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CN104475023B - A kind of preparation method of modified konjac glucomannan carbosphere heavy-metal adsorption material - Google Patents

A kind of preparation method of modified konjac glucomannan carbosphere heavy-metal adsorption material Download PDF

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CN104475023B
CN104475023B CN201410797904.1A CN201410797904A CN104475023B CN 104475023 B CN104475023 B CN 104475023B CN 201410797904 A CN201410797904 A CN 201410797904A CN 104475023 B CN104475023 B CN 104475023B
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张红平
陈盼盼
罗学刚
林晓艳
张永德
唐苹苹
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Southwest University of Science and Technology
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    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
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    • B01J20/02Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material
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    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
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Abstract

本发明公开了一种改性魔芋葡甘聚糖碳微球重金属吸附材料的制备方法,包括步骤:(1)将0.5~1重量份魔芋葡甘聚糖加入30~50重量份超纯水中,搅拌,将搅拌后的浊液在160~200℃下反应8~16h,反应液在10000r/min下离心20min,得到的固体用乙醇清洗3~5次,干燥得到碳微球;(2)用体积分数为1~5%的酸溶液调节醇水溶液的pH至4.5,将体积分数为1~3%的硅烷偶联剂溶液加入醇水溶液中震荡2h,得到改性液;(3)取3~15重量份碳微球加入100重量份改性液中,震荡3~5h,过滤,滤饼在65℃下烘干,将烘干后的滤饼用乙醇和水洗涤3~5次,真空干燥,制得改性魔芋葡甘聚糖碳微球吸附材料。本发明克服了现有重金属废水吸附材料存在的工艺难度大,制作条件苛刻等缺点,采用简单、易操作的工艺制备了重金属吸附材料。

The invention discloses a method for preparing a modified konjac glucomannan carbon microsphere heavy metal adsorption material, which comprises the steps of: (1) adding 0.5-1 weight part of konjac glucomannan into 30-50 weight parts of ultrapure water , stirring, reacting the stirred turbid liquid at 160-200° C. for 8-16 h, centrifuging the reaction liquid at 10,000 r/min for 20 min, washing the obtained solid with ethanol for 3-5 times, and drying to obtain carbon microspheres; (2) Adjust the pH of the aqueous alcohol solution to 4.5 with an acid solution with a volume fraction of 1 to 5%, add a silane coupling agent solution with a volume fraction of 1 to 3% into the aqueous alcohol solution and shake for 2 hours to obtain a modified solution; (3) take 3 ~15 parts by weight of carbon microspheres are added to 100 parts by weight of the modified solution, shaken for 3~5 hours, filtered, and the filter cake is dried at 65°C. The dried filter cake is washed with ethanol and water for 3 to 5 times, vacuum and drying to prepare the modified konjac glucomannan carbon microsphere adsorption material. The invention overcomes the disadvantages of the existing heavy metal wastewater adsorption materials such as difficult process and harsh production conditions, and prepares the heavy metal adsorption material by adopting a simple and easy-to-operate process.

Description

一种改性魔芋葡甘聚糖碳微球重金属吸附材料的制备方法A kind of preparation method of modified konjac glucomannan carbon microsphere heavy metal adsorption material

技术领域technical field

本发明属于植物化学和吸附科学领域,具体涉及魔芋葡甘聚糖碳微球重金属吸附材料的制备方法。The invention belongs to the field of phytochemistry and adsorption science, and in particular relates to a preparation method of konjac glucomannan carbon microsphere heavy metal adsorption material.

背景技术Background technique

重金属离子主要来自于矿山冶炼、机械加工、电镀及,石油化工等行业,这些行业产生的废水大都被直接排放到湖泊、河流、海洋,这不仅污染了水环境,使水质迅速恶化,且随着工业的发展,其污水排放量逐年升高,水污染尤其是水中重金属污染严重已成为不争的事实,严重危害各类生物包括人类的生存。近年来,重金属污染对人类身体健康及生存环境的威胁已引起各国科学家的的广泛关注,使得重金属废水处理技术已得到了飞速发展。处理重金属废水的方法多样,大体可以归纳为:化学法、物理法、生物法。但化学及物理方法由于处理效果不理想、费用昂贵等原因,限制了它们自身的应用前景。相对于前两种的诸多弊端,生物法凭其对低浓度的重金属废水有很好的处理效果、费用低廉、废料易处理等有优点,现今成为水处理研究领域的热点。近期,国内外很多科研工作者对农林副产品或农业废弃物进行一定的改性,研制出一些不同特性功能的吸附剂。比如木屑、柿子渣、蘑菇根、茶渣等改性后制成吸附剂,但终因其处理加工过程复杂,而没有得到很好的推广。Heavy metal ions mainly come from mining smelting, mechanical processing, electroplating, and petrochemical industries. Most of the wastewater generated by these industries is directly discharged into lakes, rivers, and oceans, which not only pollutes the water environment, but also rapidly deteriorates water quality. With the development of industry, its sewage discharge is increasing year by year. It has become an indisputable fact that water pollution, especially heavy metal pollution in water, seriously endangers the survival of various organisms including human beings. In recent years, the threat of heavy metal pollution to human health and living environment has attracted widespread attention of scientists from various countries, which has led to the rapid development of heavy metal wastewater treatment technology. There are various methods for treating heavy metal wastewater, which can be roughly summarized as: chemical methods, physical methods, and biological methods. However, chemical and physical methods have limited their own application prospects due to unsatisfactory treatment effects and high costs. Compared with the many disadvantages of the first two methods, the biological method has become a hot spot in the field of water treatment research because of its good treatment effect on low-concentration heavy metal wastewater, low cost, and easy waste disposal. Recently, many researchers at home and abroad have modified some agricultural and forestry by-products or agricultural wastes, and developed some adsorbents with different characteristics and functions. For example, wood chips, persimmon residues, mushroom roots, tea residues, etc. are modified to make adsorbents, but they have not been well promoted because of the complicated processing process.

魔芋是一种多年生草木植物,主要分布于东南亚、非洲等地;中国、日本、缅甸、越南、印度尼西亚等国,其中国魔芋产区主要分布在云、贵、川、陕西南部和湖北西部,以四川盆地周围山区的魔芋资源最为丰富。其株高约40~70公分,叶柄粗长似茎,圆柱形,淡绿色,有暗紫色斑,掌状复叶,开紫红色花。地下有球茎,呈扁圆形,直径达25cm以上,营养丰富,其含有魔芋多糖达45%以上,魔芋多糖即魔芋葡甘聚糖,又称KGM,是一种天然的高分子可溶性膳食纤维,具有水溶、增稠、悬浮、凝胶、成膜、粘结、稳定等多种理化性质,由于其粘度高、吸水多、膨胀快等理化性质,使魔芋的加工工艺受到限制,现有魔芋食品中魔芋葡甘聚糖的纯度普遍偏低,人们摄入葡甘聚糖甚少。魔芋葡甘聚糖含有碳、氢、氧元素,且其表面含有多种官能团,如醇羟基,羧基阴离子而易于被改性,能够制成吸附剂,并且其本身也具有吸附重金属离子的性能,吸附效果较好。Konjac is a perennial plant, mainly distributed in Southeast Asia, Africa and other places; in China, Japan, Myanmar, Vietnam, Indonesia and other countries, the konjac production areas in China are mainly distributed in Yunnan, Guizhou, Sichuan, southern Shaanxi and western Hubei. Konjac resources are the most abundant in the mountains around the Sichuan Basin. Its plant height is about 40-70 cm, the petiole is thick and long like a stem, cylindrical, light green, with dark purple spots, palmate compound leaves, and purple-red flowers. There are bulbs in the ground, which are flat and round, with a diameter of more than 25cm. They are rich in nutrients and contain more than 45% of konjac polysaccharides. Konjac polysaccharides are konjac glucomannan, also known as KGM. It has various physical and chemical properties such as water solubility, thickening, suspension, gel, film formation, bonding, and stability. Due to its physical and chemical properties such as high viscosity, high water absorption, and fast expansion, the processing technology of konjac is limited. Existing konjac food The purity of konjac glucomannan is generally low, and people take very little glucomannan. Konjac glucomannan contains carbon, hydrogen, and oxygen elements, and its surface contains a variety of functional groups, such as alcoholic hydroxyl groups and carboxyl anions, which are easy to be modified and can be made into adsorbents, and it also has the ability to adsorb heavy metal ions. The adsorption effect is better.

