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CN102453187B - A kind of polymer hydrogel adsorbing heavy metal and its preparation method and application - Google Patents

A kind of polymer hydrogel adsorbing heavy metal and its preparation method and application Download PDF

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CN102453187B
CN102453187B CN2010105179490A CN201010517949A CN102453187B CN 102453187 B CN102453187 B CN 102453187B CN 2010105179490 A CN2010105179490 A CN 2010105179490A CN 201010517949 A CN201010517949 A CN 201010517949A CN 102453187 B CN102453187 B CN 102453187B
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metal ions
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CN102453187A (en
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李正魁
王月明
吴凯
陈祈春
周莉
王易超
潘静赟
范念文
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Nanjing University
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Abstract

The invention belongs to the technical field of an absorption material, and particularly relates to polymer hydrogel and a preparation method and application in absorption of heavy metal ions. The polymer hydrogel is a three-dimensional network polymer which is not dissolved in water and is strongly swelled in the water, and is generated by radiation copolymerization of two monomers of hydroxyethyl acrylate (hydrophilic glass-state monomer) and 2-acrylamide-2-methylpropanesulfonic acid. The polymer hydrogel has the structural and property characteristics of low degree of cross linking, high swelling rate, property of not being dissolved in the water, strong water absorbing capability and good water-retaining property, can not be dehydrated under the condition of pressurization after absorbing the water, and simultaneously, has the basic characteristics of a general polymer compound. In the invention, the polymer hydrogel prepared by the radiation copolymerization contains multi-functional groups for absorbing the heavy metals, and has good absorption property to lead, cadmium and other heavy metals. In addition, the synthetic method is simple, the operation is simple, the reaction process is free from other impurities, and a product can be ensured to be pure.

Description

一种吸附重金属的聚合物水凝胶及其制备方法和应用A kind of polymer hydrogel adsorbing heavy metal and its preparation method and application

技术领域 technical field

本发明属于吸附材料技术领域,具体涉及一种聚合水凝胶及其制备方法和在对重金属离子吸附中的应用。 The invention belongs to the technical field of adsorption materials, and in particular relates to a polymeric hydrogel, a preparation method thereof and an application in the adsorption of heavy metal ions.

背景技术 Background technique

近年来,由于人类对重金属的开采、冶炼、加工及商业制造活动日益增多,产生的重金属在数量上和种类上都大大增加,导致重金属大量进入土壤、水体中,不仅引起严重的环境污染和资源浪费,而且对人类的身体健康产生了很大的威胁。处理重金属废水的方法很多,目前最常用的方法是化学法,它能快速去除废水中的金属离子,工艺过程简单,但存在出水金属浓度偏高,易产生二次污染,废水回用困难等缺点。而吸附法因为处理流程简单,易于操作,也是重金属废水处理技术中被广泛使用和研究的方法。吸附剂主要有活性炭、沸石、离子树脂和螯合树脂(如公开号为CN1772386 的一种螯合树脂)等,而关于水凝胶作为吸附剂的研究相对较少。 In recent years, due to the increasing mining, smelting, processing and commercial manufacturing activities of heavy metals, the amount and types of heavy metals produced have greatly increased, resulting in a large amount of heavy metals entering the soil and water bodies, not only causing serious environmental pollution and resource pollution. It is wasteful and poses a great threat to human health. There are many ways to treat heavy metal wastewater. The most commonly used method is chemical method, which can quickly remove metal ions in wastewater. The process is simple, but there are disadvantages such as high metal concentration in the effluent, easy to produce secondary pollution, and difficult to reuse wastewater. . The adsorption method is also widely used and researched in heavy metal wastewater treatment technology because of its simple treatment process and easy operation. Sorbent mainly contains activated carbon, zeolite, ion resin and chelating resin (such as a kind of chelating resin whose publication number is CN1772386), etc., and there are relatively few studies on hydrogel as sorbent.

水凝胶是不溶于水但在水中高度溶胀的三维网络聚合物。它具有低交联度、高溶胀率、不溶于水的结构和性能特征;具有吸水能力强,保水性好,吸水后即使加压也不脱水,同时具有一般高分子化合物的基本特征。在水凝胶中存在大量的功能基团,作为新型吸附剂对染料和重金属的吸附近年来备受关注。许多天然有机高分子聚合物由于具有丰富的功能性基团被研究应用于重金属废水的吸附处理上,壳聚糖类生物质材料就是一个典型的代表,专利号为CN101701042A 的吸附树脂就是以壳聚糖为基体经过化学修饰后制备成的重金属吸附材料。壳聚糖类生物质材料的结构中含有大量的-NH 和-OH 基团,这些基团对重金属离子具有较强的络合与螯合作用,对水体中的微量重金属也有较好的去除效果,而且来源广泛、成本低廉。但是这类天然生物材料也有机械强度不高、易被生物降解、受pH影响很大等缺点。人工合成具有功能性基团的高分子聚合物凝胶,也被用于重金属废水的吸附分离。现有的人工合成的高分子聚合物水凝胶包括聚丙烯酸类水凝胶等,由于具有羧基等可结合重金属离子的有效基团,对重金属废水的离子吸附与分离也有一定得效果,但效果并不很显著。而且,现有的人工合成的高分子聚合物水凝胶大多合成途径相对复杂,操作比较麻烦,也是一大缺点。 Hydrogels are three-dimensional network polymers that are insoluble in water but highly swellable in water. It has the structure and performance characteristics of low cross-linking degree, high swelling rate, and insoluble in water; it has strong water absorption capacity, good water retention, and will not dehydrate even after water absorption, and has the basic characteristics of general polymer compounds. There are a large number of functional groups in the hydrogel, and the adsorption of dyes and heavy metals as a new adsorbent has attracted much attention in recent years. Many natural organic polymers have been studied and applied to the adsorption treatment of heavy metal wastewater due to their rich functional groups. Chitosan biomass materials are a typical representative. The adsorption resin with the patent number CN101701042A is based on chitosan Sugar is a heavy metal adsorption material prepared by chemically modifying the substrate. The structure of chitosan biomass material contains a large number of -NH and -OH groups, these groups have a strong complexation and chelation effect on heavy metal ions, and have a good removal effect on trace heavy metals in water , and the source is extensive and the cost is low. However, this kind of natural biomaterials also has disadvantages such as low mechanical strength, easy biodegradation, and great influence of pH. Artificially synthesized polymer gels with functional groups are also used for the adsorption and separation of heavy metal wastewater. Existing artificially synthesized high molecular polymer hydrogels include polyacrylic acid hydrogels, etc., because they have effective groups such as carboxyl groups that can bind heavy metal ions, they also have a certain effect on the ion adsorption and separation of heavy metal wastewater, but the effect is Not very noticeable. Moreover, most of the existing artificially synthesized polymer hydrogels have relatively complicated synthesis routes and cumbersome operations, which are also major disadvantages.

发明内容 Contents of the invention

本发明需要解决的问题是提供一种吸附重金属的聚合物水凝胶及其制备方法和应用。 The problem to be solved by the present invention is to provide a polymer hydrogel for adsorbing heavy metals, its preparation method and application.

本发明的技术方案为: Technical scheme of the present invention is:

1 本发明所述水凝胶为不溶于水但在水中高度溶胀的三维网络聚合物,由丙烯酸羟乙酯(亲水性玻璃态单体)和2-丙烯酰胺基-2-甲基丙磺酸两种单体辐射共聚生成。它具有低交联度、高溶胀率、不溶于水的结构和性能特征;具有吸水能力强,保水性好,吸水后即使加压也不脱水,同时具有一般高分子化合物的基本特征。 1 The hydrogel of the present invention is a three-dimensional network polymer that is insoluble in water but highly swellable in water, composed of hydroxyethyl acrylate (hydrophilic glassy monomer) and 2-acrylamide-2-methylpropanesulfonate The acid is produced by radiation copolymerization of two monomers. It has the structure and performance characteristics of low cross-linking degree, high swelling rate, and insoluble in water; it has strong water absorption capacity, good water retention, and will not dehydrate even after water absorption, and has the basic characteristics of general polymer compounds.

2 重金属吸附聚合物水凝胶的制备方法,其主要包括以下步骤: 2. The preparation method of heavy metal adsorption polymer hydrogel, which mainly includes the following steps:

(1)将丙烯酸羟乙酯(亲水性玻璃态单体)、2-丙烯酰胺基-2-甲基丙磺酸和蒸馏水按一定比例混合均匀; (1) Mix hydroxyethyl acrylate (hydrophilic glassy monomer), 2-acrylamido-2-methylpropanesulfonic acid and distilled water in a certain proportion;

(2)2-丙烯酰胺基-2-甲基丙磺酸加丙烯酸羟乙酯:水的体积比为(1~2):5,2-丙烯酰胺基-2-甲基丙磺酸与丙烯酸羟乙酯的摩尔比为1:(1~9); (2) 2-acrylamido-2-methylpropanesulfonic acid plus hydroxyethyl acrylate: the volume ratio of water is (1~2): 5,2-acrylamido-2-methylpropanesulfonic acid and acrylic acid The molar ratio of hydroxyethyl ester is 1: (1~9);

(3)混合后经过5~20min超声波处理; (3) Ultrasonic treatment for 5~20min after mixing;

(4)向(1)的混合物中充入氮气,以保证无氧状态; (4) Inflate nitrogen into the mixture of (1) to ensure anaerobic state;

(5)在-63~-95℃温度内,采用辐射剂量为1×103~1×106Gy的高能射线辐照聚合形成水凝胶。 (5) At a temperature of -63 to -95°C, a high-energy ray with a radiation dose of 1×10 3 to 1×10 6 Gy is used to irradiate and polymerize to form a hydrogel.

