CN107376872B - Preparation method of chitosan-soybean protein composite porous microspheres for lead adsorption - Google Patents

Preparation method of chitosan-soybean protein composite porous microspheres for lead adsorption Download PDF

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CN107376872B
CN107376872B CN201710663948.9A CN201710663948A CN107376872B CN 107376872 B CN107376872 B CN 107376872B CN 201710663948 A CN201710663948 A CN 201710663948A CN 107376872 B CN107376872 B CN 107376872B
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吴雄志
庞晓霞
李娜
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Guilin University of Technology
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Abstract

The invention discloses a preparation method of chitosan-soybean protein composite porous microspheres for lead adsorption. The chitosan-soybean protein composite porous microspheres are prepared by taking soybean protein and chitosan as raw materials and crosslinking through glutaraldehyde, and are taken as adsorbing materials to carry out micro-column adsorption on lead in a solution, and the adsorption capacity of the chitosan-soybean protein composite porous microspheres on the lead is 42.8 mg/g. The invention overcomes the defects of complex preparation and high price of the existing material, and the defects of complex static adsorption operation, complex steps and the like, reduces the material preparation cost, reduces the manual operation steps, simplifies the operation flow and improves the lead adsorption efficiency.

Description

用于铅吸附的壳聚糖-大豆蛋白复合多孔微球的制备方法Preparation method of chitosan-soybean protein composite porous microspheres for lead adsorption

技术领域technical field

本发明涉及一种用于铅吸附的壳聚糖-大豆蛋白复合多孔微球的制备方法。The invention relates to a preparation method of chitosan-soybean protein composite porous microspheres for lead adsorption.

背景技术Background technique

随着全球工业发展,铅污染已对环境和人类健康造成了极大威胁,迫切需要研发快速、便捷的铅吸附材料,以满足环境检测等需求。With the development of global industry, lead pollution has posed a great threat to the environment and human health. There is an urgent need to develop fast and convenient lead adsorption materials to meet the needs of environmental testing.

目前,分离富集水中镉的方法有沉淀、离子交换、吸附等。其中,吸附法因简便、高效且吸附材料可循环使用而被广泛使用。At present, the methods for separating and enriching cadmium in water include precipitation, ion exchange, adsorption, etc. Among them, the adsorption method is widely used because it is simple, efficient, and the adsorption material can be recycled.

目前用于铅吸附的壳聚糖-大豆蛋白复合多孔微球制备暂未有相关研究。At present, there is no relevant research on the preparation of chitosan-soybean protein composite porous microspheres for lead adsorption.

发明内容SUMMARY OF THE INVENTION

本发明在于提供一种用于铅吸附的壳聚糖-大豆蛋白复合多孔微球的制备方法。The present invention provides a preparation method of chitosan-soybean protein composite porous microspheres for lead adsorption.

构思如下:虽然目前各种吸附材料用于铅的吸附,其制备繁琐,成本高昂。大豆蛋白分子结构中具有丰富的酰胺基团,壳聚糖分子中含有大量氨基,因此,利用大豆蛋白和壳聚糖制备价格低廉吸附材料用于铅的吸附,材料制备简单,具有实际应用价值。在本实验中,利用壳聚糖-大豆蛋白复合多孔微球作为微柱吸附材料,对样品溶液中铅进行动态吸附和分离,减少人工操作,简化操作过程。The idea is as follows: Although various adsorption materials are currently used for the adsorption of lead, their preparation is cumbersome and expensive. The molecular structure of soybean protein is rich in amide groups, and the chitosan molecule contains a large number of amino groups. Therefore, the use of soybean protein and chitosan to prepare low-cost adsorption materials for lead adsorption is simple in material preparation and has practical application value. In this experiment, the chitosan-soybean protein composite porous microspheres were used as the adsorption material for the microcolumns to dynamically adsorb and separate the lead in the sample solution, reducing the manual operation and simplifying the operation process.