在专利文献CN102161711A中对魔芋葡甘聚糖进行化学改性制备得到了重金属吸附材料,但是该吸附材料的制备方法复杂,工艺难度大,制作条件苛刻,工业化实现困难。在硕士论文《魔芋葡甘聚糖交联羧甲基改性及其对金属离子的吸附和解吸性能研究》则介绍了一种交联羧甲基改性的吸附材料的制备方法,并研究了其对重金属吸附性能,此吸附材料制备方案复杂,条件难以控制,并且所得魔芋葡甘聚糖改性产物取代度不是很高。In the patent document CN102161711A, konjac glucomannan is chemically modified to prepare a heavy metal adsorption material, but the preparation method of the adsorption material is complicated, the process is difficult, the production conditions are harsh, and industrialization is difficult. In the master's thesis "Konjac Glucomannan Cross-linked Carboxymethyl Modification and Its Adsorption and Desorption Properties of Metal Ions", a preparation method of cross-linked carboxymethyl modified adsorption material was introduced, and the research was carried out. Its adsorption performance on heavy metals, the preparation scheme of this adsorption material is complex, the conditions are difficult to control, and the degree of substitution of the obtained konjac glucomannan modified product is not very high.

发明内容Contents of the invention

作为各种广泛且细致的研究和实验的结果,本发明的发明人已经发现,对魔芋葡甘聚糖进行碳化和改性处理,碳化处理可使魔芋葡甘糖成微纳米球,改性处理使魔芋葡甘聚糖的吸附性能得以大幅提高。基于这种发现,完成了本发明。As a result of various extensive and meticulous studies and experiments, the inventors of the present invention have found that konjac glucomannan is subjected to carbonization and modification treatment. The adsorption performance of konjac glucomannan can be greatly improved. Based on this finding, the present invention has been accomplished.

本发明的一个目的是解决至少上述问题和/或缺陷,并提供至少后面将说明的优点。An object of the present invention is to solve at least the above problems and/or disadvantages and to provide at least the advantages as will be described hereinafter.

本发明另一个目的是提供一种改性魔芋葡甘聚糖碳微球重金属吸附材料的制备方法,通过碳化处理可使魔芋葡甘糖成微纳米球,通过硅烷偶联剂的改性处理使魔芋葡甘聚糖的吸附性能得以大幅提高。Another object of the present invention is to provide a preparation method of modified konjac glucomannan carbon microsphere heavy metal adsorption material, through carbonization treatment, konjac glucomanose can be made into micro-nano balls, and through modification treatment of silane coupling agent, the The adsorption performance of konjac glucomannan can be greatly improved.

为了实现根据本发明的这些目的和其它优点,提供了一种改性魔芋葡甘聚糖碳微球重金属吸附材料的制备方法,包括以下步骤:In order to realize these purposes and other advantages according to the present invention, a kind of preparation method of modified konjac glucomannan carbon microsphere heavy metal adsorption material is provided, comprising the following steps:

步骤一、将0.5~1重量份魔芋葡甘聚糖加入30~50重量份超纯水中,搅拌得到胶黏状浊液,在160~200℃下,将胶黏状浊液在水热反应釜中加热8~16h,然后将反应液在10000r/min的转速下离心20min,离心得到的固体用乙醇清洗3~5次,然后在50~80℃下真空干燥12~24h,得到魔芋葡甘聚糖碳微球;Step 1: Add 0.5-1 part by weight of konjac glucomannan into 30-50 parts by weight of ultra-pure water, stir to obtain a viscous turbid liquid, and place the viscous turbid liquid in a hydrothermal reaction at 160-200°C Heating in the kettle for 8-16 hours, then centrifuging the reaction solution at a speed of 10,000r/min for 20 minutes, washing the centrifuged solid with ethanol for 3-5 times, and then vacuum-drying at 50-80°C for 12-24 hours to obtain konjac glucan Polysaccharide carbon microspheres;

步骤二、用体积分数为1~5%的酸溶液调节醇水溶液的pH至4.5,将体积分数为1~3%的硅烷偶联剂溶液加入醇水溶液中震荡2h,得到改性液;所述醇水溶液中醇与水的体积比为1∶1,所述醇水溶液与硅烷偶联剂溶液的体积比是1∶0.3~0.5;Step 2, using an acid solution with a volume fraction of 1 to 5% to adjust the pH of the alcohol aqueous solution to 4.5, adding a silane coupling agent solution with a volume fraction of 1 to 3% into the alcohol aqueous solution and shaking for 2 hours to obtain a modified solution; The volume ratio of alcohol to water in the alcohol aqueous solution is 1:1, and the volume ratio of the alcohol aqueous solution to the silane coupling agent solution is 1:0.3~0.5;

步骤三、取3~15重量份步骤一制备的魔芋葡甘聚糖碳微球加入100重量份步骤二制备的改性液中,震荡3~5h,过滤,滤饼在65℃下烘干,将烘干后的滤饼用体积比为1:1的乙醇和水洗涤3~5次,50~80℃下真空干燥12~24h,制得改性魔芋葡甘聚糖碳微球吸附材料。Step 3: Add 3 to 15 parts by weight of the konjac glucomannan carbon microspheres prepared in step 1 to 100 parts by weight of the modified liquid prepared in step 2, shake for 3 to 5 hours, filter, and dry the filter cake at 65°C. The dried filter cake is washed 3 to 5 times with ethanol and water at a volume ratio of 1:1, and vacuum dried at 50 to 80° C. for 12 to 24 hours to prepare the modified konjac glucomannan carbon microsphere adsorption material.

优选的是,采用醋酸、硫酸、硝酸中的一种代替步骤二中酸溶液中的盐酸。Preferably, one of acetic acid, sulfuric acid and nitric acid is used to replace the hydrochloric acid in the acid solution in step two.

优选的是,采用乙醇代替步骤二中醇水溶液中的甲醇。Preferably, ethanol is used to replace the methanol in the alcohol aqueous solution in step 2.

优选的是,采用3-氨丙基三甲氧基硅烷、乙烯基三甲氧基硅烷、乙烯基三乙氧基硅烷中的一种代替步骤二中的硅烷偶联剂3-巯丙基三乙氧基硅烷。Preferably, one of 3-aminopropyltrimethoxysilane, vinyltrimethoxysilane and vinyltriethoxysilane is used to replace the silane coupling agent 3-mercaptopropyltriethoxy in step two base silane.

