy metals and antibiotics in aquaculture wastewater. Among them, the adsorption method based on high-efficiency biomass adsorbent has become the preferred process because of its advantages of simple operation, high efficiency, reliability, recyclability and environmental friendliness.
生物质吸附剂具有生物降解性、原料可再生性和环境友好性等传统高分子材料所不具备的绿色特性,其主要通过物理-化学的方法,在水体中富集重金属离子和有机物,已到达分别去除水体中重金属离子和有机物的目的。如申请号为CN201811142664.6,申请公布日为2018年12月14日的专利申请文件公开了一种螯合吸附剂的制备方法,该吸附剂的制备方法步骤为:将壳聚糖溶解在酸性溶液中,然后与有机溶剂混合;加入乙二胺四乙酸二酐接枝单体(EDTAD),并在60~80℃、惰性气体保护下进行接枝聚合反应;反应结束后洗涤、烘干,得到壳聚糖接枝物。该发明的螯合吸附剂,具有良好的吸附性,接枝在壳聚糖上的EDTAD提供节点尤其能够牢牢螯合钙离子。可以通过洗脱法将吸附后的吸附剂回收金属离子,并且可持续使用;在尾矿坝的内部具有较好的稳定性。申请号为CN201810159080.3,申请公布日日为2018年7月31日的专利申请文件公开了用于四环素类抗生素吸附的改性海藻酸钠吸附材料及其制备方法,该吸附材料的制备方法步骤为:步骤一、将海藻酸钠和溶剂按质量体积比为1~3:97~99的比例混合搅拌均匀,使海藻酸钠充分溶胀,超声脱泡脱气,得到海藻酸钠溶胶;步骤二、将海藻酸钠溶胶匀速地滴入到质量浓度为1~10wt%金属盐溶液中,搅拌,交联反应2~24h,过滤,干燥,即得用于四环素类抗生素吸附的改性海藻酸钠吸附材料。该发明所得吸附剂原料价廉易得,吸附剂制备过程简单,对四环素类抗生素去除效率高,吸附剂使用后可生物降解,可再生,不会出现二次污染,具有良好的应用前景。文献Zhao, G.,Huang, X., Tang, Z. et al. Polymer-Based Nanocomposites for Heavy Metal IonsRemoval from Aqueous Solution: A Review[J]. Polym. Chem., 2018, 9(26): 3562-3582。以上专利或文献公开制备的生物质吸附剂的方法只能吸附单一的重金属或抗生素,不能同步去除重金属和抗生素,解决选择性及协同吸附重金属及抗生素的问题,这使得处理复合污染物水体中的重金属或抗生素受到限制。Biomass adsorbents have green characteristics that traditional polymer materials do not have, such as biodegradability, raw material renewability, and environmental friendliness. They mainly enrich heavy metal ions and organic substances in water bodies through physical-chemical methods. The purpose of removing heavy metal ions and organic matter in water respectively. For example, the application number is CN201811142664.6, and the patent application document published on December 14, 2018 discloses a preparation method of a chelating adsorbent. The preparation method of the adsorbent is as follows: dissolving chitosan in acidic solution, and then mixed with an organic solvent; add ethylenediaminetetraacetic acid dianhydride graft monomer (EDTAD), and carry out graft polymerization reaction at 60-80°C under the protection of an inert gas; after the reaction, wash and dry, A chitosan graft was obtained. The chelating adsorbent of the invention has good adsorption properties, and the EDTAD grafted on the chitosan provides nodes, especially capable of firmly chelating calcium ions. The adsorbent after adsorption can recover metal ions by elution method, and can be used continuously; it has good stability inside the tailings dam. The application number is CN201810159080.3, and the patent application document published on July 31, 2018 discloses a modified sodium alginate adsorption material and its preparation method for the adsorption of tetracycline antibiotics. The preparation method steps of the adsorption material Step 1: Mix and stir sodium alginate and solvent according to the mass volume ratio of 1-3:97-99 to make sodium alginate fully swell, degas and degas it by ultrasonic to obtain sodium alginate sol; step 2 1. Drop the sodium alginate sol into the metal salt solution with a mass concentration of 1-10wt% at a uniform speed, stir, cross-link for 2-24 hours, filter, and dry to obtain the modified sodium alginate used for the adsorption of tetracycline antibiotics Adsorbent material. The raw material of the adsorbent obtained by the invention is cheap and easy to obtain, the preparation process of the adsorbent is simple, the removal efficiency of tetracycline antibiotics is high, the adsorbent is biodegradable after use, can be regenerated, no secondary pollution occurs, and has good application prospects. Literature Zhao, G., Huang, X., Tang, Z. et al. Polymer-Based Nanocomposites for Heavy Metal IonsRemoval from Aqueous Solution: A Review[J]. Polym. Chem., 2018, 9(26): 3562- 3582. The method of biomass adsorbent disclosed in the above patents or documents can only adsorb single heavy metals or antibiotics, and cannot simultaneously remove heavy metals and antibiotics, and solve the problem of selective and synergistic adsorption of heavy metals and antibiotics, which makes it possible to treat complex pollutants in water bodies. Heavy metals or antibiotics are restricted.
针对现有生物质吸附剂在高酸高盐环境中对重金属吸附容量低、不能同步去除重金属和抗生素,解决选择性及协同吸附重金属及抗生素的问题,本发明提供一种吡啶功能化壳聚糖吸附剂的制备方法。In view of the low adsorption capacity of existing biomass adsorbents for heavy metals in high-acid and high-salt environments, and the inability to simultaneously remove heavy metals and antibiotics, to solve the problem of selective and synergistic adsorption of heavy metals and antibiotics, the present invention provides a pyridine functionalized chitosan Sorbent preparation method.
发明内容Contents of the invention
基于背景技术存在的技术问题,本发明提出了一种吡啶功能化壳聚糖吸附剂的制备方法。Based on the technical problems existing in the background technology, the present invention proposes a preparation method of a pyridine functionalized chitosan adsorbent.
