CN107416827A - A kind of preparation method of useless tealeaves peanut based active carbon - Google Patents

A kind of preparation method of useless tealeaves peanut based active carbon Download PDF

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CN107416827A
CN107416827A CN201710365813.4A CN201710365813A CN107416827A CN 107416827 A CN107416827 A CN 107416827A CN 201710365813 A CN201710365813 A CN 201710365813A CN 107416827 A CN107416827 A CN 107416827A
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peanut shell
activated carbon
waste tea
based activated
powder
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房德职
张晓艺
张子龙
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Shandong University of Science and Technology
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Abstract

本发明提供了一种废茶叶‑花生壳基活性炭的制备方法,以废茶叶和花生壳为原料,将其粉碎混合后浸渍到以氢氧化钾、氢氧化钠、磷酸、硫酸或氯化锌为活化剂的溶液中,再经过恒温干燥器烘干、马弗炉煅烧,并将煅烧后的产物进行研磨即得到废茶叶‑花生壳基活性炭。所制得的废茶叶‑花生壳基活性炭的碳含量高、比表面积大,具有高的吸附性,其原料充分利用固体废弃物废茶叶和花生壳,扩大了制备活性炭的原料来源,实现了废弃物的再利用,积极带动循环经济的发展,且其制备工艺简单,操作方便,成本低廉。The invention provides a method for preparing waste tea-peanut shell-based activated carbon, which uses waste tea leaves and peanut shells as raw materials, pulverizes them and then impregnates them into potassium hydroxide, sodium hydroxide, phosphoric acid, sulfuric acid or zinc chloride. The solution of the activator is then dried in a constant temperature dryer, calcined in a muffle furnace, and the calcined product is ground to obtain waste tea-peanut shell-based activated carbon. The prepared waste tea-peanut shell-based activated carbon has high carbon content, large specific surface area, and high adsorption. The recycling of materials actively promotes the development of circular economy, and its preparation process is simple, easy to operate, and low in cost.

Description

一种废茶叶-花生壳基活性炭的制备方法A kind of preparation method of waste tea-peanut shell-based activated carbon

技术领域technical field

本发明属于活性炭技术领域,涉及复合原料型活性炭的制备,具体涉及一种废茶叶-花生壳基活性炭的制备方法。The invention belongs to the technical field of activated carbon, and relates to the preparation of composite raw material activated carbon, in particular to a preparation method of waste tea-peanut shell-based activated carbon.

背景技术Background technique

活性炭因具有较强的吸附性、催化性能和易再生等优点,已成为当下应用最广泛的环境友好型吸附剂。活性炭的制备原料十分广泛,绝大部分含碳物质都可制备活性炭,如植物、动物、废料、城市垃圾等。但是传统的单一原料制备活性炭存在含碳量低、比表面积小等问题,因此,利用复合原料制备活性炭以提高吸附性能,已成为近几年来的研究重点。废弃茶梗、茶末及果壳均为我国重要的农林废弃物,其化学成分主要包括纤维素、半纤维素、木质素等,与一般的木质材料无异,是制备活性炭较好的生物质原料。目前国内已有利用单一原料制备活性炭的相应研究,而利用复合型原料制备活性炭的研究较少。为寻找新的复合原料,改良活性炭相关性能,选取废茶叶和果壳作为研究对象以制备性能较高的活性炭,在扩大制备活性炭的原料来源,提供一种新型有效制备方法的同时,并将此应用于社会生产以实现废弃物的重新利用,对循环经济的发展也起到一定的带动作用。Activated carbon has become the most widely used environmentally friendly adsorbent due to its strong adsorption, catalytic performance and easy regeneration. There are a wide range of raw materials for the preparation of activated carbon, and most of the carbon-containing substances can be used to prepare activated carbon, such as plants, animals, waste materials, municipal garbage, etc. However, the traditional preparation of activated carbon from a single raw material has problems such as low carbon content and small specific surface area. Therefore, the use of composite raw materials to prepare activated carbon to improve adsorption performance has become the focus of research in recent years. Abandoned tea stems, tea powder and fruit shells are important agricultural and forestry wastes in my country. Their chemical components mainly include cellulose, hemicellulose, lignin, etc., which are no different from ordinary woody materials. They are good biomass for preparing activated carbon. raw material. At present, there have been corresponding studies on the preparation of activated carbon by using a single raw material in China, but there are few studies on the preparation of activated carbon by using composite raw materials. In order to find new composite raw materials and improve the performance of activated carbon, waste tea leaves and fruit shells were selected as research objects to prepare activated carbon with high performance. While expanding the source of raw materials for preparing activated carbon and providing a new and effective preparation method, this Applied in social production to realize the reuse of waste, it also plays a certain role in promoting the development of circular economy.