本发明至少包括以下有益效果:该制备方法克服现有技术处理重金属废水的吸附材料存在的成本高、加工复杂、工艺难度大,制作条件苛刻等缺点,采用简单、易操作的工艺制备了重金属吸附材料,本发明选用来源丰富、价格低廉的魔芋葡甘聚糖,对其进行碳化和改性处理,碳化处理可使魔芋葡甘聚糖形成微碳球,硅烷偶联剂的改性处理使碳化的魔芋葡甘聚糖的吸附性能得以大幅提高,用于处理重金属离子废水工艺中,可大幅降低重金属离子废水处理成本,具有经济价值和环保意义。The invention at least includes the following beneficial effects: the preparation method overcomes the disadvantages of high cost, complex processing, difficult process, and harsh production conditions of the prior art adsorption materials for treating heavy metal wastewater, and adopts a simple and easy-to-operate process to prepare heavy metal adsorption Material, the present invention selects konjac glucomannan with rich sources and low price, and carries out carbonization and modification treatment to it, carbonization treatment can make konjac glucomannan form micro carbon spheres, modification treatment of silane coupling agent can make The adsorption performance of konjac glucomannan can be greatly improved, and it can be used in the process of treating heavy metal ion wastewater, which can greatly reduce the cost of heavy metal ion wastewater treatment, and has economic value and environmental protection significance.

本发明的其它优点、目标和特征将部分通过下面的说明体现,部分还将通过对本发明的研究和实践而为本领域的技术人员所理解。Other advantages, objectives and features of the present invention will partly be embodied through the following descriptions, and partly will be understood by those skilled in the art through the study and practice of the present invention.

附图说明:Description of drawings:

图1为本发明实施例1制备的改性魔芋葡甘聚糖碳微球的扫描电镜图。Figure 1 is a scanning electron micrograph of modified konjac glucomannan carbon microspheres prepared in Example 1 of the present invention.

具体实施方式:detailed description:

下面结合实施例及附图对本发明做进一步的详细说明,以令本领域技术人员参照说明书文字能够据以实施。The present invention will be described in further detail below in conjunction with the embodiments and accompanying drawings, so that those skilled in the art can implement it with reference to the description.

应当理解,本文所使用的诸如“具有”、“包含”以及“包括”术语并不配出一个或多个其它元件或其组合的存在或添加。It should be understood that terms such as "having", "comprising" and "including" as used herein do not entail the presence or addition of one or more other elements or combinations thereof.

实施例1:Example 1:

步骤一、将0.7g魔芋葡甘聚糖加入40g超纯水中,搅拌得到胶黏状浊液,在180℃下,将胶黏状浊液在水热反应釜中加热12h,然后将反应液在10000r/min的转速下离心20min,离心得到的固体用乙醇清洗3次,然后在60℃下真空干燥24h,得到魔芋葡甘聚糖碳微球;Step 1. Add 0.7g of konjac glucomannan to 40g of ultrapure water, stir to obtain a sticky cloudy liquid, heat the sticky cloudy liquid in a hydrothermal reactor at 180°C for 12 hours, and then dissolve the reaction solution Centrifuge at a speed of 10000r/min for 20min, wash the centrifuged solid with ethanol for 3 times, and then vacuum-dry at 60°C for 24h to obtain konjac glucomannan carbon microspheres;

步骤二、用体积分数为5%的醋酸溶液调节100mL乙醇水溶液的pH至4.5,将体积分数为1.5%的3-巯丙基三乙氧基硅烷溶液30mL加入乙醇水溶液中震荡2h,得到改性液;所述乙醇水溶液中醇与水的体积比为1∶1;Step 2: Adjust the pH of 100 mL of aqueous ethanol solution to 4.5 with acetic acid solution with a volume fraction of 5%, add 30 mL of 3-mercaptopropyltriethoxysilane solution with a volume fraction of 1.5% into the aqueous ethanol solution and shake for 2 hours to obtain a modified Liquid; The volume ratio of alcohol and water in the ethanol aqueous solution is 1:1;

步骤三、取5g步骤一制备的魔芋葡甘聚糖碳微球加入100g步骤二制备的改性液中,震荡3h,过滤,滤饼在65℃下烘干,将烘干后的滤饼用体积比为1:1的乙醇和水洗涤3次,50℃下真空干燥24h,制得改性魔芋葡甘聚糖碳微球吸附材料。Step 3: Take 5g of konjac glucomannan carbon microspheres prepared in step 1 and add them to 100g of the modified liquid prepared in step 2, shake for 3 hours, filter, and dry the filter cake at 65°C, and use the dried filter cake with The modified konjac glucomannan carbon microspheres adsorption material was obtained by washing three times with ethanol and water at a volume ratio of 1:1, and drying in vacuum at 50°C for 24 hours.

图1所示为本实施例制备的改性魔芋葡甘聚糖碳微球的扫面电镜图。Fig. 1 shows the scanning electron micrograph of the modified konjac glucomannan carbon microspheres prepared in this example.

实施例2:Example 2:

步骤一、将0.5g魔芋葡甘聚糖加入30g超纯水中,搅拌得到胶黏状浊液,在160℃下,将胶黏状浊液在水热反应釜中加热8h,然后将反应液在10000r/min的转速下离心20min,离心得到的固体用乙醇清洗3次,然后在50℃下真空干燥24h,得到魔芋葡甘聚糖碳微球;Step 1. Add 0.5g of konjac glucomannan to 30g of ultrapure water, stir to obtain a viscous turbid solution, heat the viscous turbid solution in a hydrothermal reactor at 160°C for 8 hours, and then dissolve the reaction solution Centrifuge at a speed of 10000r/min for 20min, wash the centrifuged solid with ethanol for 3 times, and then vacuum-dry it at 50°C for 24h to obtain konjac glucomannan carbon microspheres;

步骤二、用体积分数为1%的醋酸溶液调节100mL乙醇水溶液的pH至4.5,将体积分数为1%的3-巯丙基三乙氧基硅烷溶液30mL加入乙醇水溶液中震荡2h,得到改性液;所述乙醇水溶液中醇与水的体积比为1:1;Step 2: Adjust the pH of 100 mL of aqueous ethanol solution to 4.5 with 1% acetic acid solution by volume fraction, add 30 mL of 3-mercaptopropyltriethoxysilane solution with 1% volume fraction into the aqueous ethanol solution and shake for 2 hours to obtain modified liquid; the volume ratio of alcohol to water in the ethanol aqueous solution is 1:1;

步骤三、取3g步骤一制备的魔芋葡甘聚糖碳微球加入100g步骤二制备的改性液中,震荡3h,过滤,滤饼在65℃下烘干,将烘干后的滤饼用体积比为1:1的乙醇和水洗涤3次,50℃下真空干燥24h,制得改性魔芋葡甘聚糖碳微球吸附材料。Step 3: Take 3g of konjac glucomannan carbon microspheres prepared in step 1 and add them to 100g of the modified liquid prepared in step 2, shake for 3 hours, filter, and dry the filter cake at 65°C, and use the dried filter cake with The modified konjac glucomannan carbon microspheres adsorption material was obtained by washing three times with ethanol and water at a volume ratio of 1:1, and drying in vacuum at 50°C for 24 hours.