聚合物水凝胶对重金属离子的吸附方法,其主要包括以下步骤: The polymer hydrogel is to the adsorption method of heavy metal ion, and it mainly comprises the following steps:

(1)    将制备好的聚合物水凝胶切成1cm×1cm×1cm小块放在三角瓶中; (1) Cut the prepared polymer hydrogel into small pieces of 1cm×1cm×1cm and put them in the triangular flask;

(2)    将切成小块的聚合物水凝胶用去离子水多次洗涤; (2) Wash the polymer hydrogel cut into small pieces multiple times with deionized water;

(3)    在25℃条件下对不同种类的重金属离子进行吸附。 (3) Adsorb different types of heavy metal ions at 25°C.

3 本发明与现有技术相比其有益效果为: 3 Compared with the prior art, the beneficial effects of the present invention are:

现有的重金属吸附水凝胶研究主要在于天然的有机高分子聚合物,特别是以壳聚糖为研究对象最常见,但是这类天然生物材料机械强度不高、易被生物降解、受pH影响很大。且现有人工吸附水凝胶的制备技术过程比较复杂,吸附容量不高。本发明提出一种应用辐射技术制备吸附水凝胶的方法,可以制备出一种具有功能性基团的有机高分子聚合物,可使得聚合物中的功能基团有效吸附螯合重金属离子,制备方法简单,易于操作。并且产物具有一定的机械强度,可以延长使用寿命。 Existing research on heavy metal adsorption hydrogels mainly focuses on natural organic polymers, especially chitosan as the most common research object, but this kind of natural biomaterials has low mechanical strength, is easily biodegradable, and is affected by pH. very big. Moreover, the preparation process of the existing artificial adsorption hydrogel is relatively complicated, and the adsorption capacity is not high. The present invention proposes a method for preparing adsorption hydrogel by using radiation technology, which can prepare an organic high molecular polymer with functional groups, which can make the functional groups in the polymer effectively adsorb and chelate heavy metal ions, and prepare The method is simple and easy to operate. And the product has a certain mechanical strength, which can prolong the service life.

附图说明 Description of drawings

图1为水凝胶的SEM图。 Figure 1 is the SEM image of the hydrogel.

图2为水凝胶的红外光谱图。 Figure 2 is the infrared spectrum of the hydrogel.

图3为水凝胶在不同pH下吸附Pb2+的吸附容量图。 Figure 3 is a graph of the adsorption capacity of hydrogels adsorbing Pb 2+ at different pHs.

图4为水凝胶在不同pH下吸附Cd2+的吸附容量图。 Figure 4 is a graph of the adsorption capacity of hydrogels adsorbing Cd 2+ at different pHs.

图5为水凝胶在不同pH下吸附Cu2+的吸附容量图。 Fig. 5 is a graph of the adsorption capacity of hydrogels adsorbing Cu 2+ at different pHs.

图6为水凝胶在不同pH下吸附Cr3+的吸附容量图。 Fig. 6 is a graph showing the adsorption capacity of Cr 3+ adsorbed by hydrogel at different pH.

图7为水凝胶在不同pH下吸附Fe3+的吸附容量图。 Fig. 7 is a graph of the adsorption capacity of Fe 3+ adsorbed by hydrogel at different pH.

具体实施方式 Detailed ways

本发明通过实施例进行进一步说明,但本发明并不局限于以下实施例。 The present invention is further illustrated by examples, but the present invention is not limited to the following examples.

实施例 1: Example 1:

1. 称取一定质量2-丙烯酰胺基-2-甲基丙磺酸单体(简称AMPS)溶解于去离子水中,充分溶解混合均匀作为组分A。然后,向上述溶液中加入一定量丙烯酸羟乙酯单体(简称HEA),混合均匀,作为组分B;蒸馏水作为组分C,按(A+B):C为3:7(v/v)进行混合,其中A:B为2:5 (mol/mol)。使用超声波对混合物进行处理使混合均匀; 1. Weigh a certain mass of 2-acrylamido-2-methylpropanesulfonic acid monomer (AMPS for short) and dissolve it in deionized water, fully dissolve and mix evenly as component A. Then, add a certain amount of hydroxyethyl acrylate monomer (referred to as HEA) to the above solution, mix well, as component B; distilled water as component C, according to (A+B):C is 3:7 (v/v ) for mixing, where A:B is 2:5 (mol/mol). Use ultrasound to process the mixture to make the mixture uniform;

2. 充氮气后,在-78℃的温度下,控制辐射剂量范围在1×103~1×106Gy,采用高能射线(60Co-γ射线)辐照聚合形成聚合物水凝胶; 2. After filling with nitrogen, at a temperature of -78°C, control the radiation dose in the range of 1×10 3 to 1×10 6 Gy, and use high-energy rays ( 60 Co-γ rays) to irradiate and polymerize to form polymer hydrogels;

3.将辐射后水凝胶切成1cm×1cm×1cm小块放在三角瓶中多次洗涤后,在40℃温度下烘干; 3. Cut the irradiated hydrogel into small pieces of 1cm×1cm×1cm, put them in the Erlenmeyer flask for several times, and then dry them at 40°C;

4.对产物进行结构与成分的表征,包括使用SEM进行孔结构观察和使用红外光谱分析产物的成分。SEM的结果表明,产物有较好的孔结构。产物的红外图谱与两种反应物单体的红外图谱对比,显示了经过高能射线辐射后单体的双键打开后成链形成新产物。 4. Characterize the structure and composition of the product, including using SEM to observe the pore structure and using infrared spectroscopy to analyze the composition of the product. The results of SEM showed that the product had a good pore structure. The infrared spectrum of the product is compared with the infrared spectrum of the two reactant monomers, which shows that the double bonds of the monomers are opened to form new products after being irradiated by high-energy rays.

实施例 2: Example 2:

1. 称取一定质量2-丙烯酰胺基-2-甲基丙磺酸单体(简称AMPS)溶解于去离子水中,充分溶解混合均匀作为组分A。然后,向上述溶液中加入一定量丙烯酸羟乙酯单体(简称HEA),混合均匀,作为组分B;蒸馏水作为组分C,按(A+B):C为1:5进行混合,其中A:B为2:3(mol/mol),使用超声波对混合物进行处理使混合均匀。 1. Weigh a certain mass of 2-acrylamido-2-methylpropanesulfonic acid monomer (AMPS for short) and dissolve it in deionized water, fully dissolve and mix evenly as component A. Then, add a certain amount of hydroxyethyl acrylate monomer (HEA for short) to the above solution, mix evenly, as component B; distilled water as component C, mix according to (A+B):C ratio of 1:5, where A:B is 2:3 (mol/mol), and the mixture is treated with ultrasonic waves to make the mixture uniform.

2. 充氮气后,在-63℃的温度下,控制辐射剂量范围在1×103~1×106Gy,采用高能射线(137Cs-γ射线)辐照聚合形成聚合物水凝胶。 2. After filling with nitrogen, at a temperature of -63°C, control the radiation dose in the range of 1×10 3 to 1×10 6 Gy, and use high-energy rays ( 137 Cs-γ rays) to irradiate and polymerize to form polymer hydrogels.

3. 将辐射后水凝胶切成1cm×1cm×1cm小块放在三角瓶中多次洗涤后,在40℃温度下烘干。 3. Cut the irradiated hydrogel into small pieces of 1cm×1cm×1cm, put them in the Erlenmeyer flask and wash them several times, then dry them at 40°C.