发明内容Contents of the invention

针对利用单一原料制备活性炭的相应研究较多,但利用复合型原料制备活性炭的研究较少的问题,本发明提供了一种以废茶叶和花生壳为原料制备废茶叶-花生壳基活性炭的方法。Aiming at the problem that there are many corresponding studies on the preparation of activated carbon by using a single raw material, but less research on the preparation of activated carbon by using composite raw materials, the present invention provides a method for preparing waste tea-peanut shell-based activated carbon by using waste tea leaves and peanut shells as raw materials .

一种废茶叶-花生壳基活性炭的制备方法,包括以下步骤:A preparation method of waste tea leaves-peanut shell-based activated carbon, comprising the following steps:

(1)将花生壳和废茶叶分别烘干后粉碎,将过80目筛的花生壳粉末和废茶叶粉末进行混合,得到混合原料A;(1) Peanut shells and waste tea leaves are dried and pulverized respectively, and peanut shell powder and waste tea powder passed through an 80-mesh sieve are mixed to obtain mixed raw material A;

(2)以氢氧化钾、氢氧化钠、磷酸、硫酸或氯化锌为活化剂,配置质量浓度为20%~80%的活化剂溶液,取与活化剂溶液的质量比为1:1~1:6的混合原料A浸渍在所述活化剂溶液中,在室温下浸渍1~10小时后,在100℃下于恒温干燥器中烘干30min,然后在300~700℃下于马弗炉中真空煅烧1~6小时,最后将煅烧后的产物在研钵中研磨并过80目筛即得到废茶叶-花生壳基活性炭。(2) With potassium hydroxide, sodium hydroxide, phosphoric acid, sulfuric acid or zinc chloride as the activator, configure the activator solution with a mass concentration of 20% to 80%, and take the mass ratio of the activator solution to be 1:1~ The mixed raw material A of 1:6 is immersed in the activator solution, after soaking at room temperature for 1-10 hours, dry in a constant temperature dryer at 100°C for 30min, and then in a muffle furnace at 300-700°C Calcining in a medium vacuum for 1 to 6 hours, and finally grinding the calcined product in a mortar and passing through an 80-mesh sieve to obtain waste tea-peanut shell-based activated carbon.

优选地,所述花生壳粉末和废茶叶粉末的质量比为1:7~7:1。Preferably, the mass ratio of the peanut shell powder to the waste tea powder is 1:7-7:1.

优选地,所述花生壳粉末和废茶叶粉末的质量比为1:1。Preferably, the mass ratio of the peanut shell powder to the waste tea powder is 1:1.

优选地,所述活化剂溶液为氯化锌溶液。Preferably, the activator solution is a zinc chloride solution.

优选地,所述活化剂溶液的质量浓度为40%。Preferably, the mass concentration of the activator solution is 40%.

优选地,所述混合原料A与活化剂溶液的质量比为1:3。Preferably, the mass ratio of the mixed raw material A to the activator solution is 1:3.

优选地,所述浸渍时间为2小时。Preferably, the soaking time is 2 hours.

优选地,所述煅烧温度为500℃。Preferably, the calcination temperature is 500°C.

优选地,所述煅烧时间为2小时。Preferably, the calcination time is 2 hours.