本发明提出的一种吡啶功能化壳聚糖吸附剂的制备方法,包括以下步骤:A kind of preparation method of pyridine functionalized chitosan adsorbent proposed by the present invention comprises the following steps:
S1:将5-100 g/L质量浓度的聚乙烯亚胺、2.5-100 g/L质量浓度的2-氯甲基吡啶盐酸盐及10-100 g/L质量浓度的碳酸钠溶解于体积浓度为5-80%的乙醇的水溶液中,乙醇的水溶液的溶解温度设置为20-90 ℃,且乙醇的水溶液的溶解时间设置为2-10 h,同时利用85℃油浴中磁力进行搅拌直至搅拌均匀,然后利用冷却装置进行冷却操作,冷却装置首先以3-5℃/min的速率进行冷却,直到冷却到30℃,冷却装置再以0.3-0.5℃/min的速率进行冷却,直到冷却到至室温,再利用离心设备和过滤筛依次进行离心操作、过滤处理,最后经过1-60min的旋蒸后,得到油相;S1: Dissolve polyethyleneimine with a mass concentration of 5-100 g/L, 2-chloromethylpyridine hydrochloride with a mass concentration of 2.5-100 g/L and sodium carbonate with a mass concentration of 10-100 g/L in volume In the aqueous solution of ethanol with a concentration of 5-80%, the dissolving temperature of the aqueous ethanol solution is set at 20-90°C, and the dissolving time of the aqueous ethanol solution is set at 2-10 h, and at the same time, it is stirred by magnetic force in an oil bath at 85°C until Stir evenly, and then use the cooling device for cooling operation. The cooling device first cools at a rate of 3-5°C/min until it cools to 30°C, and then cools at a rate of 0.3-0.5°C/min until it cools down to to room temperature, then use centrifugal equipment and filter sieves to perform centrifugation and filtration in sequence, and finally undergo rotary evaporation for 1-60 minutes to obtain the oil phase;
S2:将2-50 g/L质量浓度的壳聚糖粉末溶解于体积浓度为1-8%的乙酸溶液中,乙酸溶液的溶解温度设置为20-80 ℃,且乙酸溶液的溶解时间设置为20-90 min,同时利用搅拌设备进行搅拌直至搅拌均匀,然后过滤设备从上至下依次利用多个筛网进行多级过滤,且从上至下的多个筛网的网孔逐次减小,最终得到壳聚糖母液;S2: Dissolving chitosan powder with a mass concentration of 2-50 g/L in an acetic acid solution with a volume concentration of 1-8%, the dissolution temperature of the acetic acid solution is set to 20-80 ° C, and the dissolution time of the acetic acid solution is set to 20-90 min, at the same time, use the stirring equipment to stir until it is evenly stirred, and then the filter equipment uses multiple screens from top to bottom to perform multi-stage filtration, and the meshes of the multiple screens from top to bottom are gradually reduced. Finally obtain chitosan mother liquor;
S3:将步骤S1中制备的油相逐滴加入至S2中制备的壳聚糖母液中,滴加时间设置为5-60 min,油相与壳聚糖母液的反应时间设置为1-60 h,在反应的过程中利用搅拌设备进行搅拌均匀,并用体积浓度为0.4-15%的环氧氯丙烷初交联,环氧氯丙烷初交联的交联温度设置为20-80℃,且交联时间设置为1-20 h,得到混合母液;S3: Add the oil phase prepared in step S1 dropwise to the chitosan mother liquor prepared in S2, the dropping time is set to 5-60 min, and the reaction time between the oil phase and the chitosan mother liquor is set to 1-60 h , in the process of the reaction, use stirring equipment to stir evenly, and use epichlorohydrin with a volume concentration of 0.4-15% for initial cross-linking. The coupling time is set to 1-20 h to obtain the mixed mother liquor;
S4:将S3中所得的混合母液加入凝固浴中,凝固浴为溶解有硫酸钠、氢氧化钠、三聚磷酸钠和焦磷酸钠中一种或几种的混合溶液,且凝固浴中的硫酸钠和氢氧化钠的质量浓度分别为10-200 g/L和10-200 g/L,经沉淀凝固得到复合微球;S4: Add the mixed mother liquor obtained in S3 into the coagulation bath, which is a mixed solution of one or more of sodium sulfate, sodium hydroxide, sodium tripolyphosphate and sodium pyrophosphate dissolved in it, and the sulfuric acid in the coagulation bath The mass concentrations of sodium and sodium hydroxide are 10-200 g/L and 10-200 g/L respectively, and composite microspheres are obtained through precipitation and solidification;
S5:将步骤S4中的2-40 g/L的复合微球经索氏抽提器进行2-10 h的抽提,去除树脂孔道中残留的致孔剂,依次用乙醇、蒸馏水洗涤,脱水后,取出复合微球投加到pH为10-14的氢氧化钠的水溶液中,用体积浓度为0.01-1%的环氧氯丙烷进行后交联,环氧氯丙烷交联的交联温度设置为20-80℃,且环氧氯丙烷交联的交联时间设置为1-10 h,制得交联微球,交联微球再利用用蒸馏水洗至中性,脱水保存备用得到吡啶功能化壳聚糖吸附剂。S5: Extract the 2-40 g/L composite microspheres in step S4 through a Soxhlet extractor for 2-10 h to remove the porogen remaining in the resin channels, wash with ethanol and distilled water in sequence, and dehydrate Finally, take out the composite microspheres and add them to an aqueous solution of sodium hydroxide with a pH of 10-14, and use epichlorohydrin with a volume concentration of 0.01-1% for post-crosslinking. The crosslinking temperature of epichlorohydrin crosslinking is Set it to 20-80°C, and set the cross-linking time of epichlorohydrin cross-linking to 1-10 h to prepare cross-linked microspheres, wash the cross-linked microspheres with distilled water until neutral, dehydrate and store them for later use to obtain pyridine Functionalized chitosan adsorbent.
本发明的有益效果为:The beneficial effects of the present invention are:
(1)本发明制备树脂的材料成本低廉,所修饰的功能基具有稳定的空间结构,吡啶基和胺基上的多个氮原子可同时对重金属和抗生素发挥配位螯合作用;(1) The material cost of the resin prepared by the present invention is low, the modified functional group has a stable spatial structure, and multiple nitrogen atoms on the pyridyl group and the amine group can coordinate and chelate heavy metals and antibiotics at the same time;
(2)本发明提供的螯合树脂因含氮功能基吸附位点的增多,显著提高了对重金属和抗生素吸附容量,解决了在畜禽养殖废水中去除重金属或抗生素,吸附量小和吸附速率慢的问题;(2) The chelating resin provided by the present invention significantly improves the adsorption capacity for heavy metals and antibiotics due to the increase in the adsorption sites of nitrogen-containing functional groups, and solves the problem of removing heavy metals or antibiotics in livestock and poultry wastewater, with small adsorption capacity and high adsorption rate. slow problem;
(3)本发明提供的螯合树脂通过改变重金属离子和抗生素吸附pH值范围、抗盐特性以及吸附位点和空间结构,可实现对重金属和抗生素的选择性去除及同步回收,在宽泛pH范围下的畜禽养殖废水复合污染物的选择性及协同控制方面具有广阔的应用前景。(3) The chelating resin provided by the present invention can realize the selective removal and synchronous recovery of heavy metals and antibiotics by changing the adsorption pH range, salt resistance characteristics, adsorption sites and spatial structure of heavy metal ions and antibiotics. It has broad application prospects in the selective and coordinated control of complex pollutants in livestock and poultry breeding wastewater.
具体实施方式Detailed ways
下面结合具体实施例对本发明作进一步解说。The present invention will be further explained below in conjunction with specific embodiments.