4. 称取聚合物水凝胶0.1g 干燥后的产物五份分别置于100ml三角瓶中,然后分别加入50ml 1g/L的Pb2+、Cd2+、Cr3+、Cu2+、Fe3+五种单一溶液,将三角瓶置于恒温振荡器中25℃下进行恒温吸附,48h充分吸附后,分别测定各个重金属离子溶液吸附前与吸附后的浓度。测量方法为稀释后使用原子吸收法。通过吸附前后离子的浓度差,可以计算出该产物对各个离子的吸附容量。经测定,产物对Pb2+、Cr3+、Cd2+、Cu2+、Fe3+五种金属离子的吸附容量分别为:180mg/g、130mg/g、110mg/g、70mg/g、110mg/g。 4. Weigh 0.1g of the polymer hydrogel and put five parts of the dried product into 100ml Erlenmeyer flasks, and then add 50ml of 1g/L Pb 2+ , Cd 2+ , Cr 3+ , Cu 2+ , Fe 3+ Five kinds of single solutions, put the triangular flask in a constant temperature oscillator at 25°C for constant temperature adsorption, after 48 hours of full adsorption, measure the concentration of each heavy metal ion solution before and after adsorption. The measurement method is to use the atomic absorption method after dilution. The adsorption capacity of the product for each ion can be calculated by the concentration difference of ions before and after adsorption. It has been determined that the adsorption capacity of the product for five metal ions, Pb 2+ , Cr 3+ , Cd 2+ , Cu 2+ , and Fe 3+ , is 180mg/g, 130mg/g, 110mg/g, 70mg/g, 110mg/g.

实施例 3: Example 3:

1. 称取一定质量2-丙烯酰胺基-2-甲基丙磺酸单体(简称AMPS)溶解于去离子水中,充分溶解混合均匀作为组分A。然后,向上述溶液中加入一定量丙烯酸羟乙酯单体(简称HEA),混合均匀,作为组分B;蒸馏水作为组分C,按(A+B):C为1:5进行混合,其中A:B为1:1(mol/mol),使用超声波对混合物进行处理使混合均匀。 1. Weigh a certain mass of 2-acrylamido-2-methylpropanesulfonic acid monomer (AMPS for short) and dissolve it in deionized water, fully dissolve and mix evenly as component A. Then, add a certain amount of hydroxyethyl acrylate monomer (HEA for short) to the above solution, mix evenly, as component B; distilled water as component C, mix according to (A+B):C ratio of 1:5, where A:B is 1:1 (mol/mol), and the mixture is treated with ultrasonic waves to make the mixture uniform.

2. 充氮气后,在-63℃的温度下,控制辐射剂量范围在1×103~1×106Gy,采用高能射线(60Co-γ射线)辐照聚合形成聚合物水凝胶。 2. After filling with nitrogen, at a temperature of -63°C, control the radiation dose in the range of 1×10 3 to 1×10 6 Gy, and use high-energy rays ( 60 Co-γ rays) to irradiate and polymerize to form polymer hydrogels.

3. 将辐射后水凝胶切成1cm×1cm×1cm小块放在三角瓶中多次洗涤后,在40℃温度下烘干。 3. Cut the irradiated hydrogel into small pieces of 1cm×1cm×1cm, put them in the Erlenmeyer flask and wash them several times, then dry them at 40°C.

4. 称取聚合物水凝胶0.1g 干燥后的产物五份分别置于100ml三角瓶中,然后分别加入50ml 1g/L的Pb2+、Cd2+、Cr3+、Cu2+、Fe3+五种单一溶液,将三角瓶置于恒温振荡器中25℃下进行恒温吸附,48h充分吸附后,分别测定各个重金属离子溶液吸附前与吸附后的浓度。测量方法为稀释后使用原子吸收法。通过吸附前后离子的浓度差,可以计算出该产物对各个离子的吸附容量。经测定,产物对Pb2+、Cr3+、Cd2+、Cu2+、Fe3+五种金属离子的吸附容量分别为:150mg/g、130mg/g、110mg/g、70mg/g、110mg/g。 4. Weigh 0.1g of the polymer hydrogel and put five parts of the dried product into 100ml Erlenmeyer flasks, and then add 50ml of 1g/L Pb 2+ , Cd 2+ , Cr 3+ , Cu 2+ , Fe 3+ Five kinds of single solutions, put the triangular flask in a constant temperature oscillator at 25°C for constant temperature adsorption, after 48 hours of full adsorption, measure the concentration of each heavy metal ion solution before and after adsorption. The measurement method is to use the atomic absorption method after dilution. The adsorption capacity of the product for each ion can be calculated by the concentration difference of ions before and after adsorption. It has been determined that the adsorption capacities of the product for five metal ions, Pb 2+ , Cr 3+ , Cd 2+ , Cu 2+ , and Fe 3+ , are: 150mg/g, 130mg/g, 110mg/g, 70mg/g, 110mg/g.

实施例 4: Example 4:

1. 称取一定质量2-丙烯酰胺基-2-甲基丙磺酸单体(简称AMPS)溶解于去离子水中,充分溶解混合均匀作为组分A。然后,向上述溶液中加入一定量丙烯酸羟乙酯单体(简称HEA),混合均匀,作为组分B;蒸馏水作为组分C,按(A+B):C为2:5进行混合,其中A:B为1:5(mol/mol),使用超声波对混合物进行处理使混合均匀。 1. Weigh a certain mass of 2-acrylamido-2-methylpropanesulfonic acid monomer (AMPS for short) and dissolve it in deionized water, fully dissolve and mix evenly as component A. Then, add a certain amount of hydroxyethyl acrylate monomer (HEA for short) to the above solution, mix well, as component B; distilled water as component C, mix according to (A+B):C ratio of 2:5, where A:B is 1:5 (mol/mol), and the mixture is treated with ultrasonic waves to make the mixture uniform.

2. 充氮气后,在-78℃的温度下,控制辐射剂量范围在1×103~1×106Gy,采用高能射线(137Cs-γ射线)辐照聚合形成聚合物水凝胶。 2. After filling with nitrogen, at a temperature of -78°C, control the radiation dose in the range of 1×10 3 to 1×10 6 Gy, and use high-energy rays ( 137 Cs-γ rays) to irradiate and polymerize to form polymer hydrogels.

3. 将辐射后水凝胶切成1cm×1cm×1cm小块放在三角瓶中多次洗涤后,在40℃温度下烘干。 3. Cut the irradiated hydrogel into small pieces of 1cm×1cm×1cm, put them in the Erlenmeyer flask and wash them several times, then dry them at 40°C.

4. 称取聚合物水凝胶0.1g 干燥后的产物五份分别置于100ml三角瓶中,然后分别加入50ml 1g/L的Pb2+、Cd2+、Cr3+、Cu2+、Fe3+五种单一溶液,将三角瓶置于恒温振荡器中25℃下进行恒温吸附,48h充分吸附后,分别测定各个重金属离子溶液吸附前与吸附后的浓度。测量方法为稀释后使用原子吸收法。通过吸附前后离子的浓度差,可以计算出该产物对各个离子的吸附容量。经测定,产物对Pb2+、Cr3+、Cd2+、Cu2+、Fe3+五种金属离子的吸附容量分别为:130mg/g、80mg/g、70mg/g、60mg/g、110mg/g。 4. Weigh 0.1g of the polymer hydrogel and put five parts of the dried product into 100ml Erlenmeyer flasks, and then add 50ml of 1g/L Pb 2+ , Cd 2+ , Cr 3+ , Cu 2+ , Fe 3+ Five kinds of single solutions, put the triangular flask in a constant temperature oscillator at 25°C for constant temperature adsorption, after 48 hours of full adsorption, measure the concentration of each heavy metal ion solution before and after adsorption. The measurement method is to use the atomic absorption method after dilution. The adsorption capacity of the product for each ion can be calculated by the concentration difference of ions before and after adsorption. It has been determined that the adsorption capacity of the product for five metal ions, Pb 2+ , Cr 3+ , Cd 2+ , Cu 2+ , and Fe 3+ , are: 130mg/g, 80mg/g, 70mg/g, 60mg/g, 110mg/g.

实施例 5: Example 5:

1. 称取一定质量2-丙烯酰胺基-2-甲基丙磺酸单体(简称AMPS)溶解于去离子水中,充分溶解混合均匀作为组分A。然后,向上述溶液中加入一定量丙烯酸羟乙酯单体(简称HEA),混合均匀,作为组分B;蒸馏水作为组分C,按(A+B):C为2:5进行混合,其中A:B为2:3(mol/mol),使用超声波对混合物进行处理使混合均匀。 1. Weigh a certain mass of 2-acrylamido-2-methylpropanesulfonic acid monomer (AMPS for short) and dissolve it in deionized water, fully dissolve and mix evenly as component A. Then, add a certain amount of hydroxyethyl acrylate monomer (HEA for short) to the above solution, mix well, as component B; distilled water as component C, mix according to (A+B):C ratio of 2:5, where A:B is 2:3 (mol/mol), and the mixture is treated with ultrasonic waves to make the mixture uniform.

2. 充氮气后,在-78℃的温度下,控制辐射剂量范围在1×103~1×106Gy,采用高能射线(137Cs-γ射线)辐照聚合形成聚合物水凝胶。 2. After filling with nitrogen, at a temperature of -78°C, control the radiation dose in the range of 1×10 3 to 1×10 6 Gy, and use high-energy rays ( 137 Cs-γ rays) to irradiate and polymerize to form polymer hydrogels.