实施例3:Example 3:

步骤一、将1g魔芋葡甘聚糖加入50g超纯水中,搅拌得到胶黏状浊液,在200℃下,将胶黏状浊液在水热反应釜中加热16h,然后将反应液在10000r/min的转速下离心20min,离心得到的固体用乙醇清洗5次,然后在80℃下真空干燥12h,得到魔芋葡甘聚糖碳微球;Step 1. Add 1g of konjac glucomannan to 50g of ultrapure water, stir to obtain a viscous turbid liquid, heat the viscous turbid liquid in a hydrothermal reactor at 200°C for 16 hours, and then place the reaction solution in Centrifuge at a speed of 10000r/min for 20min, wash the centrifuged solid with ethanol for 5 times, and then vacuum-dry at 80°C for 12h to obtain konjac glucomannan carbon microspheres;

步骤二、用体积分数为5%的醋酸溶液调节100mL乙醇水溶液的pH至4.5,将体积分数为3%的3-巯丙基三乙氧基硅烷溶液50mL加入乙醇水溶液中震荡2h,得到改性液;所述乙醇水溶液中醇与水的体积比为1:1;Step 2. Adjust the pH of 100 mL of aqueous ethanol solution to 4.5 with 5% acetic acid solution by volume fraction, add 50 mL of 3-mercaptopropyltriethoxysilane solution with 3% volume fraction into the aqueous ethanol solution and shake for 2 hours to obtain modified liquid; the volume ratio of alcohol to water in the ethanol aqueous solution is 1:1;

步骤三、取15g步骤一制备的魔芋葡甘聚糖碳微球加入100g步骤二制备的改性液中,震荡5h,过滤,滤饼在65℃下烘干,将烘干后的滤饼用体积比为1:1的乙醇和水洗涤5次,80℃下真空干燥12h,制得改性魔芋葡甘聚糖碳微球吸附材料。Step 3: Add 15g of the konjac glucomannan carbon microspheres prepared in step 1 to 100g of the modified solution prepared in step 2, shake for 5 hours, filter, and dry the filter cake at 65°C, and use the dried filter cake with The modified konjac glucomannan carbon microspheres adsorption material was obtained by washing five times with ethanol and water at a volume ratio of 1:1, and drying in vacuum at 80°C for 12 hours.

实施例4:Example 4:

步骤一、将0.8g魔芋葡甘聚糖加入40g超纯水中,搅拌得到胶黏状浊液,在180℃下,将胶黏状浊液在水热反应釜中加热12h,然后将反应液在10000r/min的转速下离心20min,离心得到的固体用乙醇清洗4次,然后在70℃下真空干燥20h,得到魔芋葡甘聚糖碳微球;Step 1. Add 0.8g of konjac glucomannan to 40g of ultrapure water, stir to obtain a sticky cloudy liquid, heat the sticky cloudy liquid in a hydrothermal reactor at 180°C for 12 hours, and then dissolve the reaction solution Centrifuge at a speed of 10000r/min for 20min, wash the centrifuged solid with ethanol for 4 times, and then vacuum-dry it at 70°C for 20h to obtain konjac glucomannan carbon microspheres;

步骤二、用体积分数为3%的醋酸溶液调节100mL乙醇水溶液的pH至4.5,将体积分数为2%的3-巯丙基三乙氧基硅烷溶液40mL加入乙醇水溶液中震荡2h,得到改性液;所述乙醇水溶液中醇与水的体积比为1:1;Step 2: Adjust the pH of 100 mL of aqueous ethanol solution to 4.5 with 3% acetic acid solution by volume fraction, add 40 mL of 3-mercaptopropyltriethoxysilane solution with 2% volume fraction into the aqueous ethanol solution and shake for 2 hours to obtain modified liquid; the volume ratio of alcohol to water in the ethanol aqueous solution is 1:1;

步骤三、取10g步骤一制备的魔芋葡甘聚糖碳微球加入100g步骤二制备的改性液中,震荡4h,过滤,滤饼在65℃下烘干,将烘干后的滤饼用体积比为1:1的乙醇和水洗涤4次,60℃下真空干燥18h,制得改性魔芋葡甘聚糖碳微球吸附材料。Step 3: Add 10 g of konjac glucomannan carbon microspheres prepared in step 1 to 100 g of the modified solution prepared in step 2, shake for 4 hours, filter, and dry the filter cake at 65 ° C. Use the dried filter cake The modified konjac glucomannan carbon microspheres adsorption material was obtained by washing four times with ethanol and water at a volume ratio of 1:1, and drying in vacuum at 60°C for 18 hours.

为了说明本发明的效果,发明人提供比较实验如下:In order to illustrate the effect of the present invention, the inventor provides comparative experiments as follows:

比较例1:Comparative example 1:

步骤一、将0.2g魔芋葡甘聚糖加入30g超纯水中,搅拌得到胶黏状浊液,在160℃下,将胶黏状浊液在水热反应釜中加热8h,然后将反应液在10000r/min的转速下离心20min,离心得到的固体用乙醇清洗3次,然后在50℃下真空干燥24h,得到魔芋葡甘聚糖碳微球;Step 1. Add 0.2g of konjac glucomannan to 30g of ultrapure water, stir to obtain a viscous turbid solution, heat the viscous turbid solution in a hydrothermal reactor at 160°C for 8 hours, and then dissolve the reaction solution Centrifuge at a speed of 10000r/min for 20min, wash the centrifuged solid with ethanol for 3 times, and then vacuum-dry it at 50°C for 24h to obtain konjac glucomannan carbon microspheres;

步骤二、用体积分数为1%的醋酸溶液调节100mL乙醇水溶液的pH至4.5,将体积分数为1%的3-巯丙基三乙氧基硅烷溶液30mL加入乙醇水溶液中震荡2h,得到改性液;所述乙醇水溶液中醇与水的体积比为1:1;Step 2: Adjust the pH of 100 mL of aqueous ethanol solution to 4.5 with 1% acetic acid solution by volume fraction, add 30 mL of 3-mercaptopropyltriethoxysilane solution with 1% volume fraction into the aqueous ethanol solution and shake for 2 hours to obtain modified liquid; the volume ratio of alcohol to water in the ethanol aqueous solution is 1:1;

步骤三、取3g步骤一制备的魔芋葡甘聚糖碳微球加入100g步骤二制备的改性液中,震荡3h,过滤,滤饼在65℃下烘干,将烘干后的滤饼用体积比为1:1的乙醇和水洗涤3次,50℃下真空干燥24h,制得改性魔芋葡甘聚糖碳微球吸附材料。Step 3: Take 3g of konjac glucomannan carbon microspheres prepared in step 1 and add them to 100g of the modified liquid prepared in step 2, shake for 3 hours, filter, and dry the filter cake at 65°C, and use the dried filter cake with The modified konjac glucomannan carbon microspheres adsorption material was obtained by washing three times with ethanol and water at a volume ratio of 1:1, and drying in vacuum at 50°C for 24 hours.