本发明涉及壳聚糖-大豆蛋白复合多孔微球及铅的动态微柱吸附。当样品溶液中铅通过装载了壳聚糖-大豆蛋白复合多孔微球的微柱时,铅与微球材料上基团作用而被吸附,然后用洗脱液将铅洗脱并进行原子吸收光谱测定,检验材料对铅的吸附能力。The invention relates to chitosan-soybean protein composite porous microspheres and dynamic microcolumn adsorption of lead. When the lead in the sample solution passes through the microcolumns loaded with chitosan-soybean protein composite porous microspheres, the lead interacts with the groups on the microsphere material to be adsorbed, and then the lead is eluted with the eluent and subjected to atomic absorption spectroscopy Determination and testing of the material's ability to adsorb lead.

具体步骤如下:Specific steps are as follows:

(1)壳聚糖-大豆蛋白复合多孔微球制备:(1) Preparation of chitosan-soybean protein composite porous microspheres:

称取4g壳聚糖于100mL烧杯中,加入50mL质量百分比浓度为2%的醋酸溶液,搅拌溶解后静置12小时,除去溶液中气泡得到壳聚糖溶液,备用;将2.0g大豆蛋白和40mL二次水加入到100mL烧杯中,搅拌至溶解完全得到大豆蛋白溶液,备用;将40mL上述壳聚糖溶液和40mL上述大豆蛋白溶液混合,并加入2.0g纳米二氧化硅,搅拌均匀得到壳聚糖-大豆蛋白-二氧化硅混合液,备用。Weigh 4g of chitosan in a 100mL beaker, add 50mL of acetic acid solution with a concentration of 2% by mass, stir and dissolve, and let stand for 12 hours, remove air bubbles in the solution to obtain a chitosan solution, which is for later use; 2.0g soybean protein and 40mL The secondary water was added to a 100mL beaker, stirred until it was completely dissolved to obtain a soybean protein solution, which was used for later use; 40mL of the above-mentioned chitosan solution and 40mL of the above-mentioned soybean protein solution were mixed, and 2.0g of nano-silica was added, and stirred to obtain chitosan. -Soy protein-silica mixture, set aside.

取140mL液体石蜡于250mL三口烧瓶中,滴加4滴分析纯活性剂司班80,机械搅拌(300r/min)30分钟,水浴升温至60℃,将60mL壳聚糖-大豆蛋白-二氧化硅混合液逐滴滴加至上述三口瓶中,继续搅拌两个小时至形成均匀油珠颗粒,然后用分析纯氢氧化钠溶液调节混合液pH为9.5,水浴温度升至90℃,再加入20mL分析纯戊二醛溶液,反应3小时后,静置、冷却后过滤得到固体微球颗粒,用水和无水乙醇交替清洗各3-5次,在索氏提取器中用质量百分比浓度为95%的乙醇提取24小时;固体微球颗粒用浓度为5.0mol/L的氢氧化钠溶液浸泡24小时,用二次水洗至中性,过滤后在40℃下烘干,过筛得到40-60目粒径的壳聚糖-大豆蛋白复合多孔微球。Take 140 mL of liquid paraffin in a 250 mL three-necked flask, add 4 drops of analytically pure active agent Span 80 dropwise, stir mechanically (300 r/min) for 30 minutes, heat the water bath to 60 °C, and add 60 mL of chitosan-soybean protein-silicon dioxide. The mixture was added dropwise to the above three-necked flask, and continued to stir for two hours until uniform oil bead particles were formed. Then, the pH of the mixture was adjusted to 9.5 with analytically pure sodium hydroxide solution, the temperature of the water bath was raised to 90 °C, and 20 mL of analysis was added. Pure glutaraldehyde solution, after 3 hours of reaction, stand still, cool and filter to obtain solid microsphere particles, alternately wash with water and absolute ethanol for 3-5 times each, in a Soxhlet extractor with a concentration of 95% by mass. Ethanol extraction for 24 hours; the solid microspheres were soaked in sodium hydroxide solution with a concentration of 5.0mol/L for 24 hours, washed with secondary water until neutral, filtered and dried at 40°C, and sieved to obtain 40-60 mesh particles Chitosan-soybean protein composite porous microspheres.

