CN103464119B - Preparation and application of a cysteine modified palm bark adsorbent - Google Patents
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Abstract
本发明公开了一种半胱氨酸改性棕榈树皮吸附剂制备方法及应用技术,特征是:将棕榈树皮,放入容器中用水浸泡,干燥粉碎,用异丙醇与NaOH溶液处理,再用环氧氯丙烷和NaOH混合溶液浸泡、煮沸,抽滤、干燥,得环氧基棕榈树皮。在反应器中,按如下组成质量百分比加入,半胱氨酸:3~11%,环氧基棕榈树皮:9~26%,碳酸钠:4~12%;水:52~82%,各组分之和为百分之百,于50±3℃恒温、搅拌、回流反应4~8 h,冷却后,用去离子水洗涤、抽滤,至滤液呈中性为止,用少量乙醇洗涤后,放在40±5℃真空干燥箱中干燥,得到半胱氨酸改性棕榈树皮。该吸附剂对重金属离子具有吸附效率高,速度快,解吸性能好,机械性能,再生能力强,既成本低又绿色环保。The invention discloses a preparation method and application technology of a cysteine-modified palm bark adsorbent, which is characterized in that: the palm bark is soaked in water in a container, dried and pulverized, treated with isopropanol and NaOH solution, Soak in a mixed solution of epichlorohydrin and NaOH, boil, filter with suction, and dry to obtain epoxy palm bark. In the reactor, add according to the following composition mass percentages, cysteine: 3~11%, epoxy palm bark: 9~26%, sodium carbonate: 4~12%; Water: 52~82%, each The sum of the components is 100%, react at a constant temperature of 50±3°C, stir, and reflux for 4~8 hours. After cooling, wash with deionized water and filter with suction until the filtrate is neutral. After washing with a small amount of ethanol, put it in Dry in a vacuum oven at 40±5°C to obtain cysteine-modified palm bark. The adsorbent has high adsorption efficiency for heavy metal ions, high speed, good desorption performance, mechanical properties, strong regeneration ability, low cost and environmental protection.
Description
技术领域 technical field
本发明涉及一种生物吸附剂的制备方法及对重金属吸附的应用技术领域,特别涉及一种半胱氨酸改性棕榈树皮吸附剂制备方法及对重金属离子吸附的应用技术。 The invention relates to a preparation method of a biosorbent and the technical field of heavy metal adsorption application, in particular to a preparation method of a cysteine-modified palm bark adsorbent and an application technology for heavy metal ion adsorption.
背景技术 Background technique
重金属,特别是汞、镉、铅、铬等具有显著毒性,它们在水体中不能被微生物降解,而只能发生各种形态相互转化和分散、富集过程。重金属对活的生物体具有很高的毒性和致癌性,并且会在生物体内富集、积累产生很高的毒性,而且还会通过食物链产生放大效应。由于重金属所产生的毒性不能生物降解,存在水体、土壤环境中的重金属离子日益受到人们的重视。除去重金属通常采用化学沉淀法、絮凝法、离子交换法和电解法等,但是这些方法均存在费用高、效率低等缺点。近年来,利用天然高分子纤维(如棉、麻、棕榈树皮、丝瓜络、甘蔗渣、花生壳等)改性合成各种吸附剂,这种吸附剂具有价廉、易得、可再生、可生物降解等优点。 Heavy metals, especially mercury, cadmium, lead, chromium, etc. have significant toxicity. They cannot be degraded by microorganisms in water, but can only undergo various forms of mutual transformation, dispersion, and enrichment. Heavy metals are highly toxic and carcinogenic to living organisms, and will be enriched and accumulated in organisms to produce high toxicity, and will also have amplifying effects through the food chain. Because the toxicity produced by heavy metals cannot be biodegraded, heavy metal ions in water and soil environments have attracted increasing attention. To remove heavy metals, chemical precipitation, flocculation, ion exchange, and electrolysis are usually used, but these methods have disadvantages such as high cost and low efficiency. In recent years, various adsorbents have been modified and synthesized by using natural polymer fibers (such as cotton, hemp, palm bark, loofah, bagasse, peanut shells, etc.), which are cheap, easy to obtain, renewable, Biodegradable and other advantages.