3. 将辐射后水凝胶切成1cm×1cm×1cm小块放在三角瓶中多次洗涤后,在40℃温度下烘干。 3. Cut the irradiated hydrogel into small pieces of 1cm×1cm×1cm, put them in the Erlenmeyer flask and wash them several times, then dry them at 40°C.

4. 称取聚合物水凝胶0.1g 干燥后的产物五份分别置于100ml三角瓶中,然后分别加入50ml 1g/L的Pb2+、Cd2+、Cr3+、Cu2+、Fe3+五种单一溶液,将三角瓶置于恒温振荡器中25℃下进行恒温吸附,48h充分吸附后,分别测定各个重金属离子溶液吸附前与吸附后的浓度。测量方法为稀释后使用原子吸收法。通过吸附前后离子的浓度差,可以计算出该产物对各个离子的吸附容量。经测定,产物对Pb2+、Cr3+、Cd2+、Cu2+、Fe3+五种金属离子的吸附容量分别为:200mg/g、120mg/g、130mg/g、100mg/g、130mg/g。 4. Weigh 0.1g of the polymer hydrogel and put five parts of the dried product into 100ml Erlenmeyer flasks, and then add 50ml of 1g/L Pb 2+ , Cd 2+ , Cr 3+ , Cu 2+ , Fe 3+ Five kinds of single solutions, put the triangular flask in a constant temperature oscillator at 25°C for constant temperature adsorption, after 48 hours of full adsorption, measure the concentration of each heavy metal ion solution before and after adsorption. The measurement method is to use the atomic absorption method after dilution. The adsorption capacity of the product for each ion can be calculated by the concentration difference of ions before and after adsorption. It has been determined that the adsorption capacity of the product for five metal ions, Pb 2+ , Cr 3+ , Cd 2+ , Cu 2+ , and Fe 3+ , are: 200mg/g, 120mg/g, 130mg/g, 100mg/g, 130mg/g.

实施例 6: Example 6:

1. 称取一定质量2-丙烯酰胺基-2-甲基丙磺酸单体(简称AMPS)溶解于去离子水中,充分溶解混合均匀作为组分A。然后,向上述溶液中加入一定量丙烯酸羟乙酯单体(简称HEA),混合均匀,作为组分B;蒸馏水作为组分C,按(A+B):C为3:7进行混合,其中A:B为1:9(mol/mol),使用超声波对混合物进行处理使混合均匀。 1. Weigh a certain mass of 2-acrylamido-2-methylpropanesulfonic acid monomer (AMPS for short) and dissolve it in deionized water, fully dissolve and mix evenly as component A. Then, add a certain amount of hydroxyethyl acrylate monomer (referred to as HEA) to the above solution, mix well, as component B; distilled water as component C, mix according to (A+B):C ratio of 3:7, where A:B is 1:9 (mol/mol), and the mixture is treated with ultrasonic waves to make the mixture uniform.

2. 充氮气后,在-95℃的温度下,控制辐射剂量范围在1×103~1×106Gy,采用高能射线(60Co-γ射线)辐照聚合形成聚合物水凝胶。 2. After filling with nitrogen, at -95°C, control the radiation dose in the range of 1×10 3 to 1×10 6 Gy, and use high-energy rays ( 60 Co-γ rays) to irradiate and polymerize to form polymer hydrogels.

3. 将辐射后水凝胶切成1cm×1cm×1cm小块放在三角瓶中多次洗涤后,在40℃温度下烘干。 3. Cut the irradiated hydrogel into small pieces of 1cm×1cm×1cm, put them in the Erlenmeyer flask and wash them several times, then dry them at 40°C.

4. 称取聚合物水凝胶0.1g 干燥后的产物五份分别置于100ml三角瓶中,然后分别加入50ml 1g/L的Pb2+、Cd2+、Cr3+、Cu2+、Fe3+五种单一溶液,将三角瓶置于恒温振荡器中25℃下进行恒温吸附,48h充分吸附后,分别测定各个重金属离子溶液吸附前与吸附后的浓度。测量方法为稀释后使用原子吸收法。通过吸附前后离子的浓度差,可以计算出该产物对各个离子的吸附容量。经测定,产物对Pb2+、Cr3+、Cd2+、Cu2+、Fe3+五种金属离子的吸附容量分别为:140mg/g、60mg/g、70mg/g、80mg/g、130mg/g。 4. Weigh 0.1g of the polymer hydrogel and put five parts of the dried product into 100ml Erlenmeyer flasks, and then add 50ml of 1g/L Pb 2+ , Cd 2+ , Cr 3+ , Cu 2+ , Fe 3+ Five kinds of single solutions, put the triangular flask in a constant temperature oscillator at 25°C for constant temperature adsorption, after 48 hours of full adsorption, measure the concentration of each heavy metal ion solution before and after adsorption. The measurement method is to use the atomic absorption method after dilution. The adsorption capacity of the product for each ion can be calculated by the concentration difference of ions before and after adsorption. It has been determined that the adsorption capacity of the product for five metal ions, Pb 2+ , Cr 3+ , Cd 2+ , Cu 2+ , and Fe 3+ , is 140mg/g, 60mg/g, 70mg/g, 80mg/g, 130mg/g.

实施例 7: Example 7:

1. 称取一定质量2-丙烯酰胺基-2-甲基丙磺酸单体(简称AMPS)溶解于去离子水中,充分溶解混合均匀作为组分A。然后,向上述溶液中加入一定量丙烯酸羟乙酯单体(简称HEA),混合均匀,作为组分B;蒸馏水作为组分C,按(A+B):C为3:7进行混合,其中A:B为1:5(mol/mol),使用超声波对混合物进行处理使混合均匀。 1. Weigh a certain mass of 2-acrylamido-2-methylpropanesulfonic acid monomer (AMPS for short) and dissolve it in deionized water, fully dissolve and mix evenly as component A. Then, add a certain amount of hydroxyethyl acrylate monomer (referred to as HEA) to the above solution, mix well, as component B; distilled water as component C, mix according to (A+B):C ratio of 3:7, where A:B is 1:5 (mol/mol), and the mixture is treated with ultrasonic waves to make the mixture uniform.

2. 充氮气后,在-95℃的温度下,控制辐射剂量范围在1×103~1×106Gy,采用高能射线(60Co-γ射线)辐照聚合形成聚合物水凝胶。 2. After filling with nitrogen, at -95°C, control the radiation dose in the range of 1×10 3 to 1×10 6 Gy, and use high-energy rays ( 60 Co-γ rays) to irradiate and polymerize to form polymer hydrogels.

3. 将辐射后水凝胶切成1cm×1cm×1cm小块放在三角瓶中多次洗涤后,在40℃温度下烘干。 3. Cut the irradiated hydrogel into small pieces of 1cm×1cm×1cm, put them in the Erlenmeyer flask and wash them several times, then dry them at 40°C.

4. 称取聚合物水凝胶0.1g 干燥后的产物五份分别置于100ml三角瓶中,然后分别加入50ml 1g/L的Pb2+、Cd2+、Cr3+、Cu2+、Fe3+五种单一溶液,将三角瓶置于恒温振荡器中25℃下进行恒温吸附,48h充分吸附后,分别测定各个重金属离子溶液吸附前与吸附后的浓度。测量方法为稀释后使用原子吸收法。通过吸附前后离子的浓度差,可以计算出该产物对各个离子的吸附容量。经测定,产物对Pb2+、Cr3+、Cd2+、Cu2+、Fe3+五种金属离子的吸附容量分别为:160mg/g、80mg/g、100mg/g、80mg/g、110mg/g。 4. Weigh 0.1g of the polymer hydrogel and put five parts of the dried product into 100ml Erlenmeyer flasks, and then add 50ml of 1g/L Pb 2+ , Cd 2+ , Cr 3+ , Cu 2+ , Fe 3+ Five kinds of single solutions, put the triangular flask in a constant temperature oscillator at 25°C for constant temperature adsorption, after 48 hours of full adsorption, measure the concentration of each heavy metal ion solution before and after adsorption. The measurement method is to use the atomic absorption method after dilution. The adsorption capacity of the product for each ion can be calculated by the concentration difference of ions before and after adsorption. It has been determined that the adsorption capacity of the product to five metal ions, Pb 2+ , Cr 3+ , Cd 2+ , Cu 2+ , and Fe 3+ , are: 160mg/g, 80mg/g, 100mg/g, 80mg/g, 110mg/g.

实施例 8: Example 8:

1. 称取一定质量2-丙烯酰胺基-2-甲基丙磺酸单体(简称AMPS)溶解于去离子水中,充分溶解混合均匀作为组分A。然后,向上述溶液中加入一定量丙烯酸羟乙酯单体(简称HEA),混合均匀,作为组分B;蒸馏水作为组分C,按(A+B):C为3:7进行混合,其中A:B为2:3(mol/mol),使用超声波对混合物进行处理使混合均匀。 1. Weigh a certain mass of 2-acrylamido-2-methylpropanesulfonic acid monomer (AMPS for short) and dissolve it in deionized water, fully dissolve and mix evenly as component A. Then, add a certain amount of hydroxyethyl acrylate monomer (referred to as HEA) to the above solution, mix well, as component B; distilled water as component C, mix according to (A+B):C ratio of 3:7, where A:B is 2:3 (mol/mol), and the mixture is treated with ultrasonic waves to make the mixture uniform.