有益效果:Beneficial effect:

本发明制备得到的废茶叶-花生壳基活性炭的碳含量高、比表面积大,具有高的吸附性,其原料充分利用固体废弃物废茶叶和花生壳,扩大了制备活性炭的原料来源,实现了废弃物的再利用,积极带动循环经济的发展,且其制备工艺简单,操作方便,成本低廉。The waste tea leaves-peanut shell-based activated carbon prepared by the present invention has high carbon content, large specific surface area, and high adsorption property. The raw materials of the waste tea leaves and peanut shells, which are solid wastes, are fully utilized, which expands the source of raw materials for preparing activated carbon and realizes The reuse of waste actively promotes the development of circular economy, and the preparation process is simple, the operation is convenient, and the cost is low.

具体实施方式detailed description

下面结合实施例,对本发明的具体实施方式作进一步详细描述。Below in conjunction with the examples, the specific implementation of the present invention will be further described in detail.

实施例1:Example 1:

将花生壳和废茶叶分别烘干后粉碎,称取过80目筛的花生壳粉末和废茶叶粉末共10.00g(其中花生壳粉末和废茶叶粉末的质量比为1:7);称取10.00g质量浓度为20%的氢氧化钾溶液(混合原料与活化剂溶液的质量比为1:1);将花生壳粉末和废茶叶粉末的混合原料置于氢氧化钾溶液中,在室温下浸渍1小时后,在100℃下于恒温干燥器中烘干30min,然后在300℃下于马弗炉中隔绝空气煅烧1小时,最后将煅烧后的产物在研钵中研磨并过80目筛得到废茶叶-花生壳基活性炭。Peanut shells and waste tea leaves were dried and crushed respectively, and a total of 10.00 g of peanut shell powder and waste tea powder passed through a 80-mesh sieve were weighed (the mass ratio of peanut shell powder and waste tea powder was 1:7); 10.00 g was weighed. g mass concentration is 20% potassium hydroxide solution (the mass ratio of mixed raw material and activator solution is 1:1); the mixed raw material of peanut shell powder and waste tea leaf powder is placed in potassium hydroxide solution, soaked at room temperature After 1 hour, dry in a constant temperature drier at 100°C for 30 minutes, then calcinate in a muffle furnace at 300°C without air for 1 hour, and finally grind the calcined product in a mortar and pass through an 80-mesh sieve to obtain Waste tea leaves - peanut shell based activated carbon.

实施例2:Example 2:

将花生壳和废茶叶分别烘干后粉碎,称取过80目筛的花生壳粉末和废茶叶粉末共10.00g(其中花生壳粉末和废茶叶粉末的质量比为7:1);称取10.00g质量浓度为20%的氢氧化钠溶液(混合原料与活化剂溶液的质量比为1:1);将花生壳粉末和废茶叶粉末的混合原料置于氢氧化钠溶液中,在室温下浸渍1小时后,在100℃下于恒温干燥器中烘干30min,然后在300℃下于马弗炉中隔绝空气煅烧1小时,最后将煅烧后的产物在研钵中研磨并过80目筛得到废茶叶-花生壳基活性炭。Peanut shells and waste tea leaves were dried and crushed respectively, and a total of 10.00 g of peanut shell powder and waste tea powder passed through a 80-mesh sieve were weighed (the mass ratio of peanut shell powder and waste tea powder was 7:1); 10.00 g was weighed. g mass concentration is 20% sodium hydroxide solution (the mass ratio of mixed raw material and activator solution is 1:1); the mixed raw material of peanut shell powder and waste tea powder is placed in sodium hydroxide solution, soaked at room temperature After 1 hour, dry in a constant temperature drier at 100°C for 30 minutes, then calcinate in a muffle furnace at 300°C without air for 1 hour, and finally grind the calcined product in a mortar and pass through an 80-mesh sieve to obtain Waste tea leaves - peanut shell based activated carbon.

实施例3:Example 3:

将花生壳和废茶叶分别烘干后粉碎,称取过80目筛的花生壳粉末和废茶叶粉末共10.00g(其中花生壳粉末和废茶叶粉末的质量比为1:7);称取60.00g质量浓度为80%的磷酸溶液(混合原料与活化剂溶液的质量比为1:6);将花生壳粉末和废茶叶粉末的混合原料置于磷酸溶液中,在室温下浸渍10小时后,在100℃下于恒温干燥器中烘干30min,然后在700℃下于马弗炉中隔绝空气煅烧6小时,最后将煅烧后的产物在研钵中研磨并过80目筛得到废茶叶-花生壳基活性炭。Peanut shells and waste tea leaves were dried and crushed respectively, and a total of 10.00 g of peanut shell powder and waste tea powder passed through an 80-mesh sieve were weighed (the mass ratio of peanut shell powder and waste tea powder was 1:7); 60.00 g mass concentration is 80% phosphoric acid solution (the mass ratio of mixed raw material and activator solution is 1:6); The mixed raw material of peanut shell powder and waste tea leaf powder is placed in phosphoric acid solution, after soaking at room temperature for 10 hours, Dry in a constant temperature drier at 100°C for 30 minutes, then calcinate in a muffle furnace at 700°C for 6 hours without air, and finally grind the calcined product in a mortar and pass through a 80-mesh sieve to obtain waste tea leaves-peanut Shell-based activated carbon.

实施例4:Example 4:

将花生壳和废茶叶分别烘干后粉碎,称取过80目筛的花生壳粉末和废茶叶粉末共10.00g(其中花生壳粉末和废茶叶粉末的质量比为7:1);称取60.00g质量浓度为80%的硫酸溶液(混合原料与活化剂溶液的质量比为1:6);将花生壳粉末和废茶叶粉末的混合原料置于硫酸溶液中,在室温下浸渍10小时后,在100℃下于恒温干燥器中烘干30min,然后在700℃下于马弗炉中隔绝空气煅烧6小时,最后将煅烧后的产物在研钵中研磨并过80目筛得到废茶叶-花生壳基活性炭。Peanut shells and waste tea leaves were dried and crushed respectively, and a total of 10.00 g of peanut shell powder and waste tea powder passed through a 80-mesh sieve were weighed (the mass ratio of peanut shell powder and waste tea powder was 7:1); 60.00 g mass concentration is 80% sulfuric acid solution (the mass ratio of mixed raw material and activator solution is 1:6); The mixed raw material of peanut shell powder and waste tea leaf powder is placed in sulfuric acid solution, after soaking at room temperature for 10 hours, Dry in a constant temperature drier at 100°C for 30 minutes, then calcinate in a muffle furnace at 700°C for 6 hours without air, and finally grind the calcined product in a mortar and pass through a 80-mesh sieve to obtain waste tea leaves-peanut Shell-based activated carbon.

实施例5:Example 5:

将花生壳和废茶叶分别烘干后粉碎,称取过80目筛的花生壳粉末和废茶叶粉末共10.00g(其中花生壳粉末和废茶叶粉末的质量比为1:3);称取50.00g质量浓度为50%的氯化锌溶液(混合原料与活化剂溶液的质量比为1:5);将花生壳粉末和废茶叶粉末的混合原料置于氯化锌溶液中,在室温下浸渍6小时后,在100℃下于恒温干燥器中烘干30min,然后在400℃下于马弗炉中隔绝空气煅烧3小时,最后将煅烧后的产物在研钵中研磨并过80目筛得到废茶叶-花生壳基活性炭。Peanut shells and waste tea leaves were dried and crushed respectively, and a total of 10.00 g of peanut shell powder and waste tea powder passed through a 80-mesh sieve were weighed (the mass ratio of peanut shell powder and waste tea powder was 1:3); 50.00 g mass concentration is 50% zinc chloride solution (mass ratio of mixed raw material and activator solution is 1:5); the mixed raw material of peanut shell powder and waste tea powder is placed in zinc chloride solution, soaked at room temperature After 6 hours, dry in a constant temperature drier at 100°C for 30 minutes, then calcinate in a muffle furnace at 400°C for 3 hours without air, and finally grind the calcined product in a mortar and pass through an 80-mesh sieve to obtain Waste tea leaves - peanut shell based activated carbon.