(2)壳聚糖-大豆蛋白复合多孔微球吸附铅:(2) Adsorption of lead by chitosan-soybean protein composite porous microspheres:

分离富集装置由蠕动泵、自制微型柱((7cm×0.5mm i.d.)、聚四氟乙烯管(0.8mmi.d)和连接接头构成。微柱一端塞少量玻璃棉,以湿法上柱装入步骤(1)制备的交联大豆蛋白微球,再塞入少量玻璃棉,压实并连接好,利用蠕动泵将二次蒸馏水泵入微型柱,洗涤后备用;Pb(Ⅱ)的分离富集步骤如下:将pH=5.0的Pb(Ⅱ)溶液以3.0mL/min流速通过微型柱,然后用5.0mL蒸馏水以3.0mL/min流速洗去微型柱中未被吸附的离子,用10.0mL浓度为0.1mol/L的HNO3以3.6mL/min流速反向洗脱被吸附的Pb(Ⅱ);洗脱溶液用于后续原子吸收光谱测定。The separation and enrichment device is composed of a peristaltic pump, a self-made micro-column ((7cm×0.5mm id), a polytetrafluoroethylene tube (0.8mmi.d) and a connecting joint. A small amount of glass wool is plugged at one end of the micro-column, and the column is loaded by a wet method. Enter the cross-linked soybean protein microspheres prepared in step (1), and then insert a small amount of glass wool, compact and connect well, use a peristaltic pump to pump secondary distillation into the micro-column, wash it for later use; the separation of Pb(II) is rich in The collection steps are as follows: the Pb(II) solution with pH=5.0 is passed through the micro-column at a flow rate of 3.0 mL/min, and then the unadsorbed ions in the micro-column are washed with 5.0 mL of distilled water at a flow rate of 3.0 mL/min. The adsorbed Pb(II) was reversely eluted with 0.1 mol/L HNO 3 at a flow rate of 3.6 mL/min; the eluted solution was used for subsequent atomic absorption spectrometry.

(3)检测方法:(3) Detection method:

测定仪器:原子吸收分光光度计(北京普析通用仪器有限责任公司);石墨炉原子吸收光谱测定Pb的仪器条件设置:波长283.3nm,狭缝0.5nm,灯电流2.0mA,原子化器高度-0.2mm;石墨炉原子吸收光谱测定程序如表1。利用石墨炉原子吸收光谱法测定上述步骤(2)所得洗脱液中Pb(Ⅱ)浓度。Determination instrument: atomic absorption spectrophotometer (Beijing Puxi General Instrument Co., Ltd.); instrument conditions for the determination of Pb by graphite furnace atomic absorption spectrometry: wavelength 283.3nm, slit 0.5nm, lamp current 2.0mA, atomizer height- 0.2mm; the measurement procedure of graphite furnace atomic absorption spectrometry is shown in Table 1. The concentration of Pb(II) in the eluate obtained in the above step (2) was determined by graphite furnace atomic absorption spectrometry.

表1:石墨炉原子吸收光谱测定程序Table 1: Graphite Furnace Atomic Absorption Spectrometry Procedure

程序program 温度(℃)temperature(℃) 升温速度(℃/s)Heating rate (℃/s) 保持时间(s)Hold time (s) 干燥dry 8080 55 55 干燥dry 100100 1010 1010 灰化Ashing 600600 1010 1010 原子化atomized 19001900 00 44 净化purify 19501950 11 11

(4)壳聚糖-大豆蛋白复合多孔微球对铅的吸附容量测定:(4) Determination of the adsorption capacity of chitosan-soybean protein composite porous microspheres for lead:

火焰原子吸收光谱测定铅的条件:波长283.3nm,狭缝0.5nm,灯电流2.0mA,燃烧器高度5.0mm,乙炔流量1500mL/min,空气流量5000mL/min。将20.0μg/mL Pb(Ⅱ)溶液按步骤(2)进行吸附,每10mL收集一次流出液,直至流出液中铅浓度与原来溶液浓度相同即终止实验,用火焰原子吸收光谱法测定各流出液中Pb(Ⅱ)浓度,并计算出壳聚糖-大豆蛋白复合多孔微球对铅的吸附容量。The conditions for the determination of lead by flame atomic absorption spectrometry: wavelength 283.3nm, slit 0.5nm, lamp current 2.0mA, burner height 5.0mm, acetylene flow 1500mL/min, air flow 5000mL/min. The 20.0 μg/mL Pb(II) solution was adsorbed according to step (2), and the effluent was collected every 10 mL. The experiment was terminated until the lead concentration in the effluent was the same as that of the original solution, and each effluent was measured by flame atomic absorption spectrometry. The concentration of Pb(Ⅱ) was calculated, and the adsorption capacity of chitosan-soybean protein composite porous microspheres for lead was calculated.