2. 充氮气后,在-95℃的温度下,控制辐射剂量范围在1×103~1×106Gy,采用高能射线(60Co-γ射线)辐照聚合形成聚合物水凝胶。 2. After filling with nitrogen, at -95°C, control the radiation dose in the range of 1×10 3 to 1×10 6 Gy, and use high-energy rays ( 60 Co-γ rays) to irradiate and polymerize to form polymer hydrogels.

3. 将辐射后水凝胶切成1cm×1cm×1cm小块放在三角瓶中多次洗涤后,在40℃温度下烘干。 3. Cut the irradiated hydrogel into small pieces of 1cm×1cm×1cm, put them in the Erlenmeyer flask and wash them several times, then dry them at 40°C.

4. 称取聚合物水凝胶0.1g 干燥后的产物五份分别置于100ml三角瓶中,然后分别加入50ml 1g/L的Pb2+、Cd2+、Cr3+、Cu2+、Fe3+五种单一溶液,将三角瓶置于恒温振荡器中25℃下进行恒温吸附,48h充分吸附后,分别测定各个重金属离子溶液吸附前与吸附后的浓度。测量方法为稀释后使用原子吸收法。通过吸附前后离子的浓度差,可以计算出该产物对各个离子的吸附容量。经测定,产物对Pb2+、Cr3+、Cd2+、Cu2+、Fe3+五种金属离子的吸附容量分别为:190mg/g、120mg/g、140mg/g、80mg/g、150mg/g。 4. Weigh 0.1g of the polymer hydrogel and put five parts of the dried product into 100ml Erlenmeyer flasks, and then add 50ml of 1g/L Pb 2+ , Cd 2+ , Cr 3+ , Cu 2+ , Fe 3+ Five kinds of single solutions, put the triangular flask in a constant temperature oscillator at 25°C for constant temperature adsorption, after 48 hours of full adsorption, measure the concentration of each heavy metal ion solution before and after adsorption. The measurement method is to use the atomic absorption method after dilution. The adsorption capacity of the product for each ion can be calculated by the concentration difference of ions before and after adsorption. It has been determined that the adsorption capacities of the product for five metal ions, Pb 2+ , Cr 3+ , Cd 2+ , Cu 2+ , and Fe 3+ , are: 190mg/g, 120mg/g, 140mg/g, 80mg/g, 150mg/g.

实施例 9: Example 9:

1. 称取一定质量2-丙烯酰胺基-2-甲基丙磺酸单体(简称AMPS)溶解于去离子水中,充分溶解混合均匀作为组分A。然后,向上述溶液中加入一定量丙烯酸羟乙酯单体(简称HEA),混合均匀,作为组分B;蒸馏水作为组分C,按(A+B):C为3:7进行混合,其中A:B为1:9(mol/mol),使用超声波对混合物进行处理使混合均匀。 1. Weigh a certain mass of 2-acrylamido-2-methylpropanesulfonic acid monomer (AMPS for short) and dissolve it in deionized water, fully dissolve and mix evenly as component A. Then, add a certain amount of hydroxyethyl acrylate monomer (referred to as HEA) to the above solution, mix well, as component B; distilled water as component C, mix according to (A+B):C ratio of 3:7, where A:B is 1:9 (mol/mol), and the mixture is treated with ultrasonic waves to make the mixture uniform.

2. 充氮气后,在-78℃的温度下,控制辐射剂量范围在1×103~1×106Gy,采用高能射线(60Co-γ射线)辐照聚合形成聚合物水凝胶。 2. After filling with nitrogen, at a temperature of -78°C, control the radiation dose in the range of 1×10 3 to 1×10 6 Gy, and use high-energy rays ( 60 Co-γ rays) to irradiate and polymerize to form polymer hydrogels.

3. 将辐射后水凝胶切成1cm×1cm×1cm小块放在三角瓶中多次洗涤后,在40℃温度下烘干。 3. Cut the irradiated hydrogel into small pieces of 1cm×1cm×1cm, put them in the Erlenmeyer flask and wash them several times, then dry them at 40°C.

4. 称取干燥产物0.1g 各七份分别置于100ml三角瓶中,然后分别加入50ml 一定pH下的2g/L的Pb2+溶液。溶液的pH分别是1,2,3,4,5,6,7。将三角瓶置于恒温振荡器中25℃下进行恒温吸附,48h充分吸附后,分别测定各个pH下Pb2+溶液吸附前与吸附后的Pb2+的浓度。测量方法为稀释后使用原子吸收法。通过吸附前后Pb2+的浓度差,可以计算出该产物对于Pb2+的吸附容量。经测定,在pH为6时,水凝胶对Pb2+的吸附效果最好。详见附图3。 4. Weigh 0.1g of the dried product and place seven portions in 100ml Erlenmeyer flasks respectively, and then add 50ml of 2g/L Pb 2+ solution at a certain pH. The pH of the solution is 1, 2, 3, 4, 5, 6, 7, respectively. Place the Erlenmeyer flask in a constant temperature oscillator at 25°C for constant temperature adsorption. After fully adsorbed for 48 hours, measure the concentration of Pb 2+ in the Pb 2+ solution at each pH before and after adsorption. The measurement method is to use the atomic absorption method after dilution. The adsorption capacity of the product for Pb 2+ can be calculated by the concentration difference of Pb 2+ before and after adsorption. It was determined that the hydrogel had the best adsorption effect on Pb 2+ when the pH was 6. See attached drawing 3 for details.

实施例 10: Example 10:

1. 称取一定质量2-丙烯酰胺基-2-甲基丙磺酸单体(简称AMPS)溶解于去离子水中,充分溶解混合均匀作为组分A。然后,向上述溶液中加入一定量丙烯酸羟乙酯单体(简称HEA),混合均匀,作为组分B;蒸馏水作为组分C,按(A+B):C为3:7进行混合,其中A:B为1:9(mol/mol),使用超声波对混合物进行处理使混合均匀。 1. Weigh a certain mass of 2-acrylamido-2-methylpropanesulfonic acid monomer (AMPS for short) and dissolve it in deionized water, fully dissolve and mix evenly as component A. Then, add a certain amount of hydroxyethyl acrylate monomer (referred to as HEA) to the above solution, mix well, as component B; distilled water as component C, mix according to (A+B):C ratio of 3:7, where A:B is 1:9 (mol/mol), and the mixture is treated with ultrasonic waves to make the mixture uniform.

2. 充氮气后,在-63℃的温度下,控制辐射剂量范围在1×103~1×106Gy,采用高能射线(60Co-γ射线)辐照聚合形成聚合物水凝胶。 2. After filling with nitrogen, at a temperature of -63°C, control the radiation dose in the range of 1×10 3 to 1×10 6 Gy, and use high-energy rays ( 60 Co-γ rays) to irradiate and polymerize to form polymer hydrogels.

3. 将辐射后水凝胶切成1cm×1cm×1cm小块放在三角瓶中多次洗涤后,在40℃温度下烘干。 3. Cut the irradiated hydrogel into small pieces of 1cm×1cm×1cm, put them in the Erlenmeyer flask and wash them several times, then dry them at 40°C.

   4. 称取干燥产物0.1g 各七份分别置于100ml三角瓶中,然后分别加入50ml 一定pH下的2g/L的Cd2+溶液。溶液的pH分别是1,2,3,4,5,6,7。将三角瓶置于恒温振荡器中25℃下进行恒温吸附,48h充分吸附后,分别测定各个pH下Cd2+溶液吸附前与吸附后的Cd2+的浓度。测量方法为稀释后使用原子吸收法。通过吸附前后Cd2+的浓度差,可以计算出该产物对于Cd2+的吸附容量。经测定,在pH为6时,水凝胶对Cd2+的吸附效果最好。详见附图4。 4. Weigh 0.1g of the dry product and put each seven portions into 100ml Erlenmeyer flasks, and then add 50ml of 2g/L Cd 2+ solution at a certain pH. The pH of the solution is 1, 2, 3, 4, 5, 6, 7, respectively. Place the Erlenmeyer flask in a constant temperature oscillator at 25°C for constant temperature adsorption. After fully adsorbed for 48 hours, measure the concentration of Cd 2+ in the Cd 2+ solution at each pH before and after adsorption. The measurement method is to use the atomic absorption method after dilution. The adsorption capacity of the product for Cd 2+ can be calculated by the concentration difference of Cd 2+ before and after adsorption. It has been determined that the hydrogel has the best adsorption effect on Cd 2+ when the pH is 6. See attached drawing 4 for details.