棕榈树是多年生的常绿乔木植物,高可达7米;干直立,不分枝,为叶鞘形成的棕衣所包;因此棕榈树皮的纤维很长、强度大,通常用作制作床垫,是十分宝贵的生态资源之一,是一种可再生资源。目前棕榈树广泛种植长江以南地带,是十分珍贵的长纤维原料。这种天然高分子材料应用制作吸附具有天然、绿色、可生物降解、机械强度大、抗腐蚀能力强等特点,棕榈树皮作为吸附剂可再生重复使用多次,而且对染料有较大吸附容量,国外对棕榈树皮化学改性和吸附性能的研究报道的很少,中国专利申请号为:201310147720.6的专利中公开了一种巯基棕榈树皮吸附剂的制备方法及应用,其特征是:在反应器中,按如下组成质量百分比加入,硫代乙醇酸:30~45%,四氢呋喃:25~40%,碱化棕榈树皮:20~35%,冰醋酸:0.5~2.5%,浓硫酸:0.15~0.3%,各组分之和为百分之百,加塞,于40~45℃下,静止反应48~60 h,然后用去离子水洗涤、抽滤、至滤液呈中性为止,用少量乙醇洗涤后,放在35~45℃烘箱中干燥,得到巯基棕榈树皮吸附剂。其巯基榈树皮吸附剂对Cd2+的吸附容量可高达286mg/g,对Pb2+的最大吸附量为521mg/g, 对Cu2+的最大吸附量为165mg/g,最高吸附率可达98%。 Palm tree is a perennial evergreen tree plant, up to 7 meters high; the trunk is erect, unbranched, and covered by a brown coat formed by leaf sheaths; therefore, the fibers of the palm bark are very long and strong, and are usually used to make mattresses , is one of the most precious ecological resources and a renewable resource. At present, palm trees are widely planted in the area south of the Yangtze River and are very precious long-fiber raw materials. This kind of natural polymer material has the characteristics of natural, green, biodegradable, high mechanical strength and strong corrosion resistance. Palm bark can be regenerated and reused many times as an adsorbent, and has a large adsorption capacity for dyes. There are very few foreign reports on the chemical modification and adsorption properties of palm bark. The Chinese patent application number is: 201310147720.6, which discloses a preparation method and application of mercapto palm bark adsorbent, which is characterized in that: In the reactor, add according to the following composition mass percentage, thioglycolic acid: 30~45%, tetrahydrofuran: 25~40%, alkalized palm bark: 20~35%, glacial acetic acid: 0.5~2.5%, concentrated sulfuric acid: 0.15~0.3%, the sum of each component is 100%, plugged, at 40~45°C, static reaction for 48~60 h, then washed with deionized water, suction filtered, until the filtrate is neutral, washed with a small amount of ethanol Finally, it is dried in an oven at 35-45°C to obtain the mercapto palm bark adsorbent. The adsorption capacity of its mercapto palm bark adsorbent for Cd 2+ can be as high as 286mg/g, the maximum adsorption capacity for Pb 2+ is 521mg/g, the maximum adsorption capacity for Cu 2+ is 165mg/g, and the highest adsorption rate can be Up to 98%.
半胱氨酸是一种常见氨基酸,具有有效的解毒作用和抗衰老作用,因此不存在污染环境的问题,另外半胱氨酸侧链上的巯基基团和羧基基团都是可以和重金属结合的官能团,采用半胱氨酸改性制备吸附剂也有报道,李青等,研究了半胱氨酸改性介孔材料吸附Hg2+,(李青等,半胱氨酸改性介孔材料对Hg2+高选择性分离富集性能研究,分析化学,2013,41(1):93~97);杨亚玲等,研究了半胱氨酸改性甘蔗渣对Cd2+的吸附性能,其对Cd2+的最大吸附容量为:122.75mg/g,(杨亚玲等,环氧氯丙烷和半胱氨酸改性甘蔗渣对Cd2+的吸附,云南化工,2010,34(1),11~14)。利用半胱氨酸改性棕榈树皮制备吸附剂,即具有巯基与某些重金属离子有很强的鳌合作用的性质,又具有天然高分子的可再生、可降解、环保友好、廉价等优点,是重要的生物资源。利用半胱氨酸改性棕榈树皮制得吸附剂未见报道。 Cysteine is a common amino acid, which has effective detoxification and anti-aging effects, so there is no problem of polluting the environment. In addition, the sulfhydryl group and carboxyl group on the side chain of cysteine can combine with heavy metals There are also reports on the preparation of adsorbents by modifying cysteine. Li Qing et al. studied the adsorption of Hg 2+ on cysteine-modified mesoporous materials, (Li Qing et al., Cysteine-modified mesoporous materials Research on the performance of highly selective separation and enrichment of Hg 2+ , Analytical Chemistry, 2013, 41 (1): 93~97); Yang Yaling et al. studied the adsorption performance of cysteine-modified bagasse on Cd 2+ . The maximum adsorption capacity for Cd 2+ is: 122.75 mg/g, (Yang Yaling et al., Adsorption of Epichlorohydrin and Cysteine Modified Bagasse to Cd 2+ , Yunnan Chemical Industry, 2010, 34(1), 11 ~14). The adsorbent is prepared by modifying palm bark with cysteine, which not only has the property of strong chelation between sulfhydryl groups and some heavy metal ions, but also has the advantages of renewable, degradable, environmentally friendly, and cheap natural polymers. , is an important biological resource. The use of cysteine to modify palm bark to prepare adsorbents has not been reported.