实施例6:Embodiment 6:

将花生壳和废茶叶分别烘干后粉碎,称取过80目筛的花生壳粉末和废茶叶粉末共10.00g(其中花生壳粉末和废茶叶粉末的质量比为1:1);称取40.00g质量浓度为20%的氯化锌溶液(混合原料与活化剂溶液的质量比为1:4);将花生壳粉末和废茶叶粉末的混合原料置于氯化锌溶液中,在室温下浸渍6小时后,在100℃下于恒温干燥器中烘干30min,然后在500℃下于马弗炉中隔绝空气煅烧2小时,最后将煅烧后的产物在研钵中研磨并过80目筛得到废茶叶-花生壳基活性炭。Peanut shells and waste tea leaves were dried and pulverized respectively, and a total of 10.00 g of peanut shell powder and waste tea powder passed through an 80-mesh sieve were weighed (the mass ratio of peanut shell powder and waste tea powder was 1:1); 40.00 g mass concentration is 20% zinc chloride solution (mass ratio of mixed raw material and activator solution is 1:4); the mixed raw material of peanut shell powder and waste tea powder is placed in zinc chloride solution, soaked at room temperature After 6 hours, dry in a constant temperature dryer at 100°C for 30 minutes, then calcinate in a muffle furnace at 500°C for 2 hours without air, and finally grind the calcined product in a mortar and pass through an 80-mesh sieve to obtain Waste tea leaves - peanut shell based activated carbon.

称取所制得的废茶叶-花生壳基活性炭0.100g加入到50ml亚甲基蓝溶液(20mg/l)中进行吸附去除,室温条件下以恒定频率在振荡器中震荡20min后,取出静置15min,取上层清液,用可见光分光光度计测其吸光度,计算去除率为70.48%。Take by weighing 0.100 g of the waste tea leaves-peanut shell-based activated carbon and add it to 50 ml of methylene blue solution (20 mg/l) for adsorption and removal. After shaking in an oscillator at a constant frequency for 20 min at room temperature, take it out and let it stand for 15 min. The absorbance of the supernatant was measured with a visible light spectrophotometer, and the calculated removal rate was 70.48%.

实施例7:Embodiment 7:

将花生壳和废茶叶分别烘干后粉碎,称取过80目筛的花生壳粉末和废茶叶粉末共10.00g(其中花生壳粉末和废茶叶粉末的质量比为1:1);称取40.00g质量浓度为40%的氯化锌溶液(混合原料与活化剂溶液的质量比为1:4);将花生壳粉末和废茶叶粉末的混合原料置于氯化锌溶液中,在室温下浸渍6小时后,在100℃下于恒温干燥器中烘干30min,然后在500℃下于马弗炉中隔绝空气煅烧2小时,最后将煅烧后的产物在研钵中研磨并过80目筛得到废茶叶-花生壳基活性炭。Peanut shells and waste tea leaves were dried and pulverized respectively, and a total of 10.00 g of peanut shell powder and waste tea powder passed through an 80-mesh sieve were weighed (the mass ratio of peanut shell powder and waste tea powder was 1:1); 40.00 g mass concentration is 40% zinc chloride solution (mass ratio of mixed raw material and activator solution is 1:4); the mixed raw material of peanut shell powder and waste tea powder is placed in zinc chloride solution, soaked at room temperature After 6 hours, dry in a constant temperature dryer at 100°C for 30 minutes, then calcinate in a muffle furnace at 500°C for 2 hours without air, and finally grind the calcined product in a mortar and pass through an 80-mesh sieve to obtain Waste tea leaves - peanut shell based activated carbon.

称取所制得的废茶叶-花生壳基活性炭0.100g加入到50ml亚甲基蓝溶液(20mg/l)中进行吸附去除,室温条件下以恒定频率在振荡器中震荡20min后,取出静置15min,取上层清液,用可见光分光光度计测其吸光度,计算去除率为96.35%。Take by weighing 0.100 g of the waste tea leaves-peanut shell-based activated carbon and add it to 50 ml of methylene blue solution (20 mg/l) for adsorption and removal. After shaking in an oscillator at a constant frequency for 20 min at room temperature, take it out and let it stand for 15 min. The absorbance of the supernatant was measured with a visible light spectrophotometer, and the calculated removal rate was 96.35%.