实施例1Example 1
本实施例提出的一种吡啶功能化壳聚糖吸附剂的制备方法,包括以下步骤:A kind of preparation method of pyridine functionalized chitosan adsorbent proposed by the present embodiment comprises the following steps:
S1:将0.1g质量浓度为5-100 g/L的聚乙烯亚胺、0.05g质量浓度为2.5-100 g/L的2-氯甲基吡啶盐酸盐及0.2g质量浓度为10-100 g/L的碳酸钠溶解于1 ml乙醇和5 ml蒸馏水的水溶液中,其溶解温度设置为85 ℃,且溶解时间设置为2 h,同时利用85℃油浴中磁力进行搅拌直至搅拌均匀,然后利用冷却装置进行冷却操作,冷却装置首先以3-5℃/min的速率进行冷却,直到冷却到30℃,冷却装置再以0.3-0.5℃/min的速率进行冷却,直到冷却到至室温,再利用离心设备和过滤筛依次进行离心操作、过滤处理,最后经过50℃的旋转蒸发仪旋干15 min,得到油相;S1: 0.1 g of polyethyleneimine with a mass concentration of 5-100 g/L, 0.05 g of 2-chloromethylpyridine hydrochloride with a mass concentration of 2.5-100 g/L and 0.2 g of a mass concentration of 10-100 g/L Dissolve g/L sodium carbonate in an aqueous solution of 1 ml ethanol and 5 ml distilled water, set the dissolving temperature to 85 °C, and set the dissolving time to 2 h, and at the same time use magnetic force in an 85 °C oil bath to stir until it is evenly stirred, then Use the cooling device for cooling operation. The cooling device first cools at a rate of 3-5°C/min until it cools down to 30°C. The cooling device then cools at a rate of 0.3-0.5°C/min until it cools to room temperature, and then Use a centrifugal device and a filter sieve to perform centrifugation and filtration in sequence, and finally spin-dry in a rotary evaporator at 50°C for 15 minutes to obtain the oil phase;
S2:将0.06g质量浓度为2-50 g/L的壳聚糖粉末溶解于0.3 ml冰醋酸和29.4 ml蒸馏水的水溶液中,其溶解温度设置为室温,且溶解时间设置为20 min,同时利用搅拌设备进行搅拌直至搅拌均匀,然后过滤设备从上至下依次利用多个筛网进行多级过滤,且从上至下的多个筛网的网孔逐次减小,最终得到壳聚糖母液;S2: Dissolve 0.06 g of chitosan powder with a mass concentration of 2-50 g/L in an aqueous solution of 0.3 ml of glacial acetic acid and 29.4 ml of distilled water, set the dissolution temperature to room temperature, and set the dissolution time to 20 min. The stirring equipment stirs until it is evenly stirred, and then the filtering equipment uses multiple screens to perform multi-stage filtration from top to bottom, and the meshes of the multiple screens from top to bottom are gradually reduced, and finally the chitosan mother liquor is obtained;
S3:将步骤S1中制备的油相逐滴加入至S2中制备的壳聚糖母液中,滴加时间设置为5-60 min,油相与壳聚糖母液的反应时间设置为1 h,在反应的过程中利用搅拌设备进行搅拌均匀,并用0.144ml体积浓度为0.4-15%的环氧氯丙烷初交联,环氧氯丙烷初交联的交联温度设置为20℃,且交联时间设置为1 h,得到混合母液;S3: Add the oil phase prepared in step S1 dropwise to the chitosan mother liquor prepared in S2, the dropping time is set to 5-60 min, and the reaction time between the oil phase and the chitosan mother liquor is set to 1 h. During the reaction process, use a stirring device to stir evenly, and use 0.144ml of epichlorohydrin with a volume concentration of 0.4-15% for initial crosslinking. Set to 1 h to obtain the mixed mother liquor;
S4:将S3中所得混合母液泵入1000ml含有3 g无水硫酸钠和3 g氢氧化钠的凝固浴中固化成球,静置30min,经沉淀凝固得到复合微球;S4: pump the mixed mother liquor obtained in S3 into 1000 ml of a coagulation bath containing 3 g of anhydrous sodium sulfate and 3 g of sodium hydroxide to solidify into balls, let stand for 30 minutes, and obtain composite microspheres through precipitation and solidification;
S5:将步骤S4中的复合微球经索氏抽提器进行2h的抽提,去除树脂孔道中残留的致孔剂,依次用乙醇、蒸馏水洗涤各3次,脱水后,取出0.2g复合微球投加到100ml pH值为10的氢氧化钠的水溶液中,用0.01 ml体积浓度为0.01-1%的环氧氯丙烷进行后交联,环氧氯丙烷交联的交联温度设置为20℃,且环氧氯丙烷交联的交联时间设置为1 h,制得交联微球,交联微球再利用用蒸馏水洗至中性,脱水保存备用得到吡啶功能化壳聚糖吸附剂A。S5: Extract the composite microspheres in step S4 through a Soxhlet extractor for 2 hours to remove the porogen remaining in the resin channels, wash with ethanol and distilled water three times in turn, and after dehydration, take out 0.2 g of the composite microspheres. Add the ball to 100ml of sodium hydroxide aqueous solution with a pH value of 10, and use 0.01 ml of epichlorohydrin with a volume concentration of 0.01-1% for post-crosslinking, and the crosslinking temperature for epichlorohydrin crosslinking is set to 20 ℃, and the cross-linking time of epichlorohydrin cross-linking was set as 1 h to prepare cross-linked microspheres, which were washed with distilled water until neutral, dehydrated and stored for later use to obtain pyridine functionalized chitosan adsorbent a.
实施例2Example 2
本实施例提出的一种吡啶功能化壳聚糖吸附剂的制备方法,包括以下步骤:A kind of preparation method of pyridine functionalized chitosan adsorbent proposed by the present embodiment comprises the following steps:
S1:将0.2g质量浓度为5-100 g/L的聚乙烯亚胺、0.05g质量浓度为2.5-100 g/L的2-氯甲基吡啶盐酸盐及0.2g质量浓度为10-100 g/L的碳酸钠溶解于1 ml乙醇和5 ml蒸馏水的水溶液中,其溶解温度设置为85 ℃,且溶解时间设置为2 h,同时利用85℃油浴中磁力进行搅拌直至搅拌均匀,然后利用冷却装置进行冷却操作,冷却装置首先以3-5℃/min的速率进行冷却,直到冷却到30℃,冷却装置再以0.3-0.5℃/min的速率进行冷却,直到冷却到至室温,再利用离心设备和过滤筛依次进行离心操作、过滤处理,最后经过50℃的旋转蒸发仪旋干15 min,得到油相;S1: 0.2g of polyethyleneimine with a mass concentration of 5-100 g/L, 0.05g of 2-chloromethylpyridine hydrochloride with a mass concentration of 2.5-100 g/L and 0.2g of a mass concentration of 10-100 Dissolve g/L sodium carbonate in an aqueous solution of 1 ml ethanol and 5 ml distilled water, set the dissolving temperature to 85 °C, and set the dissolving time to 2 h, and at the same time use magnetic force in an 85 °C oil bath to stir until it is evenly stirred, then Use the cooling device for cooling operation. The cooling device first cools at a rate of 3-5°C/min until it cools down to 30°C. The cooling device then cools at a rate of 0.3-0.5°C/min until it cools to room temperature, and then Use a centrifugal device and a filter sieve to perform centrifugation and filtration in sequence, and finally spin-dry in a rotary evaporator at 50°C for 15 minutes to obtain the oil phase;
S2:将0.06g质量浓度为2-50 g/L的壳聚糖粉末溶解于0.3 ml冰醋酸和29.4 ml蒸馏水的水溶液中,其溶解温度设置为室温,且溶解时间设置为20 min,同时利用搅拌设备进行搅拌直至搅拌均匀,然后过滤设备从上至下依次利用多个筛网进行多级过滤,且从上至下的多个筛网的网孔逐次减小,最终得到壳聚糖母液;S2: Dissolve 0.06 g of chitosan powder with a mass concentration of 2-50 g/L in an aqueous solution of 0.3 ml of glacial acetic acid and 29.4 ml of distilled water, set the dissolution temperature to room temperature, and set the dissolution time to 20 min. The stirring equipment stirs until it is evenly stirred, and then the filtering equipment uses multiple screens to perform multi-stage filtration from top to bottom, and the meshes of the multiple screens from top to bottom are gradually reduced, and finally the chitosan mother liquor is obtained;