发明内容 Contents of the invention
本发明的目的之一是提供一种半胱氨酸改性棕榈树皮吸附剂制备方法,主要使获取的半胱氨酸改性棕榈树皮吸附剂作为水体中重金属吸附剂的吸附容量更大, 通过调节pH值的不同,可使重金属离子达到分离的目的。 One of the purposes of the present invention is to provide a method for preparing cysteine-modified palm bark adsorbent, which mainly makes the obtained cysteine-modified palm bark adsorbent have a larger adsorption capacity as heavy metal adsorbent in water , By adjusting the difference in pH value, heavy metal ions can be separated.
本发明的目的通过以下技术方案实现。 The purpose of the present invention is achieved through the following technical solutions.
一种半胱氨酸改性棕榈树皮吸附剂制备方法,特征在于该方法具有以下工艺步骤: A preparation method of cysteine modified palm bark adsorbent, characterized in that the method has the following processing steps:
(1)棕榈树皮预处理:将棕榈树皮剪成小块,用水洗涤去除泥土和杂质,放入容器中用水浸泡24~48小时,真空干燥后进行粉碎,将干燥粉碎的棕榈树皮以固液比为50~100g/L的比例,用异丙醇与1.0~3.5mol/L的NaOH溶液按体积比为1:4~10的混合溶液,室温浸泡12~20h,煮沸10~30nim,冷却后用去离子水洗涤至中性,抽滤,50~60℃烘干,得到预处理棕榈树皮; (1) Palm bark pretreatment: Cut the palm bark into small pieces, wash with water to remove soil and impurities, soak in water for 24 to 48 hours in a container, and then crush it after vacuum drying. The solid-to-liquid ratio is 50~100g/L, use a mixed solution of isopropanol and 1.0~3.5mol/L NaOH solution with a volume ratio of 1:4~10, soak at room temperature for 12~20h, boil for 10~30nm, After cooling, wash with deionized water until neutral, filter with suction, and dry at 50-60°C to obtain pretreated palm bark;
(2)环氧基棕榈树皮制备:将上述预处理棕榈树皮按100~200g/L固液比,用环氧氯丙烷与1.0~3.5mol/L的NaOH溶液按1:3~6体积比的混合溶液,室温浸泡12~20 h,再煮沸10~20min,冷却后用去离子水洗涤至中性,再乙醇洗涤,抽滤后在55~65℃下烘干,得到环氧基棕榈树皮; (2) Preparation of epoxy-based palm bark: use the above pretreated palm bark at a solid-to-liquid ratio of 100~200g/L, and use epichlorohydrin and 1.0~3.5mol/L NaOH solution at a volume of 1:3~6 The mixed solution is soaked at room temperature for 12-20 h, then boiled for 10-20 min, washed with deionized water until neutral, then washed with ethanol, filtered and dried at 55-65°C to obtain epoxy palm bark;
(3)半胱氨酸改性棕榈树皮制备:在反应器中,按如下组成质量百分比加入,半胱氨酸:3~11%,环氧基棕榈树皮:9~26%,碳酸钠:4~12%;水:52~82%,各组分之和为百分之百,于50±3℃恒温、搅拌、回流反应4~8 h,冷却后,用去离子水洗涤、抽滤,至滤液呈中性为止,用少量乙醇洗涤后,放在40±5℃真空干燥箱中干燥,得到半胱氨酸改性棕榈树皮,其中半胱氨酸与碳酸钠的质量比在1:1~1.5之间。 (3) Preparation of cysteine-modified palm bark: In the reactor, add according to the following composition mass percentage, cysteine: 3~11%, epoxy-based palm bark: 9~26%, sodium carbonate : 4~12%; water: 52~82%, the sum of each component is 100%, at 50±3℃ constant temperature, stirring, reflux reaction for 4~8 h, after cooling, wash with deionized water, suction filter, until The filtrate is washed with a small amount of ethanol until it is neutral, and then dried in a vacuum oven at 40±5°C to obtain cysteine-modified palm bark, wherein the mass ratio of cysteine to sodium carbonate is 1:1 ~1.5 between.
本发明的另一目的是提供一种半胱氨酸改性棕榈树皮吸附剂在水体系中对重金属离子,如Cd2+、Pb2+、Hg2+、Cu2+的吸附,特点为:将制备好的半胱氨酸改性棕榈树皮吸附剂用去离子水浸泡2~4h,按静态法吸附。 Another object of the present invention is to provide a cysteine-modified palm bark adsorbent for the adsorption of heavy metal ions in water systems, such as Cd 2+ , Pb 2+ , Hg 2+ , Cu 2+ , which is characterized by : Soak the prepared cysteine-modified palm bark adsorbent with deionized water for 2-4 hours, and adsorb according to the static method.
将制备好的环半胱氨酸改性棕榈树皮吸附剂用去离子水浸泡2~4h,按动态法吸附。 The prepared cyclocysteine-modified palm bark adsorbent was soaked in deionized water for 2-4 hours, and adsorbed according to the dynamic method.