实施例8:Embodiment 8:

将花生壳和废茶叶分别烘干后粉碎,称取过80目筛的花生壳粉末和废茶叶粉末共10.00g(其中花生壳粉末和废茶叶粉末的质量比为1:1);称取30.00g质量浓度为40%的氯化锌溶液(混合原料与活化剂溶液的质量比为1:3);将花生壳粉末和废茶叶粉末的混合原料置于氯化锌溶液中,在室温下浸渍6小时后,在100℃下于恒温干燥器中烘干30min,然后在500℃下于马弗炉中隔绝空气煅烧2小时,最后将煅烧后的产物在研钵中研磨并过80目筛得到废茶叶-花生壳基活性炭。Peanut shells and waste tea leaves were dried and crushed respectively, and a total of 10.00 g of peanut shell powder and waste tea powder passed through a 80-mesh sieve were weighed (the mass ratio of peanut shell powder and waste tea powder was 1:1); 30.00 g mass concentration is 40% zinc chloride solution (mass ratio of mixed raw material and activator solution is 1:3); the mixed raw material of peanut shell powder and waste tea powder is placed in zinc chloride solution, soaked at room temperature After 6 hours, dry in a constant temperature dryer at 100°C for 30 minutes, then calcinate in a muffle furnace at 500°C for 2 hours without air, and finally grind the calcined product in a mortar and pass through an 80-mesh sieve to obtain Waste tea leaves - peanut shell based activated carbon.

称取所制得的废茶叶-花生壳基活性炭0.100g加入到50ml亚甲基蓝溶液(20mg/l)中进行吸附去除,室温条件下以恒定频率在振荡器中震荡20min后,取出静置15min,取上层清液,用可见光分光光度计测其吸光度,计算去除率为97.94%。Take by weighing 0.100 g of the waste tea leaves-peanut shell-based activated carbon and add it to 50 ml of methylene blue solution (20 mg/l) for adsorption and removal. After shaking in an oscillator at a constant frequency for 20 min at room temperature, take it out and let it stand for 15 min. The absorbance of the supernatant was measured with a visible light spectrophotometer, and the calculated removal rate was 97.94%.

实施例9:Embodiment 9:

将花生壳和废茶叶分别烘干后粉碎,称取过80目筛的花生壳粉末和废茶叶粉末共10.00g(其中花生壳粉末和废茶叶粉末的质量比为1:1);称取30.00g质量浓度为40%的氯化锌溶液(混合原料与活化剂溶液的质量比为1:3);将花生壳粉末和废茶叶粉末的混合原料置于氯化锌溶液中,在室温下浸渍6小时后,在100℃下于恒温干燥器中烘干30min,然后在400℃下于马弗炉中隔绝空气煅烧2小时,最后将煅烧后的产物在研钵中研磨并过80目筛得到废茶叶-花生壳基活性炭。Peanut shells and waste tea leaves were dried and crushed respectively, and a total of 10.00 g of peanut shell powder and waste tea powder passed through a 80-mesh sieve were weighed (the mass ratio of peanut shell powder and waste tea powder was 1:1); 30.00 g mass concentration is 40% zinc chloride solution (mass ratio of mixed raw material and activator solution is 1:3); the mixed raw material of peanut shell powder and waste tea powder is placed in zinc chloride solution, soaked at room temperature After 6 hours, dry in a constant temperature dryer at 100°C for 30 minutes, then calcinate in a muffle furnace at 400°C for 2 hours without air, and finally grind the calcined product in a mortar and pass through an 80-mesh sieve to obtain Waste tea leaves - peanut shell based activated carbon.

称取所制得的废茶叶-花生壳基活性炭0.100g加入到50ml亚甲基蓝溶液(20mg/l)中进行吸附去除,室温条件下以恒定频率在振荡器中震荡20min后,取出静置15min,取上层清液,用可见光分光光度计测其吸光度,计算去除率为98.79%。Take by weighing 0.100 g of the waste tea leaves-peanut shell-based activated carbon and add it to 50 ml of methylene blue solution (20 mg/l) for adsorption and removal. After shaking in an oscillator at a constant frequency for 20 min at room temperature, take it out and let it stand for 15 min. The absorbance of the supernatant was measured with a visible light spectrophotometer, and the calculated removal rate was 98.79%.