S3:将步骤S1中制备的油相逐滴加入至S2中制备的壳聚糖母液中,滴加时间设置为5-60 min,油相与壳聚糖母液的反应时间设置为1 h,在反应的过程中利用搅拌设备进行搅拌均匀,并用0.144ml体积浓度为0.4-15%的环氧氯丙烷初交联,环氧氯丙烷初交联的交联温度设置为20℃,且交联时间设置为1 h,得到混合母液;S3: Add the oil phase prepared in step S1 dropwise to the chitosan mother liquor prepared in S2, the dropping time is set to 5-60 min, and the reaction time between the oil phase and the chitosan mother liquor is set to 1 h. During the reaction process, use a stirring device to stir evenly, and use 0.144ml of epichlorohydrin with a volume concentration of 0.4-15% for initial crosslinking. Set to 1 h to obtain the mixed mother liquor;
S4:将S3中所得混合母液泵入1000ml含有3 g无水硫酸钠和3 g氢氧化钠的凝固浴中固化成球,静置30min,经沉淀凝固得到复合微球;S4: pump the mixed mother liquor obtained in S3 into 1000 ml of a coagulation bath containing 3 g of anhydrous sodium sulfate and 3 g of sodium hydroxide to solidify into balls, let stand for 30 minutes, and obtain composite microspheres through precipitation and solidification;
S5:将步骤S4中的复合微球经索氏抽提器进行2h的抽提,去除树脂孔道中残留的致孔剂,依次用乙醇、蒸馏水洗涤各3次,脱水后,取出0.2g复合微球投加到100ml pH值为10的氢氧化钠的水溶液中,用0.01 ml体积浓度为0.01-1%的环氧氯丙烷进行后交联,环氧氯丙烷交联的交联温度设置为20℃,且环氧氯丙烷交联的交联时间设置为1 h,制得交联微球,交联微球再利用用蒸馏水洗至中性,脱水保存备用得到吡啶功能化壳聚糖吸附剂B。S5: Extract the composite microspheres in step S4 through a Soxhlet extractor for 2 hours to remove the porogen remaining in the resin channels, wash with ethanol and distilled water three times in turn, and after dehydration, take out 0.2 g of the composite microspheres. Add the ball to 100ml of sodium hydroxide aqueous solution with a pH value of 10, and use 0.01 ml of epichlorohydrin with a volume concentration of 0.01-1% for post-crosslinking, and the crosslinking temperature for epichlorohydrin crosslinking is set to 20 ℃, and the cross-linking time of epichlorohydrin cross-linking was set as 1 h to prepare cross-linked microspheres, which were washed with distilled water until neutral, dehydrated and stored for later use to obtain pyridine functionalized chitosan adsorbent b.
实施例3Example 3
本实施例提出的一种吡啶功能化壳聚糖吸附剂的制备方法,包括以下步骤:A kind of preparation method of pyridine functionalized chitosan adsorbent proposed by the present embodiment comprises the following steps:
S1:将0.7g质量浓度为5-100 g/L的聚乙烯亚胺、0.25g质量浓度为2.5-100 g/L的2-氯甲基吡啶盐酸盐及0.3231g质量浓度为10-100 g/L的碳酸钠溶解于15 ml乙醇和5 ml蒸馏水的水溶液中,其溶解温度设置为85 ℃,且溶解时间设置为2 h,同时利用85℃油浴中磁力进行搅拌直至搅拌均匀,然后利用冷却装置进行冷却操作,冷却装置首先以3-5℃/min的速率进行冷却,直到冷却到30℃,冷却装置再以0.3-0.5℃/min的速率进行冷却,直到冷却到至室温,再利用离心设备和过滤筛依次进行离心操作、过滤处理,最后经过50℃的旋转蒸发仪旋干15 min,得到油相;S1: 0.7g of polyethyleneimine with a mass concentration of 5-100 g/L, 0.25g of 2-chloromethylpyridine hydrochloride with a mass concentration of 2.5-100 g/L and 0.3231g of a mass concentration of 10-100 g/L Dissolve g/L sodium carbonate in an aqueous solution of 15 ml ethanol and 5 ml distilled water, set the dissolving temperature to 85 °C, and set the dissolving time to 2 h, and at the same time use magnetic force in an 85 °C oil bath to stir until it is evenly stirred, then Use the cooling device for cooling operation. The cooling device first cools at a rate of 3-5°C/min until it cools down to 30°C. The cooling device then cools at a rate of 0.3-0.5°C/min until it cools to room temperature, and then Use a centrifugal device and a filter sieve to perform centrifugation and filtration in sequence, and finally spin-dry in a rotary evaporator at 50°C for 15 minutes to obtain the oil phase;
S2:将0.5g质量浓度为2-50 g/L的壳聚糖粉末溶解于0.6 ml冰醋酸和29.4 ml蒸馏水的水溶液中,其溶解温度设置为室温,且溶解时间设置为30 min,同时利用搅拌设备进行搅拌直至搅拌均匀,然后过滤设备从上至下依次利用多个筛网进行多级过滤,且从上至下的多个筛网的网孔逐次减小,最终得到壳聚糖母液;S2: Dissolve 0.5 g of chitosan powder with a mass concentration of 2-50 g/L in an aqueous solution of 0.6 ml of glacial acetic acid and 29.4 ml of distilled water, set the dissolution temperature to room temperature, and set the dissolution time to 30 min. The stirring equipment stirs until it is evenly stirred, and then the filtering equipment uses multiple screens to perform multi-stage filtration from top to bottom, and the meshes of the multiple screens from top to bottom are gradually reduced, and finally the chitosan mother liquor is obtained;
S3:将步骤S1中制备的油相逐滴加入至S2中制备的壳聚糖母液中,滴加时间设置为5-60 min,油相与壳聚糖母液的反应时间设置为2 h,在反应的过程中利用搅拌设备进行搅拌均匀,并用0.23ml体积浓度为0.4-15%的环氧氯丙烷初交联,环氧氯丙烷初交联的交联温度设置为60℃,且交联时间设置为2h,得到混合母液;S3: Add the oil phase prepared in step S1 dropwise to the chitosan mother liquor prepared in S2, the dropping time is set to 5-60 min, and the reaction time between the oil phase and the chitosan mother liquor is set to 2 h. During the reaction process, use a stirring device to stir evenly, and use 0.23ml of epichlorohydrin with a volume concentration of 0.4-15% for initial cross-linking. Set to 2h to obtain mixed mother liquor;
S4:将S3中所得混合母液泵入1000ml含有13 g无水硫酸钠和16 g氢氧化钠的凝固浴中固化成球,静置30min,经沉淀凝固得到复合微球;S4: pump the mixed mother liquor obtained in S3 into 1000 ml of a coagulation bath containing 13 g of anhydrous sodium sulfate and 16 g of sodium hydroxide to solidify into balls, let stand for 30 minutes, and obtain composite microspheres through precipitation and solidification;
S5:将步骤S4中的复合微球经索氏抽提器进行4h的抽提,去除树脂孔道中残留的致孔剂,依次用乙醇、蒸馏水洗涤各3次,脱水后,取出2g复合微球投加到100ml pH值为13的氢氧化钠的水溶液中,用0.3 ml体积浓度为0.01-1%的环氧氯丙烷进行后交联,环氧氯丙烷交联的交联温度设置为60℃,且环氧氯丙烷交联的交联时间设置为2 h,制得交联微球,交联微球再利用用蒸馏水洗至中性,脱水保存备用得到吡啶功能化壳聚糖吸附剂C。S5: Extract the composite microspheres in step S4 through a Soxhlet extractor for 4 hours to remove the porogen remaining in the resin channels, wash with ethanol and distilled water for 3 times in turn, and take out 2 g of composite microspheres after dehydration Add 100ml of sodium hydroxide aqueous solution with a pH value of 13, use 0.3 ml of epichlorohydrin with a volume concentration of 0.01-1% for post-crosslinking, and set the crosslinking temperature of epichlorohydrin to 60°C , and the cross-linking time of epichlorohydrin cross-linking was set to 2 h to obtain cross-linked microspheres, which were then washed with distilled water until neutral, dehydrated and stored for later use to obtain pyridine functionalized chitosan adsorbent C .