本发明的优点及效果是: Advantage and effect of the present invention are:
(1)本发明获得的半胱氨酸改性棕榈树皮吸附剂具有良好的物理化学稳定性和优异的机械强度,与改性花生壳、甘蔗渣相比对重金属的吸附容量大,耐磨,反复使用次数多,可达10次以上; (1) The cysteine-modified palm bark adsorbent obtained in the present invention has good physical and chemical stability and excellent mechanical strength. Compared with modified peanut shells and bagasse, it has a large adsorption capacity for heavy metals and is wear-resistant , repeated use times, up to more than 10 times;
(2)本发明获得的半胱氨酸改性棕榈树皮吸附剂对水体中重金属离子的吸附和洗脱,吸附效率高,速度快,解吸性能好,能够在较宽的酸碱范围内使用; (2) The cysteine-modified palm bark adsorbent obtained in the present invention can absorb and elute heavy metal ions in water, with high adsorption efficiency, fast speed, good desorption performance, and can be used in a wide acid-base range ;
(3)稳定性好,是天然绿色产品,可生物降解; (3) Good stability, is a natural green product, biodegradable;
(4)合成的过程要求的条件容易控制,能耗低,操作简单,整个生产过程中无“三废”排放,属于清洁生产工艺,易于工业化生产。 (4) The conditions required for the synthesis process are easy to control, the energy consumption is low, the operation is simple, and there is no "three wastes" discharge in the whole production process, which belongs to the clean production process and is easy for industrial production.
具体实施方式 Detailed ways
实施例1 Example 1
(1)棕榈树皮预处理:将棕榈树皮剪成小块,用水洗涤去除泥土和杂质,放入容器中用水浸泡24h,真空干燥后进行粉碎,将干燥粉碎的棕榈树皮10g,用40mL异丙醇与160mL 1.0mol/L NaOH的混合溶液,室温浸泡15h,煮沸20nim,冷却后用去离子水洗涤至中性,抽滤,55℃烘干,得到预处理棕榈树皮; (1) Palm bark pretreatment: Cut the palm bark into small pieces, wash with water to remove soil and impurities, soak in water for 24 hours in a container, and then crush it after vacuum drying. Mix 10g of dried and crushed palm bark with 40mL A mixed solution of isopropanol and 160mL 1.0mol/L NaOH, soaked at room temperature for 15h, boiled for 20nm, washed with deionized water until neutral after cooling, filtered with suction, and dried at 55°C to obtain pretreated palm bark;
(2)环氧基棕榈树皮制备:将上述预处理棕榈树皮10g,用20mL环氧氯丙烷与100mL3.0mol/L NaOH的混合溶液,室温浸泡12 h,再煮沸15min,冷却后用去离子水洗涤至中性,再乙醇洗涤,抽滤后在55℃下烘干,得到环氧基棕榈树皮; (2) Preparation of epoxy-based palm bark: 10g of the above-mentioned pretreated palm bark was soaked in a mixed solution of 20mL epichlorohydrin and 100mL3.0mol/L NaOH at room temperature for 12 hours, then boiled for 15min, and used after cooling. Wash with deionized water until neutral, then wash with ethanol, and dry at 55°C after suction filtration to obtain epoxy-based palm bark;
(3)半胱氨酸改性棕榈树皮制备:在反应器中,分别加入,半胱氨酸:4g,环氧基棕榈树皮:10g,碳酸钠:5g;水:81mL,各组分之和为百分之百,于50±3℃恒温、搅拌、回流反应5 h,冷却后,用去离子水洗涤、抽滤,至滤液呈中性为止,用少量乙醇洗涤后,放在40±5℃真空干燥箱中干燥,得到半胱氨酸改性棕榈树皮。 (3) Preparation of cysteine-modified palm bark: In the reactor, add cysteine: 4g, epoxy-based palm bark: 10g, sodium carbonate: 5g; water: 81mL, each component The sum is 100%, react at a constant temperature of 50±3°C, stir, and reflux for 5 hours. After cooling, wash with deionized water and filter with suction until the filtrate is neutral. After washing with a small amount of ethanol, place it at 40±5°C Dry in a vacuum oven to obtain the cysteine-modified palm bark.