比较例2:Comparative example 2:

步骤一、将2g魔芋葡甘聚糖加入30g超纯水中,搅拌得到胶黏状浊液,在160℃下,将胶黏状浊液在水热反应釜中加热8h,然后将反应液在10000r/min的转速下离心20min,离心得到的固体用乙醇清洗3次,然后在50℃下真空干燥24h,得到魔芋葡甘聚糖碳微球;Step 1. Add 2g of konjac glucomannan to 30g of ultrapure water, stir to obtain a viscous turbid liquid, heat the viscous turbid liquid in a hydrothermal reactor at 160°C for 8 hours, and then put the reaction liquid in Centrifuge at a speed of 10000r/min for 20min, wash the centrifuged solid with ethanol for 3 times, and then vacuum dry at 50°C for 24h to obtain konjac glucomannan carbon microspheres;

步骤二、用体积分数为1%的醋酸溶液调节100mL乙醇水溶液的pH至4.5,将体积分数为1%的3-巯丙基三乙氧基硅烷溶液30mL加入乙醇水溶液中震荡2h,得到改性液;所述乙醇水溶液中醇与水的体积比为1:1;Step 2: Adjust the pH of 100 mL of aqueous ethanol solution to 4.5 with 1% acetic acid solution by volume fraction, add 30 mL of 3-mercaptopropyltriethoxysilane solution with 1% volume fraction into the aqueous ethanol solution and shake for 2 hours to obtain modified liquid; the volume ratio of alcohol to water in the ethanol aqueous solution is 1:1;

步骤三、取3g步骤一制备的魔芋葡甘聚糖碳微球加入100g步骤二制备的改性液中,震荡3h,过滤,滤饼在65℃下烘干,将烘干后的滤饼用体积比为1:1的乙醇和水洗涤3次,50℃下真空干燥24h,制得改性魔芋葡甘聚糖碳微球吸附材料。Step 3: Take 3g of konjac glucomannan carbon microspheres prepared in step 1 and add them to 100g of the modified liquid prepared in step 2, shake for 3 hours, filter, and dry the filter cake at 65°C, and use the dried filter cake with The modified konjac glucomannan carbon microspheres adsorption material was obtained by washing three times with ethanol and water at a volume ratio of 1:1, and drying in vacuum at 50°C for 24 hours.

比较例3:Comparative example 3:

步骤一、将0.5g魔芋葡甘聚糖加入30g超纯水中,搅拌得到胶黏状浊液,在100℃下,将胶黏状浊液在水热反应釜中加热8h,然后将反应液在10000r/min的转速下离心20min,离心得到的固体用乙醇清洗3次,然后在50℃下真空干燥24h,得到魔芋葡甘聚糖碳微球;Step 1. Add 0.5g of konjac glucomannan to 30g of ultrapure water, stir to obtain a viscous turbid solution, heat the viscous turbid solution in a hydrothermal reactor at 100°C for 8 hours, and then dissolve the reaction solution Centrifuge at a speed of 10000r/min for 20min, wash the centrifuged solid with ethanol for 3 times, and then vacuum-dry it at 50°C for 24h to obtain konjac glucomannan carbon microspheres;

步骤二、用体积分数为1%的醋酸溶液调节100mL乙醇水溶液的pH至4.5,将体积分数为1%的3-巯丙基三乙氧基硅烷溶液30mL加入乙醇水溶液中震荡2h,得到改性液;所述乙醇水溶液中醇与水的体积比为1:1;Step 2: Adjust the pH of 100 mL of aqueous ethanol solution to 4.5 with 1% acetic acid solution by volume fraction, add 30 mL of 3-mercaptopropyltriethoxysilane solution with 1% volume fraction into the aqueous ethanol solution and shake for 2 hours to obtain modified liquid; the volume ratio of alcohol to water in the ethanol aqueous solution is 1:1;

步骤三、取3g步骤一制备的魔芋葡甘聚糖碳微球加入100g步骤二制备的改性液中,震荡3h,过滤,滤饼在65℃下烘干,将烘干后的滤饼用体积比为1:1的乙醇和水洗涤3次,50℃下真空干燥24h,制得改性魔芋葡甘聚糖碳微球吸附材料。Step 3: Take 3g of konjac glucomannan carbon microspheres prepared in step 1 and add them to 100g of the modified liquid prepared in step 2, shake for 3 hours, filter, and dry the filter cake at 65°C, and use the dried filter cake with The modified konjac glucomannan carbon microspheres adsorption material was obtained by washing three times with ethanol and water at a volume ratio of 1:1, and drying in vacuum at 50°C for 24 hours.

比较例4:Comparative example 4:

步骤一、将1g魔芋葡甘聚糖加入50g超纯水中,搅拌得到胶黏状浊液,在200℃下,将胶黏状浊液在水热反应釜中加热16h,然后将反应液在10000r/min的转速下离心20min,离心得到的固体用乙醇清洗5次,然后在80℃下真空干燥12h,得到魔芋葡甘聚糖碳微球;Step 1. Add 1g of konjac glucomannan to 50g of ultrapure water, stir to obtain a viscous turbid liquid, heat the viscous turbid liquid in a hydrothermal reactor at 200°C for 16 hours, and then place the reaction solution in Centrifuge at a speed of 10000r/min for 20min, wash the centrifuged solid with ethanol for 5 times, and then vacuum-dry at 80°C for 12h to obtain konjac glucomannan carbon microspheres;

步骤二、用体积分数为5%的醋酸溶液调节100mL乙醇水溶液的pH至4.5,将体积分数为3%的3-巯丙基三乙氧基硅烷溶液50mL加入乙醇水溶液中震荡2h,得到改性液;所述乙醇水溶液中醇与水的体积比为1:1;Step 2. Adjust the pH of 100 mL of aqueous ethanol solution to 4.5 with 5% acetic acid solution by volume fraction, add 50 mL of 3-mercaptopropyltriethoxysilane solution with 3% volume fraction into the aqueous ethanol solution and shake for 2 hours to obtain modified liquid; the volume ratio of alcohol to water in the ethanol aqueous solution is 1:1;

步骤三、取1g步骤一制备的魔芋葡甘聚糖碳微球加入100g步骤二制备的改性液中,震荡5h,过滤,滤饼在65℃下烘干,将烘干后的滤饼用体积比为1:1的乙醇和水洗涤5次,80℃下真空干燥12h,制得改性魔芋葡甘聚糖碳微球吸附材料。Step 3: Add 1 g of konjac glucomannan carbon microspheres prepared in step 1 to 100 g of the modified liquid prepared in step 2, shake for 5 hours, filter, and dry the filter cake at 65 ° C. Use the dried filter cake The modified konjac glucomannan carbon microspheres adsorption material was obtained by washing five times with ethanol and water at a volume ratio of 1:1, and drying in vacuum at 80°C for 12 hours.

比较例5:Comparative example 5:

步骤一、将1g魔芋葡甘聚糖加入50g超纯水中,搅拌得到胶黏状浊液,在200℃下,将胶黏状浊液在水热反应釜中加热16h,然后将反应液在10000r/min的转速下离心20min,离心得到的固体用乙醇清洗5次,然后在80℃下真空干燥12h,得到魔芋葡甘聚糖碳微球;Step 1. Add 1g of konjac glucomannan to 50g of ultrapure water, stir to obtain a viscous turbid liquid, heat the viscous turbid liquid in a hydrothermal reactor at 200°C for 16 hours, and then place the reaction solution in Centrifuge at a speed of 10000r/min for 20min, wash the centrifuged solid with ethanol for 5 times, and then vacuum-dry at 80°C for 12h to obtain konjac glucomannan carbon microspheres;

步骤二、用体积分数为5%的醋酸溶液调节100mL乙醇水溶液的pH至4.5,将体积分数为3%的3-巯丙基三乙氧基硅烷溶液50mL加入乙醇水溶液中震荡2h,得到改性液;所述乙醇水溶液中醇与水的体积比为1:1;Step 2. Adjust the pH of 100 mL of aqueous ethanol solution to 4.5 with 5% acetic acid solution by volume fraction, add 50 mL of 3-mercaptopropyltriethoxysilane solution with 3% volume fraction into the aqueous ethanol solution and shake for 2 hours to obtain modified liquid; the volume ratio of alcohol to water in the ethanol aqueous solution is 1:1;

步骤三、取20g步骤一制备的魔芋葡甘聚糖碳微球加入100g步骤二制备的改性液中,震荡5h,过滤,滤饼在65℃下烘干,将烘干后的滤饼用体积比为1:1的乙醇和水洗涤5次,80℃下真空干燥12h,制得改性魔芋葡甘聚糖碳微球吸附材料。Step 3: Add 20 g of konjac glucomannan carbon microspheres prepared in step 1 to 100 g of the modified solution prepared in step 2, shake for 5 hours, filter, and dry the filter cake at 65 ° C. Use the dried filter cake with The modified konjac glucomannan carbon microspheres adsorption material was obtained by washing five times with ethanol and water at a volume ratio of 1:1, and drying in vacuum at 80°C for 12 hours.