实施例 11: Example 11:

1. 称取一定质量2-丙烯酰胺基-2-甲基丙磺酸单体(简称AMPS)溶解于去离子水中,充分溶解混合均匀作为组分A。然后,向上述溶液中加入一定量丙烯酸羟乙酯单体(简称HEA),混合均匀,作为组分B;蒸馏水作为组分C,按(A+B):C为3:7进行混合,其中A:B为1:9(mol/mol),使用超声波对混合物进行处理使混合均匀。 1. Weigh a certain mass of 2-acrylamido-2-methylpropanesulfonic acid monomer (AMPS for short) and dissolve it in deionized water, fully dissolve and mix evenly as component A. Then, add a certain amount of hydroxyethyl acrylate monomer (referred to as HEA) to the above solution, mix well, as component B; distilled water as component C, mix according to (A+B):C ratio of 3:7, where A:B is 1:9 (mol/mol), and the mixture is treated with ultrasonic waves to make the mixture uniform.

2. 充氮气后,在-78℃的温度下,控制辐射剂量范围在1×103~1×106Gy,采用高能射线(60Co-γ射线)辐照聚合形成聚合物水凝胶。 2. After filling with nitrogen, at a temperature of -78°C, control the radiation dose in the range of 1×10 3 to 1×10 6 Gy, and use high-energy rays ( 60 Co-γ rays) to irradiate and polymerize to form polymer hydrogels.

3. 将辐射后水凝胶切成1cm×1cm×1cm小块放在三角瓶中多次洗涤后,在40℃温度下烘干。 3. Cut the irradiated hydrogel into small pieces of 1cm×1cm×1cm, put them in the Erlenmeyer flask and wash them several times, then dry them at 40°C.

   4. 称取干燥产物0.1g 各七份分别置于100ml三角瓶中,然后分别加入50ml 一定pH下的2g/L的Cu2+溶液。溶液的pH分别是1,2,3,4,5,6,7。将三角瓶置于恒温振荡器中25℃下进行恒温吸附,48h充分吸附后,分别测定各个pH下Cu2+溶液吸附前与吸附后的Cu2+的浓度。测量方法为稀释后使用原子吸收法。通过吸附前后Cu2+的浓度差,可以计算出该产物对于Cu2+的吸附容量。经测定,在pH为4时,水凝胶对Cu2+的吸附效果最好。详见附图5。 4. Weigh 0.1g of the dried product and place seven portions in 100ml Erlenmeyer flasks respectively, and then add 50ml of 2g/L Cu 2+ solution at a certain pH. The pH of the solution is 1, 2, 3, 4, 5, 6, 7, respectively. Place the Erlenmeyer flask in a constant temperature oscillator at 25°C for constant temperature adsorption. After fully adsorbed for 48 hours, measure the concentration of Cu 2+ in the Cu 2+ solution at each pH before and after adsorption. The measurement method is to use the atomic absorption method after dilution. The adsorption capacity of the product for Cu 2+ can be calculated by the concentration difference of Cu 2+ before and after adsorption. It was determined that the hydrogel had the best adsorption effect on Cu 2+ when the pH was 4. See attached drawing 5 for details.

实施例 12: Example 12:

1. 称取一定质量2-丙烯酰胺基-2-甲基丙磺酸单体(简称AMPS)溶解于去离子水中,充分溶解混合均匀作为组分A。然后,向上述溶液中加入一定量丙烯酸羟乙酯单体(简称HEA),混合均匀,作为组分B;蒸馏水作为组分C,按(A+B):C为3:7进行混合,其中A:B为1:9(mol/mol),使用超声波对混合物进行处理使混合均匀。 1. Weigh a certain mass of 2-acrylamido-2-methylpropanesulfonic acid monomer (AMPS for short) and dissolve it in deionized water, fully dissolve and mix evenly as component A. Then, add a certain amount of hydroxyethyl acrylate monomer (referred to as HEA) to the above solution, mix well, as component B; distilled water as component C, mix according to (A+B):C ratio of 3:7, where A:B is 1:9 (mol/mol), and the mixture is treated with ultrasonic waves to make the mixture uniform.

2. 充氮气后,在-63℃的温度下,控制辐射剂量范围在1×103~1×106Gy,采用高能射线(60Co-γ射线)辐照聚合形成聚合物水凝胶。 2. After filling with nitrogen, at a temperature of -63°C, control the radiation dose in the range of 1×10 3 to 1×10 6 Gy, and use high-energy rays ( 60 Co-γ rays) to irradiate and polymerize to form polymer hydrogels.

3. 将辐射后水凝胶切成1cm×1cm×1cm小块放在三角瓶中多次洗涤后,在40℃温度下烘干。 3. Cut the irradiated hydrogel into small pieces of 1cm×1cm×1cm, put them in the Erlenmeyer flask and wash them several times, then dry them at 40°C.

   4. 称取干燥产物0.1g 各七份分别置于100ml三角瓶中,然后分别加入50ml 一定pH下的2g/L的Cr3+溶液。溶液的pH分别是1,2,3,4,5,6,7。将三角瓶置于恒温振荡器中25℃下进行恒温吸附,48h充分吸附后,分别测定各个pH下Cr3+溶液吸附前与吸附后的Cr3+的浓度。测量方法为稀释后使用原子吸收法。通过吸附前后Cr3+的浓度差,可以计算出该产物对于Cr3+的吸附容量。经测定,在pH为7时,水凝胶对Cr3+的吸附效果最好。详见附图6。 4. Weigh 0.1g of the dried product and place seven portions in 100ml Erlenmeyer flasks respectively, and then add 50ml of 2g/L Cr 3+ solution at a certain pH. The pH of the solution is 1, 2, 3, 4, 5, 6, 7, respectively. Place the Erlenmeyer flask in a constant temperature oscillator at 25°C for constant temperature adsorption. After fully adsorbed for 48 hours, measure the concentration of Cr 3+ before and after adsorption of Cr 3+ solution at each pH. The measurement method is to use the atomic absorption method after dilution. The adsorption capacity of the product for Cr 3+ can be calculated by the concentration difference of Cr 3+ before and after adsorption. It has been determined that the hydrogel has the best adsorption effect on Cr 3+ when the pH is 7. See attached drawing 6 for details.

实施例 13: Example 13:

1. 称取一定质量2-丙烯酰胺基-2-甲基丙磺酸单体(简称AMPS)溶解于去离子水中,充分溶解混合均匀作为组分A。然后,向上述溶液中加入一定量丙烯酸羟乙酯单体(简称HEA),混合均匀,作为组分B;蒸馏水作为组分C,按(A+B):C为3:7进行混合,其中A:B为1:9(mol/mol),使用超声波对混合物进行处理使混合均匀。 1. Weigh a certain mass of 2-acrylamido-2-methylpropanesulfonic acid monomer (AMPS for short) and dissolve it in deionized water, fully dissolve and mix evenly as component A. Then, add a certain amount of hydroxyethyl acrylate monomer (referred to as HEA) to the above solution, mix well, as component B; distilled water as component C, mix according to (A+B):C ratio of 3:7, where A:B is 1:9 (mol/mol), and the mixture is treated with ultrasonic waves to make the mixture uniform.

2. 充氮气后,在-63℃的温度下,控制辐射剂量范围在1×103~1×106Gy,采用高能射线(60Co-γ射线)辐照聚合形成聚合物水凝胶。 2. After filling with nitrogen, at a temperature of -63°C, control the radiation dose in the range of 1×10 3 to 1×10 6 Gy, and use high-energy rays ( 60 Co-γ rays) to irradiate and polymerize to form polymer hydrogels.

3. 将辐射后水凝胶切成1cm×1cm×1cm小块放在三角瓶中多次洗涤后,在40℃温度下烘干。 3. Cut the irradiated hydrogel into small pieces of 1cm×1cm×1cm, put them in the Erlenmeyer flask and wash them several times, then dry them at 40°C.

   4. 称取干燥产物0.1g 各七份分别置于100ml三角瓶中,然后分别加入50ml 一定pH下的2g/L的Fe3+溶液。溶液的pH分别是1,2,3,4,5,6,7。将三角瓶置于恒温振荡器中25℃下进行恒温吸附,48h充分吸附后,分别测定各个pH下Fe3+溶液吸附前与吸附后的Fe3+的浓度。测量方法为稀释后使用原子吸收法。通过吸附前后Fe3+的浓度差,可以计算出该产物对于Fe3+的吸附容量。经测定,在pH为2时,水凝胶对Fe3+的吸附效果最好。详见附图7。 4. Weigh 0.1g of the dry product and place seven portions in each of 100ml Erlenmeyer flasks, then add 50ml of 2g/L Fe 3+ solution at a certain pH. The pH of the solution is 1, 2, 3, 4, 5, 6, 7, respectively. Place the triangular flask in a constant temperature oscillator at 25°C for constant temperature adsorption. After fully adsorbing for 48 hours, measure the concentration of Fe 3+ in the Fe 3+ solution at each pH before and after adsorption. The measurement method is to use the atomic absorption method after dilution. The adsorption capacity of the product for Fe 3+ can be calculated by the concentration difference of Fe 3+ before and after adsorption. It was determined that the hydrogel had the best adsorption effect on Fe 3+ when the pH was 2. See attached drawing 7 for details.