实施例2 Example 2
(1)棕榈树皮预处理:将棕榈树皮剪成小块,用水洗涤去除泥土和杂质,放入容器中用水浸泡40h,真空干燥后进行粉碎,将干燥粉碎的棕榈树皮20g,用50mL异丙醇与300mL 2.0mol/L NaOH的混合溶液,室温浸泡12h,煮沸30nim,冷却后用去离子水洗涤至中性,抽滤,50℃烘干,得到预处理棕榈树皮; (1) Palm bark pretreatment: Cut the palm bark into small pieces, wash with water to remove soil and impurities, soak in water for 40 hours in a container, dry in a vacuum and then crush it. Take 20g of the dried and crushed palm bark in 50mL A mixed solution of isopropanol and 300mL 2.0mol/L NaOH, soaked at room temperature for 12h, boiled for 30nm, washed with deionized water until neutral after cooling, filtered with suction, and dried at 50°C to obtain pretreated palm bark;
(2)环氧基棕榈树皮制备:将上述预处理棕榈树皮20g,用30mL环氧氯丙烷与180mL2.0mol/L NaOH的混合溶液,室温浸泡20 h,再煮沸10min,冷却后用去离子水洗涤至中性,再乙醇洗涤,抽滤后在60℃下烘干,得到环氧基棕榈树皮; (2) Preparation of epoxy-based palm bark: 20g of the above-mentioned pretreated palm bark was soaked in a mixed solution of 30mL epichlorohydrin and 180mL2.0mol/L NaOH at room temperature for 20 hours, then boiled for 10min, and then used after cooling. Wash with deionized water until neutral, then wash with ethanol, and dry at 60°C after suction filtration to obtain epoxy palm bark;
(3)半胱氨酸改性棕榈树皮制备:在反应器中,分别加入,半胱氨酸:4g,环氧基棕榈树皮:10g,碳酸钠:5g;水:81mL,各组分之和为百分之百,于50±3℃恒温、搅拌、回流反应6h,冷却后,用去离子水洗涤、抽滤,至滤液呈中性为止,用少量乙醇洗涤后,放在40±5℃真空干燥箱中干燥,得到半胱氨酸改性棕榈树皮。 (3) Preparation of cysteine-modified palm bark: In the reactor, add cysteine: 4g, epoxy-based palm bark: 10g, sodium carbonate: 5g; water: 81mL, each component The sum is 100%. React at a constant temperature of 50±3°C, stir, and reflux for 6 hours. After cooling, wash with deionized water and filter with suction until the filtrate is neutral. After washing with a small amount of ethanol, place it in a vacuum at 40±5°C. drying in a drying oven to obtain cysteine-modified palm bark.
实施例3 Example 3
(1)棕榈树皮预处理:将棕榈树皮剪成小块,用水洗涤去除泥土和杂质,放入容器中用水浸泡32h,真空干燥后进行粉碎,将干燥粉碎的棕榈树皮30g,用50mL异丙醇与250mL 3.0mol/L NaOH的混合溶液,室温浸泡20h,煮沸10nim,冷却后用去离子水洗涤至中性,抽滤,60℃烘干,得到预处理棕榈树皮; (1) Palm bark pretreatment: Cut the palm bark into small pieces, wash with water to remove soil and impurities, soak in water for 32 hours in a container, dry in a vacuum and then crush it. Take 30g of the dried and crushed palm bark in 50mL A mixed solution of isopropanol and 250mL 3.0mol/L NaOH, soaked at room temperature for 20h, boiled for 10nm, washed with deionized water until neutral after cooling, filtered with suction, and dried at 60°C to obtain pretreated palm bark;
(2)环氧基棕榈树皮制备:将上述预处理棕榈树皮20g,用50mL环氧氯丙烷与150mL3.5mol/L NaOH的混合溶液,室温浸泡15 h,再煮沸20min,冷却后用去离子水洗涤至中性,再乙醇洗涤,抽滤后在55℃下烘干,得到环氧基棕榈树皮; (2) Preparation of epoxy-based palm bark: 20g of the above-mentioned pretreated palm bark was soaked in a mixed solution of 50mL epichlorohydrin and 150mL3.5mol/L NaOH at room temperature for 15 hours, then boiled for 20min, and used after cooling. Wash with deionized water until neutral, then wash with ethanol, and dry at 55°C after suction filtration to obtain epoxy-based palm bark;
(3)半胱氨酸改性棕榈树皮制备:在反应器中,分别加入,半胱氨酸:6g,环氧基棕榈树皮:12g,碳酸钠:6.5g;水:31mL,各组分之和为百分之百,于50±3℃恒温、搅拌、回流反应8 h,冷却后,用去离子水洗涤、抽滤,至滤液呈中性为止,用少量乙醇洗涤后,放在40±5℃真空干燥箱中干燥,得到半胱氨酸改性棕榈树皮。 (3) Preparation of cysteine-modified palm bark: In the reactor, add cysteine: 6g, epoxy-based palm bark: 12g, sodium carbonate: 6.5g; water: 31mL, each group The sum of the fractions is 100%, react at a constant temperature of 50±3°C, stir, and reflux for 8 hours. After cooling, wash with deionized water and filter with suction until the filtrate is neutral. After washing with a small amount of ethanol, place it at 40±5 °C in a vacuum drying oven to obtain cysteine-modified palm bark.