比较例6:Comparative example 6:

步骤一、将0.8g魔芋葡甘聚糖加入40g超纯水中,搅拌得到胶黏状浊液,在180℃下,将胶黏状浊液在水热反应釜中加热12h,然后将反应液在10000r/min的转速下离心20min,离心得到的固体用乙醇清洗4次,然后在70℃下真空干燥20h,得到魔芋葡甘聚糖碳微球;Step 1. Add 0.8g of konjac glucomannan to 40g of ultrapure water, stir to obtain a sticky cloudy liquid, heat the sticky cloudy liquid in a hydrothermal reactor at 180°C for 12 hours, and then dissolve the reaction solution Centrifuge at a speed of 10000r/min for 20min, wash the centrifuged solid with ethanol for 4 times, and then vacuum-dry it at 70°C for 20h to obtain konjac glucomannan carbon microspheres;

步骤二、用体积分数为3%的醋酸溶液调节100mL乙醇水溶液的pH至4.5,将体积分数为0.5%的3-巯丙基三乙氧基硅烷溶液40mL加入乙醇水溶液中震荡2h,得到改性液;所述乙醇水溶液中醇与水的体积比为1:1;Step 2. Adjust the pH of 100 mL of ethanol aqueous solution to 4.5 with 3% acetic acid solution by volume fraction, add 40 mL of 3-mercaptopropyltriethoxysilane solution with 0.5% volume fraction into the aqueous ethanol solution and shake for 2 hours to obtain modified liquid; the volume ratio of alcohol to water in the ethanol aqueous solution is 1:1;

步骤三、取10g步骤一制备的魔芋葡甘聚糖碳微球加入100g步骤二制备的改性液中,震荡4h,过滤,滤饼在65℃下烘干,将烘干后的滤饼用体积比为1:1的乙醇和水洗涤4次,60℃下真空干燥18h,制得改性魔芋葡甘聚糖碳微球吸附材料。Step 3: Add 10 g of konjac glucomannan carbon microspheres prepared in step 1 to 100 g of the modified solution prepared in step 2, shake for 4 hours, filter, and dry the filter cake at 65 ° C. Use the dried filter cake The modified konjac glucomannan carbon microspheres adsorption material was obtained by washing four times with ethanol and water at a volume ratio of 1:1, and drying in vacuum at 60°C for 18 hours.

比较例7:Comparative example 7:

步骤一、将0.8g魔芋葡甘聚糖加入40g超纯水中,搅拌得到胶黏状浊液,在180℃下,将胶黏状浊液在水热反应釜中加热12h,然后将反应液在10000r/min的转速下离心20min,离心得到的固体用乙醇清洗4次,然后在70℃下真空干燥20h,得到魔芋葡甘聚糖碳微球;Step 1. Add 0.8g of konjac glucomannan to 40g of ultrapure water, stir to obtain a sticky cloudy liquid, heat the sticky cloudy liquid in a hydrothermal reactor at 180°C for 12 hours, and then dissolve the reaction solution Centrifuge at a speed of 10000r/min for 20min, wash the centrifuged solid with ethanol for 4 times, and then vacuum-dry it at 70°C for 20h to obtain konjac glucomannan carbon microspheres;

步骤二、用体积分数为3%的醋酸溶液调节100mL乙醇水溶液的pH至4.5,将体积分数为5%的3-巯丙基三乙氧基硅烷溶液40mL加入乙醇水溶液中震荡2h,得到改性液;所述乙醇水溶液中醇与水的体积比为1:1;Step 2: Adjust the pH of 100 mL of aqueous ethanol solution to 4.5 with 3% acetic acid solution by volume fraction, add 40 mL of 3-mercaptopropyltriethoxysilane solution with 5% volume fraction into the aqueous ethanol solution and shake for 2 hours to obtain the modified liquid; the volume ratio of alcohol to water in the ethanol aqueous solution is 1:1;

步骤三、取10g步骤一制备的魔芋葡甘聚糖碳微球加入100g步骤二制备的改性液中,震荡4h,过滤,滤饼在65℃下烘干,将烘干后的滤饼用体积比为1:1的乙醇和水洗涤4次,60℃下真空干燥18h,制得改性魔芋葡甘聚糖碳微球吸附材料。Step 3: Add 10 g of konjac glucomannan carbon microspheres prepared in step 1 to 100 g of the modified solution prepared in step 2, shake for 4 hours, filter, and dry the filter cake at 65 ° C. Use the dried filter cake The modified konjac glucomannan carbon microspheres adsorption material was obtained by washing four times with ethanol and water at a volume ratio of 1:1, and drying in vacuum at 60°C for 18 hours.

采用以上实施例1~4和对比例1~7制备的吸附材料分别对重金属铅离子和镉离子进行静态吸附研究。The adsorption materials prepared in Examples 1-4 and Comparative Examples 1-7 above were used for static adsorption research on heavy metal lead ions and cadmium ions, respectively.

分别取上述实施例1~4和对比例1~7制备的吸附材料20mg与100mL50mg/L的铅离子溶液混合,调节pH为4,置于摇床振荡2h,转速为130rpm,吸附温度为25℃;Mix 20 mg of the adsorption material prepared in the above-mentioned Examples 1-4 and Comparative Examples 1-7 with 100 mL of 50 mg/L lead ion solution, adjust the pH to 4, place it on a shaker for 2 h, the rotation speed is 130 rpm, and the adsorption temperature is 25 °C ;

分别取上述实施例1~4和对比例1~7制备的吸附材料20mg与100mL40mg/L的镉离子溶液混合,调节pH为4,置于摇床振荡2h,转速为130rpm,吸附温度为25℃;Take 20 mg of the adsorption materials prepared in the above-mentioned Examples 1-4 and Comparative Examples 1-7 and mix them with 100 mL of 40 mg/L cadmium ion solution, adjust the pH to 4, place on a shaking table for 2 h, the rotation speed is 130 rpm, and the adsorption temperature is 25 °C ;

对两种离子的吸附效果如表1所示,重金属离子的去除率由以下公式(1)计算,The adsorption effects of the two ions are shown in Table 1, and the removal rate of heavy metal ions is calculated by the following formula (1),

去除率=(Co-Cm)/Co×100%(1)Removal rate = (C o -C m )/C o × 100% (1)

其中,Co为吸附前重金属离子的浓度,Cm为吸附后重金属离子的浓度。Among them, C o is the concentration of heavy metal ions before adsorption, and C m is the concentration of heavy metal ions after adsorption.

吸附材料的吸附量由以下公式(2)计算,The adsorption capacity of the adsorbent material is calculated by the following formula (2),

吸附量=(Co-Ce)V/m(2)Adsorption capacity=(C o -C e )V/m(2)

其中,Co为吸附前重金属离子的浓度,Ce为吸附平衡后重金属离子的浓度,V为加入重金属溶液的体积,m为加入的吸附材料的质量。Among them, C o is the concentration of heavy metal ions before adsorption, C e is the concentration of heavy metal ions after adsorption equilibrium, V is the volume of heavy metal solution added, and m is the mass of adsorption material added.