本发明克服了已有材料制备复杂、价格高昂的缺点,以及静态吸附操作繁琐、步骤复杂等缺点,降低了材料制备成本,减少人工操作步骤,简化了操作流程,提高了铅吸附效率。The invention overcomes the disadvantages of complicated preparation and high price of existing materials, as well as the disadvantages of cumbersome static adsorption operation and complicated steps, reduces material preparation cost, reduces manual operation steps, simplifies operation process, and improves lead adsorption efficiency.

附图说明Description of drawings

图1为本发明实施例制得的壳聚糖-大豆蛋白复合多孔微球的扫描电镜照片。1 is a scanning electron microscope photograph of the chitosan-soybean protein composite porous microspheres prepared in the embodiment of the present invention.

具体实施方式Detailed ways

实施例:Example:

(1)壳聚糖-大豆蛋白复合多孔微球制备:(1) Preparation of chitosan-soybean protein composite porous microspheres:

称取4g壳聚糖于100mL烧杯中,加入50mL质量百分比浓度为2%的醋酸溶液,搅拌溶解后静置12小时,除去溶液中气泡得到壳聚糖溶液,备用。2.0g大豆蛋白和40mL二次水加入到100mL烧杯中,搅拌至溶解完全得到大豆蛋白溶液,备用;将40mL上述壳聚糖溶液和40mL上述大豆蛋白溶液混合,并加入2.0g纳米二氧化硅,搅拌均匀得到壳聚糖-大豆蛋白-二氧化硅混合液,备用。Weigh 4g of chitosan in a 100mL beaker, add 50mL of acetic acid solution with a concentration of 2% by mass, stir to dissolve, and let stand for 12 hours, remove air bubbles in the solution to obtain a chitosan solution for later use. 2.0g soybean protein and 40mL secondary water were added into a 100mL beaker, stirred until dissolved completely to obtain a soybean protein solution, for subsequent use; 40mL of the above-mentioned chitosan solution and 40mL of the above-mentioned soybean protein solution were mixed, and 2.0g of nano-silica was added, Stir evenly to obtain a chitosan-soybean protein-silicon dioxide mixed solution, which is for later use.

取140mL液体石蜡于250mL三口烧瓶中,滴加4滴分析纯活性剂司班80,机械搅拌(300r/min)30分钟,水浴升温至60℃,将60mL壳聚糖-大豆蛋白-二氧化硅混合液逐滴滴加至上述三口瓶中,继续搅拌两个小时至形成均匀油珠颗粒,然后用分析纯氢氧化钠溶液调节混合液pH为9.5,水浴温度升至90℃,再加入20mL分析纯戊二醛溶液,反应3小时后,静置、冷却后过滤得到固体微球颗粒,用水和无水乙醇交替清洗各3次,在索氏提取器中用质量百分比浓度为95%的乙醇提取24小时。固体微球颗粒用浓度为5.0mol/L的氢氧化钠溶液浸泡24小时,用二次水洗至中性,过滤后在40℃下烘干,过筛得到40-60目粒径的壳聚糖-大豆蛋白复合多孔微球。壳聚糖-大豆蛋白复合多孔微球的扫描电镜照片如图1。Take 140 mL of liquid paraffin in a 250 mL three-necked flask, add 4 drops of analytically pure active agent Span 80 dropwise, stir mechanically (300 r/min) for 30 minutes, heat the water bath to 60 °C, and add 60 mL of chitosan-soybean protein-silicon dioxide. The mixture was added dropwise to the above three-necked flask, and continued to stir for two hours until uniform oil bead particles were formed. Then, the pH of the mixture was adjusted to 9.5 with analytically pure sodium hydroxide solution, the temperature of the water bath was raised to 90 °C, and 20 mL of analysis was added. Pure glutaraldehyde solution, after 3 hours of reaction, stand, cool and filter to obtain solid microsphere particles, alternately wash with water and absolute ethanol 3 times each, and extract with 95% ethanol in a Soxhlet extractor 24 hours. The solid microsphere particles were soaked in sodium hydroxide solution with a concentration of 5.0mol/L for 24 hours, washed with secondary water until neutral, filtered and dried at 40°C, and sieved to obtain chitosan with a particle size of 40-60 mesh. - Soy protein composite porous microspheres. The scanning electron microscope photograph of chitosan-soybean protein composite porous microspheres is shown in Figure 1.