实施例4 Example 4
(1)棕榈树皮预处理:将棕榈树皮剪成小块,用水洗涤去除泥土和杂质,放入容器中用水浸泡24h,真空干燥后进行粉碎,将干燥粉碎的棕榈树皮10g,用40mL异丙醇与160mL 1.0mol/L NaOH的混合溶液,室温浸泡15h,煮沸20nim,冷却后用去离子水洗涤至中性,抽滤,55℃烘干,得到预处理棕榈树皮; (1) Palm bark pretreatment: Cut the palm bark into small pieces, wash with water to remove soil and impurities, soak in water for 24 hours in a container, and then crush it after vacuum drying. Mix 10g of dried and crushed palm bark with 40mL A mixed solution of isopropanol and 160mL 1.0mol/L NaOH, soaked at room temperature for 15h, boiled for 20nm, washed with deionized water until neutral after cooling, filtered with suction, and dried at 55°C to obtain pretreated palm bark;
(2)环氧基棕榈树皮制备:将上述预处理棕榈树皮10g,用20mL环氧氯丙烷与100mL3.0mol/L NaOH的混合溶液,室温浸泡12 h,再煮沸15min,冷却后用去离子水洗涤至中性,再乙醇洗涤,抽滤后在55℃下烘干,得到环氧基棕榈树皮; (2) Preparation of epoxy-based palm bark: 10g of the above-mentioned pretreated palm bark was soaked in a mixed solution of 20mL epichlorohydrin and 100mL3.0mol/L NaOH at room temperature for 12 hours, then boiled for 15min, and used after cooling. Wash with deionized water until neutral, then wash with ethanol, and dry at 55°C after suction filtration to obtain epoxy-based palm bark;
(3)半胱氨酸改性棕榈树皮制备:在反应器中,分别加入,半胱氨酸:4g,环氧基棕榈树皮:6g,碳酸钠:5g;水:35mL,各组分之和为百分之百,于50±3℃恒温、搅拌、回流反应5 h,冷却后,用去离子水洗涤、抽滤,至滤液呈中性为止,用少量乙醇洗涤后,放在40±5℃真空干燥箱中干燥,得到半胱氨酸改性棕榈树皮。 (3) Preparation of cysteine-modified palm bark: In the reactor, add cysteine: 4g, epoxy-based palm bark: 6g, sodium carbonate: 5g; water: 35mL, each component The sum is 100%, react at a constant temperature of 50±3°C, stir, and reflux for 5 hours. After cooling, wash with deionized water and filter with suction until the filtrate is neutral. After washing with a small amount of ethanol, place it at 40±5°C Dry in a vacuum oven to obtain the cysteine-modified palm bark.
实施例5 Example 5
(1)棕榈树皮预处理:将棕榈树皮剪成小块,用水洗涤去除泥土和杂质,放入容器中用水浸泡40h,真空干燥后进行粉碎,将干燥粉碎的棕榈树皮20g,用50mL异丙醇与300mL 2.0mol/L NaOH的混合溶液,室温浸泡12h,煮沸30nim,冷却后用去离子水洗涤至中性,抽滤,50℃烘干,得到预处理棕榈树皮; (1) Palm bark pretreatment: Cut the palm bark into small pieces, wash with water to remove soil and impurities, soak in water for 40 hours in a container, dry in a vacuum and then crush it. Take 20g of the dried and crushed palm bark in 50mL A mixed solution of isopropanol and 300mL 2.0mol/L NaOH, soaked at room temperature for 12h, boiled for 30nm, washed with deionized water until neutral after cooling, filtered with suction, and dried at 50°C to obtain pretreated palm bark;
(2)环氧基棕榈树皮制备:将上述预处理棕榈树皮20g,用30mL环氧氯丙烷与180mL2.0mol/L NaOH的混合溶液,室温浸泡20 h,再煮沸10min,冷却后用去离子水洗涤至中性,再乙醇洗涤,抽滤后在60℃下烘干,得到环氧基棕榈树皮; (2) Preparation of epoxy-based palm bark: 20g of the above-mentioned pretreated palm bark was soaked in a mixed solution of 30mL epichlorohydrin and 180mL2.0mol/L NaOH at room temperature for 20 hours, then boiled for 10min, and then used after cooling. Wash with deionized water until neutral, then wash with ethanol, and dry at 60°C after suction filtration to obtain epoxy palm bark;
(3)半胱氨酸改性棕榈树皮制备:在反应器中,分别加入,半胱氨酸:5g,环氧基棕榈树皮:10g,碳酸钠:5g;水:30mL,各组分之和为百分之百,于50±3℃恒温、搅拌、回流反应6h,冷却后,用去离子水洗涤、抽滤,至滤液呈中性为止,用少量乙醇洗涤后,放在40±5℃真空干燥箱中干燥,得到半胱氨酸改性棕榈树皮。 (3) Preparation of cysteine-modified palm bark: In the reactor, add cysteine: 5g, epoxy-based palm bark: 10g, sodium carbonate: 5g; water: 30mL, each component The sum is 100%. React at a constant temperature of 50±3°C, stir, and reflux for 6 hours. After cooling, wash with deionized water and filter with suction until the filtrate is neutral. After washing with a small amount of ethanol, place it in a vacuum at 40±5°C. drying in a drying oven to obtain cysteine-modified palm bark.