实施例4Example 4
本实施例提出的一种吡啶功能化壳聚糖吸附剂的制备方法,包括以下步骤:A kind of preparation method of pyridine functionalized chitosan adsorbent proposed by the present embodiment comprises the following steps:
S1:将0.7g质量浓度为5-100 g/L的聚乙烯亚胺、0.25g质量浓度为2.5-100 g/L的2-氯甲基吡啶盐酸盐及0.3231g质量浓度为10-100 g/L的碳酸钠溶解于15 ml乙醇和5 ml蒸馏水的水溶液中,其溶解温度设置为85 ℃,且溶解时间设置为2 h,同时利用85℃油浴中磁力进行搅拌直至搅拌均匀,然后利用冷却装置进行冷却操作,冷却装置首先以3-5℃/min的速率进行冷却,直到冷却到30℃,冷却装置再以0.3-0.5℃/min的速率进行冷却,直到冷却到至室温,再利用离心设备和过滤筛依次进行离心操作、过滤处理,最后经过50℃的旋转蒸发仪旋干15 min,得到油相;S1: 0.7g of polyethyleneimine with a mass concentration of 5-100 g/L, 0.25g of 2-chloromethylpyridine hydrochloride with a mass concentration of 2.5-100 g/L and 0.3231g of a mass concentration of 10-100 g/L Dissolve g/L sodium carbonate in an aqueous solution of 15 ml ethanol and 5 ml distilled water, set the dissolving temperature to 85 °C, and set the dissolving time to 2 h, and at the same time use magnetic force in an 85 °C oil bath to stir until it is evenly stirred, then Use the cooling device for cooling operation. The cooling device first cools at a rate of 3-5°C/min until it cools down to 30°C. The cooling device then cools at a rate of 0.3-0.5°C/min until it cools to room temperature, and then Use a centrifugal device and a filter sieve to perform centrifugation and filtration in sequence, and finally spin-dry in a rotary evaporator at 50°C for 15 minutes to obtain the oil phase;
S2:将0.9g质量浓度为2-50 g/L的壳聚糖粉末溶解于0.6 ml冰醋酸和29.4 ml蒸馏水的水溶液中,其溶解温度设置为室温,且溶解时间设置为30 min,同时利用搅拌设备进行搅拌直至搅拌均匀,然后过滤设备从上至下依次利用多个筛网进行多级过滤,且从上至下的多个筛网的网孔逐次减小,最终得到壳聚糖母液;S2: Dissolve 0.9 g of chitosan powder with a mass concentration of 2-50 g/L in an aqueous solution of 0.6 ml of glacial acetic acid and 29.4 ml of distilled water, set the dissolution temperature to room temperature, and set the dissolution time to 30 min. The stirring equipment stirs until it is evenly stirred, and then the filtering equipment uses multiple screens to perform multi-stage filtration from top to bottom, and the meshes of the multiple screens from top to bottom are gradually reduced, and finally the chitosan mother liquor is obtained;
S3:将步骤S1中制备的油相逐滴加入至S2中制备的壳聚糖母液中,滴加时间设置为5-60 min,油相与壳聚糖母液的反应时间设置为2 h,在反应的过程中利用搅拌设备进行搅拌均匀,并用0.23ml体积浓度为0.4-15%的环氧氯丙烷初交联,环氧氯丙烷初交联的交联温度设置为60℃,且交联时间设置为2h,得到混合母液;S3: Add the oil phase prepared in step S1 dropwise to the chitosan mother liquor prepared in S2, the dropping time is set to 5-60 min, and the reaction time between the oil phase and the chitosan mother liquor is set to 2 h. During the reaction process, use a stirring device to stir evenly, and use 0.23ml of epichlorohydrin with a volume concentration of 0.4-15% for initial cross-linking. Set to 2h to obtain mixed mother liquor;
S4:将S3中所得混合母液泵入1000ml含有13 g无水硫酸钠和16 g氢氧化钠的凝固浴中固化成球,静置30min,经沉淀凝固得到复合微球;S4: pump the mixed mother liquor obtained in S3 into 1000 ml of a coagulation bath containing 13 g of anhydrous sodium sulfate and 16 g of sodium hydroxide to solidify into balls, let stand for 30 minutes, and obtain composite microspheres through precipitation and solidification;
S5:将步骤S4中的复合微球经索氏抽提器进行4h的抽提,去除树脂孔道中残留的致孔剂,依次用乙醇、蒸馏水洗涤各3次,脱水后,取出2g复合微球投加到100ml pH值为13的氢氧化钠的水溶液中,用0.3 ml体积浓度为0.01-1%的环氧氯丙烷进行后交联,环氧氯丙烷交联的交联温度设置为60℃,且环氧氯丙烷交联的交联时间设置为2 h,制得交联微球,交联微球再利用用蒸馏水洗至中性,脱水保存备用得到吡啶功能化壳聚糖吸附剂D。S5: Extract the composite microspheres in step S4 through a Soxhlet extractor for 4 hours to remove the porogen remaining in the resin channels, wash with ethanol and distilled water for 3 times in turn, and take out 2 g of composite microspheres after dehydration Add 100ml of sodium hydroxide aqueous solution with a pH value of 13, use 0.3 ml of epichlorohydrin with a volume concentration of 0.01-1% for post-crosslinking, and set the crosslinking temperature of epichlorohydrin to 60°C , and the cross-linking time of epichlorohydrin cross-linking was set to 2 h, and the cross-linked microspheres were obtained, and the cross-linked microspheres were washed with distilled water until neutral, dehydrated and stored for later use to obtain pyridine functionalized chitosan adsorbent D .