(2)壳聚糖-大豆蛋白复合多孔微球吸附铅:(2) Adsorption of lead by chitosan-soybean protein composite porous microspheres:

分离富集装置由蠕动泵、自制微型柱(7cm×0.5mm i.d.)、聚四氟乙烯管(0.8mmi.d)和连接接头构成。微柱一端塞少量玻璃棉,以湿法上柱装入步骤(1)制备的交联大豆蛋白微球,再塞入少量玻璃棉,压实并连接好,利用蠕动泵将二次蒸馏水泵入微型柱,洗涤后备用;Pb(Ⅱ)的分离富集步骤如下:将pH=5.0的Pb(Ⅱ)溶液以3.0mL/min流速通过微型柱,然后用5.0mL蒸馏水以3.0mL/min流速洗去微型柱中未被吸附的离子,用10.0mL浓度为0.1mol/L的HNO3以3.6mL/min流速反向洗脱被吸附的Pb(Ⅱ);洗脱溶液用于后续原子吸收光谱测定。The separation and enrichment device consists of a peristaltic pump, a self-made micro-column (7cm×0.5mm id), a polytetrafluoroethylene tube (0.8mmi.d) and a connecting joint. One end of the micro-column is plugged with a small amount of glass wool, and the cross-linked soybean protein microspheres prepared in step (1) are loaded into the column by wet method, and then a small amount of glass wool is plugged in, compacted and connected well, and the secondary distilled water is pumped in by a peristaltic pump. The micro-column is used after washing; the separation and enrichment steps of Pb(II) are as follows: Pb(II) solution with pH=5.0 is passed through the micro-column at a flow rate of 3.0mL/min, and then washed with 5.0mL distilled water at a flow rate of 3.0mL/min To remove the unadsorbed ions in the micro-column, use 10.0 mL of HNO 3 with a concentration of 0.1 mol/L to reverse elute the adsorbed Pb(II) at a flow rate of 3.6 mL/min; the elution solution is used for subsequent atomic absorption spectrometry determination .

(3)检测方法:(3) Detection method:

测定仪器:原子吸收分光光度计(北京普析通用仪器有限责任公司);石墨炉原子吸收光谱测定Pb的仪器条件设置:波长283.3nm,狭缝0.5nm,灯电流2.0mA,原子化器高度-0.2mm;石墨炉原子吸收光谱测定程序如表1。利用石墨炉原子吸收光谱法测定上述步骤(2)所得洗脱液中Pb(Ⅱ)浓度。Determination instrument: atomic absorption spectrophotometer (Beijing Puxi General Instrument Co., Ltd.); instrument conditions for the determination of Pb by graphite furnace atomic absorption spectrometry: wavelength 283.3nm, slit 0.5nm, lamp current 2.0mA, atomizer height- 0.2mm; the measurement procedure of graphite furnace atomic absorption spectrometry is shown in Table 1. The concentration of Pb(II) in the eluate obtained in the above step (2) was determined by graphite furnace atomic absorption spectrometry.