实施例6 Example 6
(1)棕榈树皮预处理:将棕榈树皮剪成小块,用水洗涤去除泥土和杂质,放入容器中用水浸泡32h,真空干燥后进行粉碎,将干燥粉碎的棕榈树皮30g,用50mL异丙醇与250mL 3.0mol/L NaOH的混合溶液,室温浸泡20h,煮沸10nim,冷却后用去离子水洗涤至中性,抽滤,60℃烘干,得到预处理棕榈树皮; (1) Palm bark pretreatment: Cut the palm bark into small pieces, wash with water to remove soil and impurities, soak in water for 32 hours in a container, dry in a vacuum and then crush it. Take 30g of the dried and crushed palm bark in 50mL A mixed solution of isopropanol and 250mL 3.0mol/L NaOH, soaked at room temperature for 20h, boiled for 10nm, washed with deionized water until neutral after cooling, filtered with suction, and dried at 60°C to obtain pretreated palm bark;
(2)环氧基棕榈树皮制备:将上述预处理棕榈树皮20g,用50mL环氧氯丙烷与150mL3.5mol/L NaOH的混合溶液,室温浸泡15 h,再煮沸20min,冷却后用去离子水洗涤至中性,再乙醇洗涤,抽滤后在55℃下烘干,得到环氧基棕榈树皮; (2) Preparation of epoxy-based palm bark: 20g of the above-mentioned pretreated palm bark was soaked in a mixed solution of 50mL epichlorohydrin and 150mL3.5mol/L NaOH at room temperature for 15 hours, then boiled for 20min, and used after cooling. Wash with deionized water until neutral, then wash with ethanol, and dry at 55°C after suction filtration to obtain epoxy-based palm bark;
(3)半胱氨酸改性棕榈树皮制备:在反应器中,分别加入,半胱氨酸:3g,环氧基棕榈树皮:18g,碳酸钠:4g;水:75mL,各组分之和为百分之百,于50±3℃恒温、搅拌、回流反应7h,冷却后,用去离子水洗涤、抽滤,至滤液呈中性为止,用少量乙醇洗涤后,放在40±5℃真空干燥箱中干燥,得到半胱氨酸改性棕榈树皮。 (3) Preparation of cysteine-modified palm bark: In the reactor, add cysteine: 3g, epoxy-based palm bark: 18g, sodium carbonate: 4g; water: 75mL, each component The sum is 100%, react at a constant temperature of 50±3°C, stir, and reflux for 7 hours. After cooling, wash with deionized water and filter with suction until the filtrate is neutral. After washing with a small amount of ethanol, place it in a vacuum at 40±5°C. drying in a drying oven to obtain cysteine-modified palm bark.
实施例7 Example 7
以上实施例制备的半胱氨酸改性棕榈树皮,采用化学法检测其巯基含量相同。 The cysteine-modified palm bark prepared in the above examples has the same sulfhydryl content as detected by chemical methods.
半胱氨酸改性棕榈树皮应用方法:将制备好的半胱氨酸改性棕榈树皮用去离子水浸泡2 h,按一种是静态吸附法,另一种是动态吸附法,对金属离子吸附进行应用。 Application method of cysteine-modified palm bark: Soak the prepared cysteine-modified palm bark in deionized water for 2 h, one is static adsorption method, the other is dynamic adsorption method, for Metal ion adsorption for application.
用静态吸附法测定吸附性能,取不同浓度的金属离子溶液20mL,在相同条件下加入等量的半胱氨酸改性棕榈树皮,震荡吸附0.5 h取清液,用原子吸收测定清液中金属离子的浓度,根据吸附前后金属离子溶液浓度变化计算出吸附率。 The adsorption performance was measured by static adsorption method. 20 mL of metal ion solutions with different concentrations were taken, and an equal amount of cysteine-modified palm bark was added under the same conditions. The concentration of metal ions is calculated according to the concentration change of metal ion solution before and after adsorption.
用动态法测定吸附性能,将一定量的半胱氨酸改性棕榈树皮以湿法装入吸附柱,取不同浓度的金属离子溶液,用稀酸和稀碱调节pH值,以2 mL/min的流速通过吸附柱,用原子吸收测定过滤液和柱上吸附的金属离子量,由此计算吸附率。 The adsorption performance was determined by a dynamic method. A certain amount of cysteine-modified palm bark was loaded into the adsorption column by a wet method, and metal ion solutions with different concentrations were taken, and the pH value was adjusted with dilute acid and dilute alkali. The flow rate of min passes through the adsorption column, and the amount of metal ions adsorbed on the filtrate and the column is measured by atomic absorption, thereby calculating the adsorption rate.