表1Table 1

从表1可知,实施例1~4由于采用了本发明所述比例范围内的原料和工艺参数,其对重金属铅离子和镉离子溶液的吸附效果较好,去除率均大于94%,对铅离子的吸附量均大于100mg/g,对镉离子的吸附量均大于50mg/g。As can be seen from Table 1, embodiment 1~4 owing to have adopted raw material and process parameter in the ratio scope of the present invention, it is better to the adsorption effect of heavy metal lead ion and cadmium ion solution, and removal rate is all greater than 94%, to lead The adsorption capacity of ions is greater than 100mg/g, and the adsorption capacity of cadmium ions is greater than 50mg/g.

而对比例中所采用的原料和工艺参数的比例不在本发明所述的比例范围之内,因此对重金属铅离子和镉离子溶液的吸附效果较差,去除率均小于90%,对铅离子的吸附量均小于80mg/g,对镉离子的吸附量均小于40mg/g。And the raw material that adopts in the comparative example and the ratio of process parameter are not within the ratio scope described in the present invention, therefore the adsorption effect to heavy metal lead ion and cadmium ion solution is relatively poor, removal rate is all less than 90%, to lead ion The adsorption capacity is less than 80mg/g, and the adsorption capacity for cadmium ions is less than 40mg/g.

比较例1和比较例2与实施例2相比,区别是比较例1在步骤一添加的魔芋葡甘聚糖的量为0.2g,比较例2在步骤一添加的魔芋葡甘聚糖的量为2g,两者均不在本发明所述的比例范围之内,这将导致魔芋葡甘聚糖碳化后的微球结构不均匀,得到的吸附材料对重金属离子的去除率和吸附量均低于实施例2所制备的吸附材料。Comparative example 1 and comparative example 2 are compared with embodiment 2, and the difference is that the amount of konjac glucomannan added in step 1 of comparative example 1 is 0.2g, and the amount of konjac glucomannan added in step 1 of comparative example 2 It is 2g, both of which are not within the ratio range described in the present invention, which will lead to the inhomogeneous microsphere structure after konjac glucomannan carbonization, and the adsorption material obtained is all lower than the removal rate and adsorption capacity of heavy metal ions. Adsorbent material prepared in Example 2.

比较例3与实施例2相比,区别是比较例3在步骤一中的反应温度为100℃,该反应温度不在本发明所述的反应温度160~200℃内,温度较低,魔芋葡甘聚糖的碳化不够完全,得到的微球的粒径较大,因此吸附材料对重金属离子的去除率和吸附量均低于实施例2所制备的吸附材料。Compared with Example 2, Comparative Example 3 differs in that the reaction temperature in Step 1 of Comparative Example 3 is 100° C., which is not within the reaction temperature of 160 to 200° C. in the present invention, and the temperature is lower. Konjac glucan The carbonization of the polysaccharide is not complete, and the particle size of the obtained microspheres is relatively large, so the removal rate and adsorption capacity of the adsorption material for heavy metal ions are lower than those of the adsorption material prepared in Example 2.

比较例4和比较例5与实施例3相比,区别是比较例4在步骤三添加的魔芋葡甘聚糖碳微球的量为1g,比较例5在步骤一添加的魔芋葡甘聚糖碳微球的量为20g,两者均不在本发明所述的比例范围之内,当魔芋葡甘聚糖碳微球的量低于所述范围时,将导致魔芋葡甘聚糖碳微球被大量的3-巯丙基三乙氧基硅烷所覆盖,这不利于吸附重金属离子,当魔芋葡甘聚糖碳微球的量高于所述范围时,将导致魔芋葡甘聚糖碳微球的改性不完全,不能有效的发挥3-巯丙基三乙氧基硅烷的作用,因此得到的吸附材料对重金属离子的去除率和吸附量均低于实施例3所制备的吸附材料。Comparative example 4 and comparative example 5 are compared with embodiment 3, and the difference is that the amount of konjac glucomannan carbon microspheres added in step 3 of comparative example 4 is 1g, and the amount of konjac glucomannan added in step 1 of comparative example 5 The amount of carbon microspheres is 20g, both of which are not within the ratio range described in the present invention. When the amount of konjac glucomannan carbon microspheres is lower than the range, it will cause konjac glucomannan carbon microspheres Covered by a large amount of 3-mercaptopropyltriethoxysilane, which is not conducive to the adsorption of heavy metal ions, when the amount of konjac glucomannan carbon microspheres is higher than the stated range, it will cause konjac glucomannan carbon microspheres The modification of the spheres is incomplete and cannot effectively play the role of 3-mercaptopropyltriethoxysilane, so the removal rate and adsorption capacity of the obtained adsorption material for heavy metal ions are lower than those prepared in Example 3.

比较例6和比较例7与实施例4相比,区别是比较例6在步骤二改性液的制备中加入的3-巯丙基三乙氧基硅烷的体积分数为0.5%,比较例7在步骤二改性液的制备中加入的3-巯丙基三乙氧基硅烷的体积分数为5%,两者均不在本发明所述的比例范围1~3%之内,当3-巯丙基三乙氧基硅烷的体积分数低于所述范围时,在步骤三中对魔芋葡甘聚糖碳微球的改性将不完全,不能有效的发挥3-巯丙基三乙氧基硅烷的作用,当3-巯丙基三乙氧基硅烷的体积分数高于所述范围时,在步骤三中魔芋葡甘聚糖碳微球将被大量的3-巯丙基三乙氧基硅烷所覆盖,因此得到的吸附材料对重金属离子的去除率和吸附量均低于实施例4所制备的吸附材料。Compared with Example 4, Comparative Example 6 and Comparative Example 7, the difference is that the volume fraction of 3-mercaptopropyltriethoxysilane added in the preparation of step two modified liquid in Comparative Example 6 is 0.5%, and that of Comparative Example 7 The volume fraction of the 3-mercaptopropyltriethoxysilane added in the preparation of the modified liquid in step 2 is 5%, both of which are not within the proportion range of 1 to 3% described in the present invention. When 3-mercaptopropyltriethoxysilane When the volume fraction of propyltriethoxysilane is lower than the range, the modification of konjac glucomannan carbon microspheres will be incomplete in step 3, and the 3-mercaptopropyltriethoxy group cannot be effectively brought into play. The effect of silane, when the volume fraction of 3-mercaptopropyltriethoxysilane is higher than said range, in step 3, konjac glucomannan carbon microspheres will be covered by a large amount of 3-mercaptopropyltriethoxy Silane covered, so the removal rate and adsorption capacity of the obtained adsorbent material for heavy metal ions are lower than the adsorbent material prepared in Example 4.

可见,本发明中采用的原料按所述比例,并且在吸附材料的制备工艺过程中,各个参数在所述的范围内,制备的吸附材料对重金属离子的吸附性能较好。It can be seen that the raw materials used in the present invention are in the stated proportion, and during the preparation process of the adsorbent material, each parameter is within the stated range, and the prepared adsorbent material has better adsorption performance on heavy metal ions.

尽管本发明的实施方案已公开如上,但其并不仅仅限于说明书和实施方式中所列运用,它完全可以被适用于各种适合本发明的领域,对于熟悉本领域的人员而言,可容易地实现另外的修改,因此在不背离权利要求及等同范围所限定的一般概念下,本发明并不限于特定的细节和这里示出与描述的图例。Although the embodiment of the present invention has been disclosed as above, it is not limited to the use listed in the specification and implementation, it can be applied to various fields suitable for the present invention, and it can be easily understood by those skilled in the art Therefore, the invention is not limited to the specific details and examples shown and described herein without departing from the general concept defined by the claims and their equivalents.