表1:石墨炉原子吸收光谱测定程序Table 1: Graphite Furnace Atomic Absorption Spectrometry Procedure

程序program 温度(℃)temperature(℃) 升温速度(℃/s)Heating rate (℃/s) 保持时间(s)Hold time (s) 干燥dry 8080 55 55 干燥dry 100100 1010 1010 灰化Ashing 600600 1010 1010 原子化atomized 19001900 00 44 净化purify 19501950 11 11

(4)壳聚糖-大豆蛋白复合多孔微球对铅的吸附容量测定:(4) Determination of the adsorption capacity of chitosan-soybean protein composite porous microspheres for lead:

火焰原子吸收光谱测定铅的条件:波长283.3nm,狭缝0.5nm,灯电流2.0mA,燃烧器高度5.0mm,乙炔流量1500mL/min,空气流量5000mL/min。将20.0μg/mL的Pb(Ⅱ)溶液按步骤(2)进行吸附,每10mL收集一次流出液,直至流出液中铅浓度与原来溶液浓度相同即终止实验,用火焰原子吸收光谱法测定流出液中Pb(Ⅱ)浓度,并计算出壳聚糖-大豆蛋白复合多孔微球对铅的吸附容量为42.8mg/g。The conditions for the determination of lead by flame atomic absorption spectrometry: wavelength 283.3nm, slit 0.5nm, lamp current 2.0mA, burner height 5.0mm, acetylene flow 1500mL/min, air flow 5000mL/min. The 20.0 μg/mL Pb(II) solution was adsorbed according to step (2), and the effluent was collected every 10 mL. The experiment was terminated until the lead concentration in the effluent was the same as that of the original solution, and the effluent was measured by flame atomic absorption spectrometry. The Pb(Ⅱ) concentration was calculated, and the adsorption capacity of chitosan-soybean protein composite porous microspheres for lead was calculated to be 42.8 mg/g.

Claims (1)