实施例14: Example 14:

1.称取一定质量2-丙烯酰胺基-2-甲基丙磺酸单体(简称AMPS)溶解于去离子水中,充分溶解混合均匀作为组分A。然后,向上述溶液中加入一定量丙烯酸羟乙酯单体(简称HEA),混合均匀,作为组分B;蒸馏水作为组分C,按(A+B):C为3:7进行混合,其中A:B为2:3 (mol/mol),使用超声波对混合物进行处理使混合均匀。 1. Weigh a certain mass of 2-acrylamido-2-methylpropanesulfonic acid monomer (AMPS for short) and dissolve it in deionized water, fully dissolve and mix evenly as component A. Then, add a certain amount of hydroxyethyl acrylate monomer (referred to as HEA) to the above solution, mix well, as component B; distilled water as component C, mix according to (A+B):C ratio of 3:7, where A:B is 2:3 (mol/mol), and the mixture is treated with ultrasonic waves to make the mixture uniform.

2. 充氮气后,在-78℃的温度下,控制辐射剂量范围在1×103~1×106Gy,采用高能射线(137Cs-γ射线)辐照聚合形成聚合物水凝胶。 2. After filling with nitrogen, at a temperature of -78°C, control the radiation dose in the range of 1×10 3 to 1×10 6 Gy, and use high-energy rays ( 137 Cs-γ rays) to irradiate and polymerize to form polymer hydrogels.

3.将辐射后水凝胶切成1cm×1cm×1cm小块放在三角瓶中多次洗涤后,在40℃温度下烘干。 3. The irradiated hydrogel was cut into small pieces of 1 cm×1 cm×1 cm, washed in a Erlenmeyer flask several times, and then dried at 40°C.

   4. 某生活污水收到周边Cu2+的污染,其中Cu2+的含量约为10mg/L。将该生活污水经过一定的预处理后,采用制备的聚合物凝胶进行处理。于1L的废水中,加入2g凝胶干燥产物处理。24h后,废水中Cu2+吸附率为60%。增加凝胶产物的量使之到达6g/L时,Cu2+的去除率可以到达90%以上。 4. A certain domestic sewage is polluted by surrounding Cu 2+ , and the content of Cu 2+ is about 10mg/L. After a certain pretreatment, the domestic sewage is treated with the prepared polymer gel. In 1L of waste water, add 2g of gel-dried product for treatment. After 24h, the adsorption rate of Cu 2+ in wastewater was 60%. When increasing the amount of gel product to 6g/L, the removal rate of Cu 2+ can reach more than 90%.

实施例15: Example 15:

1.称取一定质量2-丙烯酰胺基-2-甲基丙磺酸单体(简称AMPS)溶解于去离子水中,充分溶解混合均匀作为组分A。然后,向上述溶液中加入一定量丙烯酸羟乙酯单体(简称HEA),混合均匀,作为组分B;蒸馏水作为组分C,按(A+B):C为3:7进行混合,其中A:B为2:3 (mol/mol),使用超声波对混合物进行处理使混合均匀。 1. Weigh a certain mass of 2-acrylamido-2-methylpropanesulfonic acid monomer (AMPS for short) and dissolve it in deionized water, fully dissolve and mix evenly as component A. Then, add a certain amount of hydroxyethyl acrylate monomer (referred to as HEA) to the above solution, mix well, as component B; distilled water as component C, mix according to (A+B):C ratio of 3:7, where A:B is 2:3 (mol/mol), and the mixture is treated with ultrasonic waves to make the mixture uniform.

2. 充氮气后,在-78℃的温度下,控制辐射剂量范围在1×103~1×106Gy,采用高能射线(137Cs-γ射线)辐照聚合形成聚合物水凝胶。 2. After filling with nitrogen, at a temperature of -78°C, control the radiation dose in the range of 1×10 3 to 1×10 6 Gy, and use high-energy rays ( 137 Cs-γ rays) to irradiate and polymerize to form polymer hydrogels.

3.将辐射后水凝胶切成1cm×1cm×1cm小块放在三角瓶中多次洗涤后,在40℃温度下烘干。 3. The irradiated hydrogel was cut into small pieces of 1 cm×1 cm×1 cm, washed in a Erlenmeyer flask several times, and then dried at 40°C.

   4. 某电镀废水含有大量的重金属离子,其中Cr3+的含量约为500mg/L。将该电镀废水经过一定的预处理后,采用制备的聚合物凝胶进行处理。于1L的废水中,加入2g凝胶干燥产物处理。24h后,废水中Cr3+吸附率为40%。增加凝胶产物的量使之到达10g/L时,Cr3+的去除率可以到达90%以上。 4. A certain electroplating wastewater contains a large amount of heavy metal ions, among which the content of Cr 3+ is about 500mg/L. After a certain pretreatment, the electroplating wastewater is treated with the prepared polymer gel. In 1L of waste water, add 2g of gel-dried product for treatment. After 24h, the adsorption rate of Cr 3+ in wastewater was 40%. When the amount of gel product is increased to 10g/L, the removal rate of Cr 3+ can reach more than 90%.

实施例16: Example 16:

1.称取一定质量2-丙烯酰胺基-2-甲基丙磺酸单体(简称AMPS)溶解于去离子水中,充分溶解混合均匀作为组分A。然后,向上述溶液中加入一定量丙烯酸羟乙酯单体(简称HEA),混合均匀,作为组分B;蒸馏水作为组分C,按(A+B):C为3:7进行混合,其中A:B为2:3 (mol/mol),使用超声波对混合物进行处理使混合均匀。 1. Weigh a certain mass of 2-acrylamido-2-methylpropanesulfonic acid monomer (AMPS for short) and dissolve it in deionized water, fully dissolve and mix evenly as component A. Then, add a certain amount of hydroxyethyl acrylate monomer (referred to as HEA) to the above solution, mix well, as component B; distilled water as component C, mix according to (A+B):C ratio of 3:7, where A:B is 2:3 (mol/mol), and the mixture is treated with ultrasonic waves to make the mixture uniform.

2. 充氮气后,在-78℃的温度下,控制辐射剂量范围在1×103~1×106Gy,采用高能射线(137Cs-γ射线)辐照聚合形成聚合物水凝胶。 2. After filling with nitrogen, at a temperature of -78°C, control the radiation dose in the range of 1×10 3 to 1×10 6 Gy, and use high-energy rays ( 137 Cs-γ rays) to irradiate and polymerize to form polymer hydrogels.

3.将辐射后水凝胶切成1cm×1cm×1cm小块放在三角瓶中多次洗涤后,在40℃温度下烘干。 3. The irradiated hydrogel was cut into small pieces of 1 cm×1 cm×1 cm, washed in a Erlenmeyer flask several times, and then dried at 40°C.

   4. 某农灌井水因邻近某铅冶炼厂,受到铅污染,,其中Pb2+的含量约为4mg/L。将该井水采集部分水样,经过一定的预处理后,采用制备的聚合物凝胶进行处理。将聚合物凝胶以2g/L的比例投加至水样中,经过24h吸附后,水样中的Pb2+降低至2mg/L以下。当投加量增至8mg/L时,处理后的水样中Pb2+的浓度下降至0.2mg/L以下,去除率达到95%。 4. The well water of an agricultural irrigation is polluted by lead because it is adjacent to a lead smelting plant, and the Pb 2+ content in it is about 4mg/L. Part of the water samples were collected from the well, and after a certain pretreatment, they were treated with the prepared polymer gel. The polymer gel was added to the water sample at a ratio of 2g/L. After 24 hours of adsorption, the Pb 2+ in the water sample was reduced to below 2mg/L. When the dosage increased to 8mg/L, the concentration of Pb 2+ in the treated water samples dropped below 0.2mg/L, and the removal rate reached 95%.

实施例16 Example 16

1.称取一定质量2-丙烯酰胺基-2-甲基丙磺酸单体(简称AMPS)溶解于去离子水中,充分溶解混合均匀作为组分A。然后,向上述溶液中加入一定量丙烯酸羟乙酯单体(简称HEA),混合均匀,作为组分B;蒸馏水作为组分C,按(A+B):C为3:7进行混合,其中A:B为2:3 (mol/mol),使用超声波对混合物进行处理使混合均匀。 1. Weigh a certain mass of 2-acrylamido-2-methylpropanesulfonic acid monomer (AMPS for short) and dissolve it in deionized water, fully dissolve and mix evenly as component A. Then, add a certain amount of hydroxyethyl acrylate monomer (referred to as HEA) to the above solution, mix well, as component B; distilled water as component C, mix according to (A+B):C ratio of 3:7, where A:B is 2:3 (mol/mol), and the mixture is treated with ultrasonic waves to make the mixture uniform.