实施例5Example 5
本实施例提出的一种吡啶功能化壳聚糖吸附剂的制备方法,包括以下步骤:A kind of preparation method of pyridine functionalized chitosan adsorbent proposed by the present embodiment comprises the following steps:
S1:将0.7g质量浓度为5-100 g/L的聚乙烯亚胺、0.5g质量浓度为2.5-100 g/L的2-氯甲基吡啶盐酸盐及0.3231g质量浓度为10-100 g/L的碳酸钠溶解于15 ml乙醇和5 ml蒸馏水的水溶液中,其溶解温度设置为85 ℃,且溶解时间设置为2 h,同时利用85℃油浴中磁力进行搅拌直至搅拌均匀,然后利用冷却装置进行冷却操作,冷却装置首先以3-5℃/min的速率进行冷却,直到冷却到30℃,冷却装置再以0.3-0.5℃/min的速率进行冷却,直到冷却到至室温,再利用离心设备和过滤筛依次进行离心操作、过滤处理,最后经过50℃的旋转蒸发仪旋干15 min,得到油相;S1: 0.7g of polyethyleneimine with a mass concentration of 5-100 g/L, 0.5g of 2-chloromethylpyridine hydrochloride with a mass concentration of 2.5-100 g/L and 0.3231g of a mass concentration of 10-100 Dissolve g/L sodium carbonate in an aqueous solution of 15 ml ethanol and 5 ml distilled water, set the dissolving temperature to 85 °C, and set the dissolving time to 2 h, and at the same time use magnetic force in an 85 °C oil bath to stir until it is evenly stirred, then Use the cooling device for cooling operation. The cooling device first cools at a rate of 3-5°C/min until it cools down to 30°C. The cooling device then cools at a rate of 0.3-0.5°C/min until it cools to room temperature, and then Use a centrifugal device and a filter sieve to perform centrifugation and filtration in sequence, and finally spin-dry in a rotary evaporator at 50°C for 15 minutes to obtain the oil phase;
S2:将0.9g质量浓度为2-50 g/L的壳聚糖粉末溶解于0.6 ml冰醋酸和29.4 ml蒸馏水的水溶液中,其溶解温度设置为室温,且溶解时间设置为30 min,同时利用搅拌设备进行搅拌直至搅拌均匀,然后过滤设备从上至下依次利用多个筛网进行多级过滤,且从上至下的多个筛网的网孔逐次减小,最终得到壳聚糖母液;S2: Dissolve 0.9 g of chitosan powder with a mass concentration of 2-50 g/L in an aqueous solution of 0.6 ml of glacial acetic acid and 29.4 ml of distilled water, set the dissolution temperature to room temperature, and set the dissolution time to 30 min. The stirring equipment stirs until it is evenly stirred, and then the filtering equipment uses multiple screens to perform multi-stage filtration from top to bottom, and the meshes of the multiple screens from top to bottom are gradually reduced, and finally the chitosan mother liquor is obtained;
S3:将步骤S1中制备的油相逐滴加入至S2中制备的壳聚糖母液中,滴加时间设置为5-60 min,油相与壳聚糖母液的反应时间设置为2 h,在反应的过程中利用搅拌设备进行搅拌均匀,并用0.23ml体积浓度为0.4-15%的环氧氯丙烷初交联,环氧氯丙烷初交联的交联温度设置为60℃,且交联时间设置为2h,得到混合母液;S3: Add the oil phase prepared in step S1 dropwise to the chitosan mother liquor prepared in S2, the dropping time is set to 5-60 min, and the reaction time between the oil phase and the chitosan mother liquor is set to 2 h. During the reaction process, use a stirring device to stir evenly, and use 0.23ml of epichlorohydrin with a volume concentration of 0.4-15% for initial cross-linking. Set to 2h to obtain mixed mother liquor;
S4:将S3中所得混合母液泵入1000ml含有13 g无水硫酸钠和16 g氢氧化钠的凝固浴中固化成球,静置30min,经沉淀凝固得到复合微球;S4: pump the mixed mother liquor obtained in S3 into 1000 ml of a coagulation bath containing 13 g of anhydrous sodium sulfate and 16 g of sodium hydroxide to solidify into balls, let stand for 30 minutes, and obtain composite microspheres through precipitation and solidification;
S5:将步骤S4中的复合微球经索氏抽提器进行4h的抽提,去除树脂孔道中残留的致孔剂,依次用乙醇、蒸馏水洗涤各3次,脱水后,取出2g复合微球投加到100ml pH值为13的氢氧化钠的水溶液中,用0.3 ml体积浓度为0.01-1%的环氧氯丙烷进行后交联,环氧氯丙烷交联的交联温度设置为60℃,且环氧氯丙烷交联的交联时间设置为2 h,制得交联微球,交联微球再利用用蒸馏水洗至中性,脱水保存备用得到吡啶功能化壳聚糖吸附剂E。S5: Extract the composite microspheres in step S4 through a Soxhlet extractor for 4 hours to remove the porogen remaining in the resin channels, wash with ethanol and distilled water for 3 times in turn, and take out 2 g of composite microspheres after dehydration Add 100ml of sodium hydroxide aqueous solution with a pH value of 13, use 0.3 ml of epichlorohydrin with a volume concentration of 0.01-1% for post-crosslinking, and set the crosslinking temperature of epichlorohydrin to 60°C , and the cross-linking time of epichlorohydrin cross-linking was set to 2 h to obtain cross-linked microspheres, which were washed with distilled water until neutral, dehydrated and stored for later use to obtain pyridine functionalized chitosan adsorbent E .
实施例6Example 6
本实施例提出的一种吡啶功能化壳聚糖吸附剂的制备方法,包括以下步骤:A kind of preparation method of pyridine functionalized chitosan adsorbent proposed by the present embodiment comprises the following steps:
S1:将2g质量浓度为5-100 g/L的聚乙烯亚胺、2g质量浓度为2.5-100 g/L的2-氯甲基吡啶盐酸盐及2g质量浓度为10-100 g/L的碳酸钠溶解于15 ml乙醇和5 ml蒸馏水的水溶液中,其溶解温度设置为85 ℃,且溶解时间设置为2 h,同时利用85℃油浴中磁力进行搅拌直至搅拌均匀,然后利用冷却装置进行冷却操作,冷却装置首先以3-5℃/min的速率进行冷却,直到冷却到30℃,冷却装置再以0.3-0.5℃/min的速率进行冷却,直到冷却到至室温,再利用离心设备和过滤筛依次进行离心操作、过滤处理,最后经过50℃的旋转蒸发仪旋干15min,得到油相;S1: 2 g of polyethyleneimine with a mass concentration of 5-100 g/L, 2 g of 2-chloromethylpyridine hydrochloride with a mass concentration of 2.5-100 g/L and 2 g of a mass concentration of 10-100 g/L Sodium carbonate was dissolved in an aqueous solution of 15 ml ethanol and 5 ml distilled water, the dissolution temperature was set at 85°C, and the dissolution time was set at 2 h, and at the same time, it was stirred by magnetic force in an oil bath at 85°C until it was evenly stirred, and then the cooling device was used to For cooling operation, the cooling device first cools at a rate of 3-5°C/min until it cools to 30°C, and then cools at a rate of 0.3-0.5°C/min until it cools to room temperature, and then uses a centrifugal device Centrifuge and filter in turn with a filter sieve, and finally spin-dry in a rotary evaporator at 50°C for 15 minutes to obtain the oil phase;
S2:将1.5g质量浓度为2-50 g/L的壳聚糖粉末溶解于2.4 ml冰醋酸和29.4 ml蒸馏水的水溶液中,其溶解温度设置为室温,且溶解时间设置为90 min,同时利用搅拌设备进行搅拌直至搅拌均匀,然后过滤设备从上至下依次利用多个筛网进行多级过滤,且从上至下的多个筛网的网孔逐次减小,最终得到壳聚糖母液;S2: Dissolve 1.5 g of chitosan powder with a mass concentration of 2-50 g/L in an aqueous solution of 2.4 ml of glacial acetic acid and 29.4 ml of distilled water, set the dissolution temperature to room temperature, and set the dissolution time to 90 min. The stirring equipment stirs until it is evenly stirred, and then the filtering equipment uses multiple screens to perform multi-stage filtration from top to bottom, and the meshes of the multiple screens from top to bottom are gradually reduced, and finally the chitosan mother liquor is obtained;