1.一种用于铅吸附的壳聚糖-大豆蛋白复合多孔微球的制备方法,其特征在于具体步骤为:1. a preparation method for the chitosan-soybean protein composite porous microspheres for lead adsorption, is characterized in that concrete steps are: (1)壳聚糖-大豆蛋白复合多孔微球制备:(1) Preparation of chitosan-soybean protein composite porous microspheres: 称取4g壳聚糖于100mL烧杯中,加入50 mL质量百分比浓度为2%的醋酸溶液,搅拌溶解后静置12小时,除去溶液中气泡得到壳聚糖溶液,备用;将2.0 g大豆蛋白和40 mL二次水加入到100 mL烧杯中,搅拌至溶解完全得到大豆蛋白溶液,备用;将40 mL上述壳聚糖溶液和40 mL上述大豆蛋白溶液混合,并加入2.0g纳米二氧化硅,搅拌均匀得到壳聚糖-大豆蛋白-二氧化硅混合液,备用;Weigh 4 g of chitosan in a 100 mL beaker, add 50 mL of acetic acid solution with a mass percentage concentration of 2%, stir and dissolve and let stand for 12 hours, remove air bubbles in the solution to obtain a chitosan solution, which is for later use; 2.0 g of soybean protein and 40 mL of secondary water was added to a 100 mL beaker, stirred until it was completely dissolved to obtain a soybean protein solution, which was used for later use; 40 mL of the above chitosan solution and 40 mL of the above soybean protein solution were mixed, and 2.0 g of nano-silica was added, and stirred. The chitosan-soybean protein-silicon dioxide mixed solution is uniformly obtained, for subsequent use; 取140mL液体石蜡于250mL三口烧瓶中,滴加4滴分析纯活性剂司班80,300r/min机械搅拌30分钟,水浴升温至60℃,将60 mL壳聚糖-大豆蛋白-二氧化硅混合液逐滴滴加至上述三口瓶中,继续搅拌两个小时至形成均匀油珠颗粒,然后用分析纯氢氧化钠溶液调节混合液pH为9.5,水浴温度升至90℃,再加入20 mL分析纯戊二醛溶液,反应3小时后,静置、冷却后过滤得到固体微球颗粒,用水和无水乙醇交替清洗各3-5次,在索氏提取器中用质量百分比浓度为95%的乙醇提取24小时;固体微球颗粒用浓度为5.0 mol/L的氢氧化钠溶液浸泡24小时,用二次水洗至中性,过滤后在40℃下烘干,过筛得到40-60目粒径的壳聚糖-大豆蛋白复合多孔微球;Take 140 mL of liquid paraffin in a 250 mL three-necked flask, add 4 drops of analytically pure active agent Span 80 dropwise, stir mechanically at 300 r/min for 30 minutes, heat the water bath to 60 °C, and mix 60 mL of chitosan-soybean protein-silicon dioxide. The liquid was added dropwise to the above three-necked bottle, and continued to stir for two hours until uniform oil beads were formed. Then, the pH of the mixture was adjusted to 9.5 with analytical pure sodium hydroxide solution, the temperature of the water bath was raised to 90 °C, and 20 mL was added for analysis. Pure glutaraldehyde solution, after 3 hours of reaction, stand still, cool and filter to obtain solid microsphere particles, alternately wash with water and absolute ethanol for 3-5 times each, in a Soxhlet extractor with a mass percentage concentration of 95%. Ethanol extraction for 24 hours; the solid microspheres were soaked in sodium hydroxide solution with a concentration of 5.0 mol/L for 24 hours, washed with secondary water until neutral, filtered and dried at 40 ° C, and sieved to obtain 40-60 mesh particles Chitosan-soybean protein composite porous microspheres with diameters; (2)壳聚糖-大豆蛋白复合多孔微球吸附铅:(2) Adsorption of lead by chitosan-soybean protein composite porous microspheres: 分离富集装置由蠕动泵、自制微型柱和连接接头构成;微柱一端塞少量玻璃棉,以湿法上柱装入步骤(1)制备的交联大豆蛋白微球,再塞入少量玻璃棉,压实并连接好,利用蠕动泵将二次蒸馏水泵入微型柱,洗涤后备用;Pb(Ⅱ)的分离富集步骤如下:将pH=5.0的Pb(Ⅱ)溶液以3.0 mL/min流速通过微型柱,然后用5.0mL 蒸馏水以3.0 mL/min流速洗去微型柱中未被吸附的离子,用10.0 mL浓度为0.1 mol/L 的HNO3以3.6 mL/min流速反向洗脱被吸附的Pb(Ⅱ);洗脱溶液用于后续原子吸收光谱测定;The separation and enrichment device is composed of a peristaltic pump, a self-made micro-column and a connecting joint; one end of the micro-column is plugged with a small amount of glass wool, and the cross-linked soybean protein microspheres prepared in step (1) are loaded into the column by wet method, and then a small amount of glass wool is inserted into the column. , compacted and connected well, use the peristaltic pump to pump the secondary distilled water into the micro-column, wash it for later use; the separation and enrichment steps of Pb(II) are as follows: Pb(II) solution with pH=5.0 is pumped at a flow rate of 3.0 mL/min Passed through the micro-column, then washed the unadsorbed ions in the micro-column with 5.0 mL of distilled water at a flow rate of 3.0 mL/min, and reversely eluted the adsorbed ions with 10.0 mL of HNO3 with a concentration of 0.1 mol/L at a flow rate of 3.6 mL/min. of Pb(II); the elution solution was used for subsequent atomic absorption spectrometry; (3)检测方法:(3) Detection method: 测定仪器:原子吸收分光光度计;石墨炉原子吸收光谱测定Pb的仪器条件设置:波长283.3 nm,狭缝0.5 nm,灯电流2.0 mA,原子化器高度-0.2 mm;石墨炉原子吸收光谱测定程序如表1;利用石墨炉原子吸收光谱法测定上述步骤(2)所得洗脱液中Pb(Ⅱ)浓度;Determination instrument: atomic absorption spectrophotometer; instrument conditions for the determination of Pb by graphite furnace atomic absorption spectrometry: wavelength 283.3 nm, slit 0.5 nm, lamp current 2.0 mA, atomizer height -0.2 mm; graphite furnace atomic absorption spectrometry program As shown in Table 1; use graphite furnace atomic absorption spectrometry to measure the concentration of Pb(II) in the eluate obtained in the above step (2); 表1 :石墨炉原子吸收光谱测定程序Table 1: Graphite Furnace Atomic Absorption Spectrometry Procedure 程序program 温度(℃)Temperature (℃) 升温速度(℃/s)Heating rate (℃/s) 保持时间(s)Hold time (s) 干燥dry 8080 55 55 干燥dry 100100 1010 1010 灰化Ashing 600600 1010 1010 原子化atomized 19001900 00 44 净化purify 19501950 11 11
(4)壳聚糖-大豆蛋白复合多孔微球对铅的吸附容量测定:(4) Determination of the adsorption capacity of chitosan-soybean protein composite porous microspheres for lead: 火焰原子吸收光谱测定铅的条件:波长283.3 nm,狭缝0.5 nm,灯电流2.0 mA,燃烧器高度5.0mm,乙炔流量1500 mL/min,空气流量5000 mL/min;将20.0 μg /mL的 Pb(Ⅱ)溶液按步骤(2)进行吸附,每10 mL收集一次流出液,直至流出液中铅浓度与原来溶液浓度相同即终止实验,用火焰原子吸收光谱法测定各流出液中Pb(Ⅱ)浓度,并计算出壳聚糖-大豆蛋白复合多孔微球对铅的吸附容量。The conditions for the determination of lead by flame atomic absorption spectrometry: wavelength 283.3 nm, slit 0.5 nm, lamp current 2.0 mA, burner height 5.0 mm, acetylene flow 1500 mL/min, air flow 5000 mL/min; 20.0 μg/mL Pb (II) The solution is adsorbed according to step (2), the effluent is collected every 10 mL, and the experiment is terminated until the lead concentration in the effluent is the same as the original solution concentration, and the Pb(II) in each effluent is determined by flame atomic absorption spectrometry. concentration, and the adsorption capacity of chitosan-soybean protein composite porous microspheres for lead was calculated.
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Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101391199A (en) * 2007-09-21 2009-03-25 中国科学院化学研究所 Multi-cavity composite micro/nanocapsules and its preparation method and device
CN101805452A (en) * 2010-03-11 2010-08-18 南昌航空大学 Preparation method of crosslinked carboxymethyl chitosan nano particle