实施例10:Example 10:

将花生壳和废茶叶分别烘干后粉碎,称取过80目筛的花生壳粉末和废茶叶粉末共10.00g(其中花生壳粉末和废茶叶粉末的质量比为1:1);称取30.00g质量浓度为40%的氯化锌溶液(混合原料与活化剂溶液的质量比为1:3);将花生壳粉末和废茶叶粉末的混合原料置于氯化锌溶液中,在室温下浸渍2小时后,在100℃下于恒温干燥器中烘干30min,然后在500℃下于马弗炉中隔绝空气煅烧2小时,最后将煅烧后的产物在研钵中研磨并过80目筛得到废茶叶-花生壳基活性炭。Peanut shells and waste tea leaves were dried and crushed respectively, and a total of 10.00 g of peanut shell powder and waste tea powder passed through a 80-mesh sieve were weighed (the mass ratio of peanut shell powder and waste tea powder was 1:1); 30.00 g mass concentration is 40% zinc chloride solution (mass ratio of mixed raw material and activator solution is 1:3); the mixed raw material of peanut shell powder and waste tea powder is placed in zinc chloride solution, soaked at room temperature After 2 hours, dry in a constant temperature dryer at 100°C for 30 minutes, then calcinate in a muffle furnace at 500°C for 2 hours without air, and finally grind the calcined product in a mortar and pass through an 80-mesh sieve to obtain Waste tea leaves - peanut shell based activated carbon.

称取所制得的废茶叶-花生壳基活性炭0.100g加入到50ml亚甲基蓝溶液(20mg/l)中进行吸附去除,室温条件下以恒定频率在振荡器中震荡20min后,取出静置15min,取上层清液,用可见光分光光度计测其吸光度,计算去除率为99.08%。Take by weighing 0.100 g of the waste tea leaves-peanut shell-based activated carbon and add it to 50 ml of methylene blue solution (20 mg/l) for adsorption and removal. After shaking in an oscillator at a constant frequency for 20 min at room temperature, take it out and let it stand for 15 min. The absorbance of the supernatant was measured with a visible light spectrophotometer, and the calculated removal rate was 99.08%.

实施例11:Example 11:

将花生壳和废茶叶分别烘干后粉碎,称取过80目筛的花生壳粉末和废茶叶粉末共10.00g(其中花生壳粉末和废茶叶粉末的质量比为1:1);称取30.00g质量浓度为40%的氯化锌溶液(混合原料与活化剂溶液的质量比为1:3);将花生壳粉末和废茶叶粉末的混合原料置于氯化锌溶液中,在室温下浸渍2小时后,在100℃下于恒温干燥器中烘干30min,然后在500℃下于马弗炉中隔绝空气煅烧3小时,最后将煅烧后的产物在研钵中研磨并过80目筛得到废茶叶-花生壳基活性炭。Peanut shells and waste tea leaves were dried and crushed respectively, and a total of 10.00 g of peanut shell powder and waste tea powder passed through a 80-mesh sieve were weighed (the mass ratio of peanut shell powder and waste tea powder was 1:1); 30.00 g mass concentration is 40% zinc chloride solution (mass ratio of mixed raw material and activator solution is 1:3); the mixed raw material of peanut shell powder and waste tea powder is placed in zinc chloride solution, soaked at room temperature After 2 hours, dry in a constant temperature drier at 100°C for 30 minutes, then calcinate in a muffle furnace at 500°C for 3 hours without air, and finally grind the calcined product in a mortar and pass through an 80-mesh sieve to obtain Waste tea leaves - peanut shell based activated carbon.

称取所制得的废茶叶-花生壳基活性炭0.100g加入到50ml亚甲基蓝溶液(20mg/l)中进行吸附去除,室温条件下以恒定频率在振荡器中震荡20min后,取出静置15min,取上层清液,用可见光分光光度计测其吸光度,计算去除率为98.11%。Take by weighing 0.100 g of the waste tea leaves-peanut shell-based activated carbon and add it to 50 ml of methylene blue solution (20 mg/l) for adsorption and removal. After shaking in an oscillator at a constant frequency for 20 min at room temperature, take it out and let it stand for 15 min. The absorbance of the supernatant was measured with a visible light spectrophotometer, and the calculated removal rate was 98.11%.