S3:将步骤S1中制备的油相逐滴加入至S2中制备的壳聚糖母液中,滴加时间设置为5-60 min,油相与壳聚糖母液的反应时间设置为8h,在反应的过程中利用搅拌设备进行搅拌均匀,并用2ml体积浓度为0.4-15%的环氧氯丙烷初交联,环氧氯丙烷初交联的交联温度设置为70℃,且交联时间设置为8h,得到混合母液;S3: Add the oil phase prepared in step S1 dropwise to the chitosan mother liquor prepared in S2, the dropping time is set to 5-60 min, and the reaction time between the oil phase and the chitosan mother liquor is set to 8h. During the process, the stirring equipment was used to stir evenly, and 2ml of epichlorohydrin with a volume concentration of 0.4-15% was used for initial cross-linking. The cross-linking temperature of epichlorohydrin initial cross-linking was set to 70°C, and the cross-linking time was set 8h, obtain mixed mother liquor;
S4:将S3中所得混合母液泵入1000ml含有50 g无水硫酸钠和50 g氢氧化钠的凝固浴中固化成球,静置30min,经沉淀凝固得到复合微球;S4: pump the mixed mother liquor obtained in S3 into 1000 ml of a coagulation bath containing 50 g of anhydrous sodium sulfate and 50 g of sodium hydroxide to solidify into balls, let stand for 30 minutes, and obtain composite microspheres through precipitation and solidification;
S5:将步骤S4中的复合微球经索氏抽提器进行10h的抽提,去除树脂孔道中残留的致孔剂,依次用乙醇、蒸馏水洗涤各3次,脱水后,取出4g复合微球投加到100ml pH值为14的氢氧化钠的水溶液中,用0.5ml体积浓度为0.01-1%的环氧氯丙烷进行后交联,环氧氯丙烷交联的交联温度设置为70℃,且环氧氯丙烷交联的交联时间设置为7 h,制得交联微球,交联微球再利用用蒸馏水洗至中性,脱水保存备用得到吡啶功能化壳聚糖吸附剂F。S5: Extract the composite microspheres in step S4 through a Soxhlet extractor for 10 hours to remove the porogen remaining in the resin channels, wash with ethanol and distilled water for 3 times each, and after dehydration, take out 4g of composite microspheres Add 100ml of sodium hydroxide aqueous solution with a pH value of 14, and use 0.5ml of epichlorohydrin with a volume concentration of 0.01-1% for post-crosslinking. The crosslinking temperature for epichlorohydrin crosslinking is set to 70°C , and the cross-linking time of epichlorohydrin cross-linking was set to 7 h to obtain cross-linked microspheres, which were then washed with distilled water until neutral, dehydrated and stored for later use to obtain pyridine functionalized chitosan adsorbent F .
实施例7Example 7
本实施例提出的一种吡啶功能化壳聚糖吸附剂的制备方法,包括以下步骤:A kind of preparation method of pyridine functionalized chitosan adsorbent proposed by the present embodiment comprises the following steps:
S1:将2g质量浓度为5-100 g/L的聚乙烯亚胺、2g质量浓度为2.5-100 g/L的2-氯甲基吡啶盐酸盐及2g质量浓度为10-100 g/L的碳酸钠溶解于15 ml乙醇和5 ml蒸馏水的水溶液中,其溶解温度设置为85 ℃,且溶解时间设置为2 h,同时利用85℃油浴中磁力进行搅拌直至搅拌均匀,然后利用冷却装置进行冷却操作,冷却装置首先以3-5℃/min的速率进行冷却,直到冷却到30℃,冷却装置再以0.3-0.5℃/min的速率进行冷却,直到冷却到至室温,再利用离心设备和过滤筛依次进行离心操作、过滤处理,最后经过50℃的旋转蒸发仪旋干15min,得到油相;S1: 2 g of polyethyleneimine with a mass concentration of 5-100 g/L, 2 g of 2-chloromethylpyridine hydrochloride with a mass concentration of 2.5-100 g/L and 2 g of a mass concentration of 10-100 g/L Sodium carbonate was dissolved in an aqueous solution of 15 ml ethanol and 5 ml distilled water, the dissolution temperature was set at 85°C, and the dissolution time was set at 2 h, and at the same time, it was stirred by magnetic force in an oil bath at 85°C until it was evenly stirred, and then the cooling device was used to For cooling operation, the cooling device first cools at a rate of 3-5°C/min until it cools to 30°C, and then cools at a rate of 0.3-0.5°C/min until it cools to room temperature, and then uses a centrifugal device Centrifuge and filter in turn with a filter sieve, and finally spin-dry in a rotary evaporator at 50°C for 15 minutes to obtain the oil phase;
S2:将1.5g质量浓度为2-50 g/L的壳聚糖粉末溶解于2.4 ml冰醋酸和29.4 ml蒸馏水的水溶液中,其溶解温度设置为室温,且溶解时间设置为90 min,同时利用搅拌设备进行搅拌直至搅拌均匀,然后过滤设备从上至下依次利用多个筛网进行多级过滤,且从上至下的多个筛网的网孔逐次减小,最终得到壳聚糖母液;S2: Dissolve 1.5 g of chitosan powder with a mass concentration of 2-50 g/L in an aqueous solution of 2.4 ml of glacial acetic acid and 29.4 ml of distilled water, set the dissolution temperature to room temperature, and set the dissolution time to 90 min. The stirring equipment stirs until it is evenly stirred, and then the filtering equipment uses multiple screens to perform multi-stage filtration from top to bottom, and the meshes of the multiple screens from top to bottom are gradually reduced, and finally the chitosan mother liquor is obtained;
S3:将步骤S1中制备的油相逐滴加入至S2中制备的壳聚糖母液中,滴加时间设置为5-60 min,油相与壳聚糖母液的反应时间设置为10h,在反应的过程中利用搅拌设备进行搅拌均匀,并用4ml体积浓度为0.4-15%的环氧氯丙烷初交联,环氧氯丙烷初交联的交联温度设置为80℃,且交联时间设置为10h,得到混合母液;S3: Add the oil phase prepared in step S1 dropwise to the chitosan mother liquor prepared in S2, the dropping time is set to 5-60 min, the reaction time of the oil phase and the chitosan mother liquor is set to 10h, after the reaction During the process, the stirring equipment was used to stir evenly, and 4ml of epichlorohydrin with a volume concentration of 0.4-15% was used for initial crosslinking. The crosslinking temperature of epichlorohydrin initial crosslinking was set to 80 ° C, and the crosslinking time was set to 10h, obtain mixed mother liquor;
S4:将S3中所得混合母液泵入1000ml含有50 g无水硫酸钠和50 g氢氧化钠的凝固浴中固化成球,静置30min,经沉淀凝固得到复合微球;S4: pump the mixed mother liquor obtained in S3 into 1000 ml of a coagulation bath containing 50 g of anhydrous sodium sulfate and 50 g of sodium hydroxide to solidify into balls, let stand for 30 minutes, and obtain composite microspheres through precipitation and solidification;
S5:将步骤S4中的复合微球经索氏抽提器进行10h的抽提,去除树脂孔道中残留的致孔剂,依次用乙醇、蒸馏水洗涤各3次,脱水后,取出4g复合微球投加到100ml pH值为14的氢氧化钠的水溶液中,用1ml体积浓度为0.01-1%的环氧氯丙烷进行后交联,环氧氯丙烷交联的交联温度设置为80℃,且环氧氯丙烷交联的交联时间设置为10 h,制得交联微球,交联微球再利用用蒸馏水洗至中性,脱水保存备用得到吡啶功能化壳聚糖吸附剂G。S5: Extract the composite microspheres in step S4 through a Soxhlet extractor for 10 hours to remove the porogen remaining in the resin channels, wash with ethanol and distilled water for 3 times each, and after dehydration, take out 4g of composite microspheres Add 100ml of sodium hydroxide aqueous solution with a pH value of 14, and use 1ml of epichlorohydrin with a volume concentration of 0.01-1% for post-crosslinking. The crosslinking temperature for epichlorohydrin crosslinking is set to 80°C. And the cross-linking time of epichlorohydrin cross-linking was set to 10 h to prepare cross-linked microspheres, which were washed with distilled water until neutral, dehydrated and stored for later use to obtain pyridine functionalized chitosan adsorbent G.