Family Cites Families (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101675996B (en) * 2008-09-19 2011-12-14 中国科学院过程工程研究所 Chitosan nano-microspheres product and preparation method thereof
EP2451550A4 (en) * 2009-07-06 2013-11-13 Halosource Inc Dual polymer system for water recovery and separation of suspended solids from aqueous media
CN103007894B (en) * 2012-12-13 2014-12-10 南京信息工程大学 Soybean protein micro sphere material and preparation method and application of material in treating waste water containing heavy metal ion
CN103285823A (en) * 2013-05-26 2013-09-11 青岛国强环保科技有限公司 Material for absorbing and digesting industrial wastewater containing heavy metal ions
CN103266153B (en) * 2013-06-17 2014-12-31 江西科技师范大学 Production method of modified chitosan
CN103528980B (en) * 2013-09-23 2015-12-09 桂林理工大学 Utilize the flame atomic absorption spectrometry method of trace lead, cadmium in thiomalic acid modified silica-gel separation and concentration-mensuration water sample
CN105131329B (en) * 2015-10-16 2018-03-30 武汉科技大学 A kind of preparation method and application of the polyvinyl alcohol crosslinked affinity membrane of macropore chitosan of chelated metal ions

Patent Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101391199A (en) * 2007-09-21 2009-03-25 中国科学院化学研究所 Multi-cavity composite micro/nanocapsules and its preparation method and device
CN101805452A (en) * 2010-03-11 2010-08-18 南昌航空大学 Preparation method of crosslinked carboxymethyl chitosan nano particle

Non-Patent Citations (4)

* Cited by examiner, † Cited by third party
Title
Adsorption Behavior of Heavy Metal Ions from Aqueous Solution by Soy Protein Hollow Microspheres;Dagang Liu et al;《INDUSTRIAL & ENGINEERING CHEMISTRY RESEARCH》;20130813;第52卷(第32期);第11036-11044页 *
Pb2+印迹改性磁性壳聚糖纳米材料的制备及吸附性能研究;张全丽;《中国优秀硕士学位论文全文数据库 工程科技Ⅰ辑》;20130615(第6期);正文 *
壳聚糖Pb2+螯合吸附剂的性能表征;程爱华 等;《环境工程学报》;20150831;第9卷(第8期);第3597-3601页 *
戊二醛交联壳聚糖席夫碱的合成及其对Pb2+吸附性能的研究;胡惠媛 等;《试验与研究》;20161231;第43卷(第16期);第10-13页 *

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