2. 充氮气后,在-78℃的温度下,控制辐射剂量范围在1×103~1×106Gy,采用高能射线(137Cs-γ射线)辐照聚合形成聚合物水凝胶。 2. After filling with nitrogen, at a temperature of -78°C, control the radiation dose in the range of 1×10 3 to 1×10 6 Gy, and use high-energy rays ( 137 Cs-γ rays) to irradiate and polymerize to form polymer hydrogels.

3.将辐射后水凝胶切成1cm×1cm×1cm小块放在三角瓶中多次洗涤后,在40℃温度下烘干。 3. The irradiated hydrogel was cut into small pieces of 1 cm×1 cm×1 cm, washed in a Erlenmeyer flask several times, and then dried at 40°C.

4. 某湖泊由于周围工业污水的排入,受到一定重金属离子的污染,其中Cd2+的含量约为1mg/L。将该湖水采集部分水样,经过一定的预处理后,采用制备的聚合物凝胶进行处理。将聚合物凝胶以2g/L的比例投加至水样中,经过24h吸附后,水样中的Cd2+降低至0.5mg/L以下。当投加量增至8mg/L时,处理后的水样中Cd2+的浓度下降至0.03mg/L以下,去除率达到94%以上。 4. Due to the discharge of surrounding industrial sewage, a certain lake was polluted by certain heavy metal ions, among which the content of Cd 2+ was about 1mg/L. Some water samples were collected from the lake, and after a certain pretreatment, they were treated with the prepared polymer gel. The polymer gel was added to the water sample at a ratio of 2g/L. After 24 hours of adsorption, the Cd 2+ in the water sample was reduced to below 0.5mg/L. When the dosage increased to 8mg/L, the concentration of Cd 2+ in the treated water samples dropped below 0.03mg/L, and the removal rate reached over 94%.

Claims (5)

1.一种吸附重金属离子的聚合物水凝胶,由丙烯酸羟乙酯和2-丙烯酰胺基-2-甲基丙磺酸两种单体辐射共聚生成,该水凝胶的特征在于其制备过程由以下步骤构成:1. A polymer hydrogel that absorbs heavy metal ions is generated by radiation copolymerization of two monomers, hydroxyethyl acrylate and 2-acrylamido-2-methylpropanesulfonic acid. The hydrogel is characterized in that it is prepared The process consists of the following steps: (1)将丙烯酸羟乙酯、2-丙烯酰胺基-2-甲基丙磺酸和蒸馏水按一定比例混合均匀;(1) Mix hydroxyethyl acrylate, 2-acrylamido-2-methylpropanesulfonic acid and distilled water in a certain proportion; (2)2-丙烯酰胺基-2-甲基丙磺酸加丙烯酸羟乙酯:水的体积比为1~2:5,2-丙烯酰胺基-2-甲基丙磺酸与丙烯酸羟乙酯的摩尔比为1:1~9;(2) 2-acrylamido-2-methylpropanesulfonic acid plus hydroxyethyl acrylate: the volume ratio of water is 1 to 2:5, 2-acrylamido-2-methylpropanesulfonic acid and hydroxyethyl acrylate The molar ratio of ester is 1:1~9; (3)混合后经过5~20min超声波处理;(3) Ultrasonic treatment for 5 to 20 minutes after mixing; (4)向(1)的混合物中充入氮气,以保证无氧状态;(4) charge nitrogen into the mixture of (1) to ensure anaerobic state; (5)在-63~-95℃温度内,采用辐射剂量为1×103~1×106Gy的高能射线辐照聚合形成水凝胶,高能射线为60Coγ射线或137Csγ射线。(5) At a temperature of -63 to -95°C, the hydrogel is irradiated and polymerized by high-energy rays with a radiation dose of 1×10 3 to 1×10 6 Gy, and the high-energy rays are 60 Co gamma rays or 137 Cs gamma rays. 2.根据权利要求1所述的吸附重金属离子的聚合物水凝胶在不同pH条件下对重金属离子吸附中的应用。2. The application of the polymer hydrogel adsorbing heavy metal ions according to claim 1 to the adsorption of heavy metal ions under different pH conditions. 3.根据权利要求1所述的吸附重金属离子的聚合物水凝胶在处理工业废水中对重金属离子吸附中的应用。3. the application of the polymer hydrogel adsorbing heavy metal ions according to claim 1 in the adsorption of heavy metal ions in the treatment of industrial wastewater. 4.根据权利要求1所述的吸附重金属离子的聚合物水凝胶在处理生活污水中对重金属离子吸附中的应用。4. The application of the polymer hydrogel adsorbing heavy metal ions according to claim 1 in the adsorption of heavy metal ions in the treatment of domestic sewage. 5.根据权利要求1所述的吸附重金属离子的聚合物水凝胶在处理自然水体中对重金属离子吸附中的应用。5. The application of the polymer hydrogel adsorbing heavy metal ions according to claim 1 in the adsorption of heavy metal ions in the treatment of natural water bodies.
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* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102796337B (en) * 2012-06-27 2016-05-04 盐城工学院 Hydrogel material of a kind of Adsorption of Heavy Metal Ions and preparation method thereof
CN104030492A (en) * 2014-06-26 2014-09-10 南京大学 Treatment process and device of industrial wastewater containing heavy metal ions
CN104530307B (en) * 2014-12-19 2017-01-11 西南石油大学 Preparation of hydrophilic acrylic adsorption resin and application of acrylic adsorption resin in phenolic wastewater treatment
CN104804130B (en) * 2015-04-10 2017-01-11 华南理工大学 Hydrogel applicable to seawater desalination and preparation method thereof
CN105709704B (en) * 2016-02-03 2019-04-02 西北师范大学 A kind of preparation of chitosan-based adsorbent and its application in effluent containing heavy metal ions processing
CN109174047A (en) * 2018-09-30 2019-01-11 天津市金鳞水处理科技有限公司 One kind having both detection of heavy metal ion and absorbent-type polyacrylamide microgel
CN109437459B (en) * 2018-12-07 2021-06-22 童年 Mixed industrial sewage treatment method

Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1649921A (en) * 2002-05-01 2005-08-03 株式会社北海道Tlo (Semi)interpenetrating mesh structure hydrogel and manufacturing method thereof
US7176247B1 (en) * 2003-06-27 2007-02-13 The United States Of America As Represented By The Secretary Of The Army Interpenetrating polymer network
CN101397347A (en) * 2007-09-27 2009-04-01 北京师范大学 High intensity hydrogel, preparation method and use thereof

Family Cites Families (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
EP1620076A4 (en) * 2003-04-25 2010-08-25 Kos Life Sciences Inc Formation of strong superporous hydrogels

Patent Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1649921A (en) * 2002-05-01 2005-08-03 株式会社北海道Tlo (Semi)interpenetrating mesh structure hydrogel and manufacturing method thereof
US7176247B1 (en) * 2003-06-27 2007-02-13 The United States Of America As Represented By The Secretary Of The Army Interpenetrating polymer network
CN101397347A (en) * 2007-09-27 2009-04-01 北京师范大学 High intensity hydrogel, preparation method and use thereof

Non-Patent Citations (7)

* Cited by examiner, † Cited by third party
Title
Charles W. Walker Jr..Proton-conducting polymer membrane comprised of a copolymer of 2-acrylamido-2-methylpropanesulfonic acid and 2-hydroxyethyl methacrylate.《Journal of Power Sources》.2002,第110卷(第1期),
Isotachophoresis of synthetic ion-containing polymers separation of copolymer mixtures of poly(2-hydroxyethylmethacrylate-CO-2-acrylamido-2-methylpropanesulfonate);L.Ronald Whitlock等;《Journal of Chromatography》;19861231;第368卷;第125-134页 *
L.Ronald Whitlock等.Isotachophoresis of synthetic ion-containing polymers separation of copolymer mixtures of poly(2-hydroxyethylmethacrylate-CO-2-acrylamido-2-methylpropanesulfonate).《Journal of Chromatography》.1986,第368卷125-134.
Proton-conducting polymer membrane comprised of a copolymer of 2-acrylamido-2-methylpropanesulfonic acid and 2-hydroxyethyl methacrylate;Charles W. Walker Jr.;《Journal of Power Sources》;20020720;第110卷(第1期);第144-151页 *
林文廉等.辐射聚合及其用途.《让射线造福人类》.北京师范大学出版社,1997,(第1版),第161-162页. *
辐射诱导合成水凝胶及其处理重金属废水的研究进展;陈玉伟等;《化学进展》;20091024;第21卷(第10期);第1节第6段,第3节第1段 *
陈玉伟等.辐射诱导合成水凝胶及其处理重金属废水的研究进展.《化学进展》.2009,第21卷(第10期),2250-2256.

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