为研究吡啶功能化壳聚糖用的吸附剂对重金属和抗生素的吸附性能,进行如下吸附实验,具体吸附条件为:将0.5g吸附剂分别置于50ml硝酸铜、硝酸镉、硝酸锌、四环素、环丙沙星和磺胺甲恶唑中进行单双组分吸附,其中重金属的浓度均为1mmol/l,抗生素的浓度均为0.5mmol/l,调节溶液的初始pH为5,吸附温度为25℃,震荡速率为130r/min,吸附时间为24h。所得复合吸附剂A-G对单一重金属、抗生素溶液的吸附容量及元素分析结果见表1、表2。In order to study the adsorption performance of the adsorbent for pyridine functionalized chitosan on heavy metals and antibiotics, the following adsorption experiments were carried out. The specific adsorption conditions were: 0.5g of the adsorbent was placed in 50ml of copper nitrate, cadmium nitrate, zinc nitrate, tetracycline, Carry out single and double component adsorption in ciprofloxacin and sulfamethoxazole, in which the concentration of heavy metals is 1mmol/l, the concentration of antibiotics is 0.5mmol/l, the initial pH of the solution is adjusted to 5, and the adsorption temperature is 25°C , the shaking rate is 130r/min, and the adsorption time is 24h. See Table 1 and Table 2 for the adsorption capacity and elemental analysis results of the composite adsorbents A-G for single heavy metal and antibiotic solution.
表1实施例A-G中复合吸附剂对单一重金属、抗生素溶液的吸附容量:Composite adsorbent in table 1 embodiment A-G is to the adsorption capacity of single heavy metal, antibiotic solution:
结合实施例1-7,采用本发明提供制备的方法合成的吡啶功能化壳聚糖吸附剂,方法简单、成本低廉、绿色环保,可以在畜禽养殖废水中重金属和抗生素的同步去除等领域具有广泛的应用价值。In conjunction with Examples 1-7, the pyridine functionalized chitosan adsorbent synthesized by the method provided by the present invention is simple, low in cost, and environmentally friendly, and can be used in the fields of simultaneous removal of heavy metals and antibiotics in livestock and poultry wastewater. Wide application value.
表2实施例A-G中制备的系列吡啶功能化壳聚糖吸附剂主要技术指标Main technical indicators of series pyridine functionalized chitosan adsorbent prepared in the embodiment A-G of table 2
以上所述,仅为本发明较佳的具体实施方式,但本发明的保护范围并不局限于此,任何熟悉本技术领域的技术人员在本发明揭露的技术范围内,根据本发明的技术方案及其发明构思加以等同替换或改变,都应涵盖在本发明的保护范围之内。The above is only a preferred embodiment of the present invention, but the scope of protection of the present invention is not limited thereto, any person familiar with the technical field within the technical scope disclosed in the present invention, according to the technical solution of the present invention Any equivalent replacement or change of the inventive concepts thereof shall fall within the protection scope of the present invention.
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CN112337437A (en) * | 2020-10-29 | 2021-02-09 | 海南师范大学 | A kind of preparation method of pyridine functionalized sodium alginate adsorbent |
CN112387256A (en) * | 2020-10-21 | 2021-02-23 | 南京大学 | Preparation method and application of pyridylamine-based composite hydrogel adsorbent |
CN112495357A (en) * | 2020-12-09 | 2021-03-16 | 昆明理工大学 | Preparation method and application of adsorption polymer containing pyridine group |
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CN119549126A (en) * | 2025-01-24 | 2025-03-04 | 兰州大学 | Modified porous chitosan gel bead, preparation method thereof and application thereof in cobalt-nickel separation |
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Citations (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPH02229830A (en) * | 1989-03-03 | 1990-09-12 | Fuji Spinning Co Ltd | Production of chitosan-based chelate resin |
CN104774283A (en) * | 2015-04-27 | 2015-07-15 | 南京大学 | Acrylic acid pyridine chelating resin as well as preparation method and application thereof |
CN105126790A (en) * | 2015-09-06 | 2015-12-09 | 河南师范大学 | Synthesis and application method of composite function resin for selectively removing nitrate and phosphate at same time |
CN105289560A (en) * | 2015-10-16 | 2016-02-03 | 南京大学 | Chitosan-based composite adsorbent capable of synergistically and efficiently removing positive and negative ions of heavy metals and preparation method thereof |
CN107022037A (en) * | 2017-03-20 | 2017-08-08 | 浙江工商大学 | A kind of 2,6 diamino-pyridine modification of chitosan and its preparation method and application |
-
2019
- 2019-07-30 CN CN201910696803.8A patent/CN110368911A/en active Pending
Patent Citations (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPH02229830A (en) * | 1989-03-03 | 1990-09-12 | Fuji Spinning Co Ltd | Production of chitosan-based chelate resin |
CN104774283A (en) * | 2015-04-27 | 2015-07-15 | 南京大学 | Acrylic acid pyridine chelating resin as well as preparation method and application thereof |
CN105126790A (en) * | 2015-09-06 | 2015-12-09 | 河南师范大学 | Synthesis and application method of composite function resin for selectively removing nitrate and phosphate at same time |
CN105289560A (en) * | 2015-10-16 | 2016-02-03 | 南京大学 | Chitosan-based composite adsorbent capable of synergistically and efficiently removing positive and negative ions of heavy metals and preparation method thereof |
CN107022037A (en) * | 2017-03-20 | 2017-08-08 | 浙江工商大学 | A kind of 2,6 diamino-pyridine modification of chitosan and its preparation method and application |
Non-Patent Citations (2)
Title |
---|
LING, C ET AL.: "Contrastive study for coadsorption of copper and two dihydroxybenzene isomers by a multi-amine modified resin", 《JOURNAL OF HAZARDOUS MATERIALS》 * |
宗黎丹等: "新型吡啶基螯合树脂对强酸高盐溶液中铜镍的分离特性", 《离子交换与吸附》 * |
Cited By (7)
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CN112387256A (en) * | 2020-10-21 | 2021-02-23 | 南京大学 | Preparation method and application of pyridylamine-based composite hydrogel adsorbent |
CN112337437A (en) * | 2020-10-29 | 2021-02-09 | 海南师范大学 | A kind of preparation method of pyridine functionalized sodium alginate adsorbent |
CN112337437B (en) * | 2020-10-29 | 2021-11-19 | 海南师范大学 | Preparation method of pyridine functionalized sodium alginate adsorbent |
CN112495357A (en) * | 2020-12-09 | 2021-03-16 | 昆明理工大学 | Preparation method and application of adsorption polymer containing pyridine group |
CN113402632A (en) * | 2021-07-05 | 2021-09-17 | 华南农业大学 | Novel chitosan-based pyridine quaternary ammonium salt adsorption biological material and preparation method and application thereof |
CN119549126A (en) * | 2025-01-24 | 2025-03-04 | 兰州大学 | Modified porous chitosan gel bead, preparation method thereof and application thereof in cobalt-nickel separation |
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