Claims (4)

1.一种改性魔芋葡甘聚糖碳微球重金属吸附材料的制备方法,其特征在于,包括以下步骤: 1. a preparation method of modified konjac glucomannan carbon microspheres heavy metal adsorption material, is characterized in that, comprises the following steps: 步骤一、将0.5~1重量份魔芋葡甘聚糖加入30~50重量份超纯水中,搅拌得到胶黏状浊液,在160~200℃下,将胶黏状浊液在水热反应釜中加热8~16h,然后将反应液在10000r/min的转速下离心20min,离心得到的固体用乙醇清洗3~5次,然后在50~80℃下真空干燥12~24h,得到魔芋葡甘聚糖碳微球; Step 1: Add 0.5-1 part by weight of konjac glucomannan into 30-50 parts by weight of ultra-pure water, stir to obtain a viscous turbid liquid, and place the viscous turbid liquid in a hydrothermal reaction at 160-200°C Heating in the kettle for 8-16 hours, then centrifuging the reaction solution at a speed of 10,000r/min for 20 minutes, washing the centrifuged solid with ethanol for 3-5 times, and then vacuum-drying at 50-80°C for 12-24 hours to obtain konjac glucan Polysaccharide carbon microspheres; 步骤二、用体积分数为1~5%的酸溶液调节醇水溶液的pH至4.5,将体积分数为1~3%的硅烷偶联剂溶液加入醇水溶液中震荡2h,得到改性液;所述醇水溶液中醇与水的体积比为1:1,所述醇水溶液与硅烷偶联剂溶液的体积比是1:0.3~0.5;所述酸溶液中的酸为盐酸;所述醇水溶液中的醇为甲醇;所述硅烷偶联剂为3-巯丙基三乙氧基硅烷; Step 2, using an acid solution with a volume fraction of 1 to 5% to adjust the pH of the alcohol aqueous solution to 4.5, adding a silane coupling agent solution with a volume fraction of 1 to 3% into the alcohol aqueous solution and shaking for 2 hours to obtain a modified solution; The volume ratio of alcohol to water in the alcohol aqueous solution is 1:1, and the volume ratio of the alcohol aqueous solution to the silane coupling agent solution is 1:0.3-0.5; the acid in the acid solution is hydrochloric acid; The alcohol is methanol; the silane coupling agent is 3-mercaptopropyltriethoxysilane; 步骤三、取3~15重量份步骤一制备的魔芋葡甘聚糖碳微球加入100重量份步骤二制备的改性液中,震荡3~5h,过滤,滤饼在65℃下烘干,将烘干后的滤饼用体积比为1:1的乙醇和水洗涤3~5次,50~80℃下真空干燥12~24h,制得改性魔芋葡甘聚糖碳微球吸附材料。 Step 3: Add 3 to 15 parts by weight of the konjac glucomannan carbon microspheres prepared in step 1 to 100 parts by weight of the modified liquid prepared in step 2, shake for 3 to 5 hours, filter, and dry the filter cake at 65°C. The dried filter cake is washed 3 to 5 times with ethanol and water at a volume ratio of 1:1, and vacuum dried at 50 to 80° C. for 12 to 24 hours to prepare the modified konjac glucomannan carbon microsphere adsorption material. 2.根据权利要求1所述的改性魔芋葡甘聚糖碳微球重金属吸附材料的制备方法,其特征在于,采用醋酸、硫酸、硝酸中的一种代替步骤二中酸溶液中的盐酸。 2. the preparation method of modified konjac glucomannan carbon microspheres heavy metal adsorption material according to claim 1, is characterized in that, adopts a kind of in acetic acid, sulfuric acid, nitric acid to replace the hydrochloric acid in the acid solution in step two. 3.根据权利要求1所述的改性魔芋葡甘聚糖碳微球重金属吸附材料的制备方法,其特征在于,采用乙醇代替步骤二中醇水溶液中的甲醇。 3. the preparation method of modified konjac glucomannan carbon microspheres heavy metal adsorption material according to claim 1, is characterized in that, adopts ethanol to replace the methanol in the alcohol aqueous solution in step two. 4.根据权利要求1所述的改性魔芋葡甘聚糖碳微球重金属吸附材料的制备方法,其特征在于,采用3-氨丙基三甲氧基硅烷、乙烯基三甲氧基硅烷、乙烯基三乙氧基硅烷中的一种代替步骤二中的硅烷偶联剂3-巯丙基三乙氧基硅烷。 4. the preparation method of modified konjac glucomannan carbon microspheres heavy metal adsorption material according to claim 1 is characterized in that, adopts 3-aminopropyltrimethoxysilane, vinyltrimethoxysilane, vinyl One of the triethoxysilanes replaces the silane coupling agent 3-mercaptopropyltriethoxysilane in step two.
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Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN110856714A (en) * 2018-08-23 2020-03-03 中国农业大学 Application of oxidized konjak microsphere in food or medicine delivery system

Families Citing this family (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN104941589B (en) * 2015-06-15 2017-05-10 西部矿业股份有限公司 Preparation method of porous biological carbon heavy metal adsorbing material based on cotton straw
CN105618003B (en) * 2016-03-28 2018-04-03 广西师范大学 A kind of immobilization sericin gel particle sorbing material and preparation method thereof
CN107487796A (en) * 2017-09-01 2017-12-19 展亚男 A kind of complex ecological renovation agent and its preparation method and application
CN108148219B (en) * 2018-01-29 2020-11-10 天津华清环宇环保科技有限公司 Preparation method of polymer molecular brush modified konjac glucomannan carbon microspheres
CN108854970B (en) * 2018-06-28 2021-05-18 西南科技大学 Preparation method of collagen peptide grafted hydrothermal carbon microsphere adsorbent
CN113142015B (en) * 2021-04-22 2022-03-04 西南科技大学 Method for preparing organic nutrient soil by washing mud with natural sand and gravel slurry
CN113368822A (en) * 2021-06-23 2021-09-10 苏州博禧环境科技有限公司 Preparation process of modified konjac glucomannan carbon microsphere-based heavy metal adsorption material

Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US5770090A (en) * 1989-07-28 1998-06-23 Lewis, Iii; Tom Method for recovery of heavy metal from waste water
CN103157438A (en) * 2013-04-10 2013-06-19 哈尔滨工业大学 Preparation method of carbon microsphere/nanometer iron oxide magnetic composite material

Patent Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US5770090A (en) * 1989-07-28 1998-06-23 Lewis, Iii; Tom Method for recovery of heavy metal from waste water
CN103157438A (en) * 2013-04-10 2013-06-19 哈尔滨工业大学 Preparation method of carbon microsphere/nanometer iron oxide magnetic composite material

Non-Patent Citations (2)

* Cited by examiner, † Cited by third party
Title
"尺寸可控空心碳球的水热合成";靳秀芝等;《稀有金属材料与工程》;20110630;第40卷;第101-103页 *
"硅烷偶联剂KH-570表面修饰羟基磷灰石的结构与吸附性能研究";王晓等;《材料导报 B:研究篇》;20120331;第26卷(第3期);第117-120页 *

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN110856714A (en) * 2018-08-23 2020-03-03 中国农业大学 Application of oxidized konjak microsphere in food or medicine delivery system

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