按上述方法制备半胱氨酸改性棕榈树皮在金属离子吸附中的应用。本发明的半胱氨酸改性棕榈树皮在金属离子吸附领域的应用为直接对水体中各种金属离子的吸附和洗脱。其方法是: The application of cysteine-modified palm bark in the adsorption of metal ions prepared by the above method. The application of the cysteine-modified palm bark of the present invention in the field of metal ion adsorption is to directly adsorb and elute various metal ions in water bodies. The method is:
(1)对于含有K+、Na+、Ca2+、Mg2+、Ba2+、Al3+、Cu2+、Zn2+、Cd2+、Fe3+、Ag+、Co2+、Ni2+、Pb2+、Se4+、Pt4+、Pd2+、Au3+ 中的一种或几种的待处理水体系,采用半胱氨酸改性棕榈树皮用静态吸附的方法进行水处理,即取半胱氨酸改性棕榈树皮浸没于待处理水体系中, 震荡吸附0.5 h,其吸附规律如下: (1) For those containing K + , Na + , Ca 2+ , Mg 2+ , Ba 2+ , Al 3+ , Cu 2+ , Zn 2+ , Cd 2+ , Fe 3+ , Ag + , Co 2+ , One or more of Ni 2+ , Pb 2+ , Se 4+ , Pt 4+ , Pd 2+ , Au 3+ in the water system to be treated, using cysteine modified palm bark with static adsorption Methods Water treatment was carried out, that is, palm bark modified by cysteine was immersed in the water system to be treated, and oscillated and adsorbed for 0.5 h. The adsorption rules were as follows:
a.对于碱金属和碱土金属如有K+、Na+、Ca2+、Mg2+、Ba2+、Al3+等不吸附,所以说试样中存在碱金属和碱土金属时不影响半胱氨酸改性棕榈树皮的吸附性能。 a. For alkali metals and alkaline earth metals such as K + , Na + , Ca 2+ , Mg 2+ , Ba 2+ , Al 3+ , etc., it does not adsorb, so the presence of alkali metals and alkaline earth metals in the sample does not affect cysteine Adsorption properties of acid-modified palm bark.
b.对于贵金属离子有较强的吸附性能,吸附强弱顺序为:Pt4+ > Au3+ > Pd2+ > Ag+。 b. It has strong adsorption performance for noble metal ions, and the order of adsorption strength is: Pt 4+ > Au 3+ > Pd 2+ > Ag + .
c.对重金属离子也有较强的吸附性能,吸附强弱顺序为:Se4+、Ag+ > Cu2+ > Fe3+,Pb2+ > Zn2+> Cd2+ > Co2+、Ni2+。 c. It also has strong adsorption performance for heavy metal ions, and the order of adsorption strength is: Se 4+ , Ag + > Cu 2+ > Fe 3+ , Pb 2+ > Zn 2+ > Cd 2+ > Co 2+ , Ni 2+ .
吸附容量与半胱氨酸改性棕榈树皮中巯基含量用量、吸附温度、溶液体系的 pH值等因素有关。 The adsorption capacity is related to factors such as the content of sulfhydryl groups in cysteine-modified palm bark, the adsorption temperature, and the pH value of the solution system.
(2)对于含有K+、Na+、Ca2+、Mg2+、Ba2+、Al3+、Cu2+、Zn2+、Cd2+、Fe3+、Ag+、Co2+、Ni2+、Pb2+、Se4+、Pt4+、Pd2+、Au3+ 中的一种或几种的待处理水体系,采用半胱氨酸改性棕榈树皮用动态吸附的方法进行水处理,其吸附的规律同上,吸附容量与半胱氨酸改性棕榈树皮中巯基含量用量、吸附温度、溶液体系的 pH值、溶液的流速等因素有关。 (2) For those containing K + , Na + , Ca 2+ , Mg 2+ , Ba 2+ , Al 3+ , Cu 2+ , Zn 2+ , Cd 2+ , Fe 3+ , Ag + , Co 2+ , One or more of Ni 2+ , Pb 2+ , Se 4+ , Pt 4+ , Pd 2+ , Au 3+ in the water system to be treated, using cysteine modified palm bark with dynamic adsorption Methods Water treatment, the adsorption rule is the same as above, and the adsorption capacity is related to factors such as the content of sulfhydryl groups in cysteine-modified palm bark, adsorption temperature, pH value of the solution system, and flow rate of the solution.
获得的半胱氨酸改性棕榈树皮对Cd2+的吸附容量可高达295mg/g,对Pb2+的最大吸附量为533mg/g, 对Cu2+的最大吸附量为179mg/g,Hg2+的最大吸附量为492mg/g,最高吸附率可达99%。 The obtained cysteine-modified palm bark has an adsorption capacity of up to 295 mg/g for Cd 2+ , a maximum adsorption capacity for Pb 2+ of 533 mg/g, and a maximum adsorption capacity for Cu 2+ of 179 mg/g. The maximum adsorption capacity of Hg 2+ is 492mg/g, and the highest adsorption rate can reach 99%.
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