实施例12:Example 12:

将花生壳和废茶叶分别烘干后粉碎,称取过80目筛的花生壳粉末和废茶叶粉末共10.00g(其中花生壳粉末和废茶叶粉末的质量比为7:1);称取30.00g质量浓度为40%的氯化锌溶液(混合原料与活化剂溶液的质量比为1:3);将花生壳粉末和废茶叶粉末的混合原料置于氯化锌溶液中,在室温下浸渍2小时后,在100℃下于恒温干燥器中烘干30min,然后在500℃下于马弗炉中隔绝空气煅烧2小时,最后将煅烧后的产物在研钵中研磨并过80目筛得到废茶叶-花生壳基活性炭。Peanut shells and waste tea leaves were dried and crushed respectively, and a total of 10.00 g of peanut shell powder and waste tea powder passed through a 80-mesh sieve were weighed (the mass ratio of peanut shell powder and waste tea powder was 7:1); 30.00 g mass concentration is 40% zinc chloride solution (mass ratio of mixed raw material and activator solution is 1:3); the mixed raw material of peanut shell powder and waste tea powder is placed in zinc chloride solution, soaked at room temperature After 2 hours, dry in a constant temperature dryer at 100°C for 30 minutes, then calcinate in a muffle furnace at 500°C for 2 hours without air, and finally grind the calcined product in a mortar and pass through an 80-mesh sieve to obtain Waste tea leaves - peanut shell based activated carbon.

称取所制得的废茶叶-花生壳基活性炭0.100g加入到50ml亚甲基蓝溶液(20mg/l)中进行吸附去除,室温条件下以恒定频率在振荡器中震荡20min后,取出静置15min,取上层清液,用可见光分光光度计测其吸光度,计算去除率为98.80%。Take by weighing 0.100 g of the waste tea leaves-peanut shell-based activated carbon and add it to 50 ml of methylene blue solution (20 mg/l) for adsorption and removal. After shaking in an oscillator at a constant frequency for 20 min at room temperature, take it out and let it stand for 15 min. The absorbance of the supernatant was measured with a visible light spectrophotometer, and the calculated removal rate was 98.80%.

当然,上述说明并非是对本发明的限制,本发明也并不仅限于上述举例,本技术领域的技术人员在本发明的实质范围内所做出的变化、改型、添加或替换,也应属于本发明的保护范围。Of course, the above descriptions are not intended to limit the present invention, and the present invention is not limited to the above examples. Changes, modifications, additions or replacements made by those skilled in the art within the scope of the present invention shall also belong to the present invention. protection scope of the invention.

Claims (9)

1.一种废茶叶-花生壳基活性炭的制备方法,其特征在于,包括以下步骤:1. a preparation method of waste tea leaves-peanut shell-based activated carbon, is characterized in that, comprises the following steps: (1)将花生壳和废茶叶分别烘干后粉碎,将过80目筛的花生壳粉末和废茶叶粉末进行混合,得到混合原料A;(1) Peanut shells and waste tea leaves are dried and pulverized respectively, and peanut shell powder and waste tea powder passed through an 80-mesh sieve are mixed to obtain mixed raw material A; (2)以氢氧化钾、氢氧化钠、磷酸、硫酸或氯化锌为活化剂,配置质量浓度为20%~80%的活化剂溶液;取与活化剂溶液的质量比为1:1~1:6的混合原料A浸渍在所述活化剂溶液中,在室温下浸渍1~10小时后,在100℃下于恒温干燥器中烘干30min,然后在300~700℃下于马弗炉中真空煅烧1~6小时,最后将煅烧后的产物在研钵中研磨并过80目筛即得到废茶叶-花生壳基活性炭。(2) With potassium hydroxide, sodium hydroxide, phosphoric acid, sulfuric acid or zinc chloride as the activator, configure the activator solution with a mass concentration of 20% to 80%; the mass ratio to the activator solution is 1:1~ The mixed raw material A of 1:6 is immersed in the activator solution, after soaking at room temperature for 1-10 hours, dry in a constant temperature dryer at 100°C for 30min, and then in a muffle furnace at 300-700°C Calcining in a medium vacuum for 1 to 6 hours, and finally grinding the calcined product in a mortar and passing through an 80-mesh sieve to obtain waste tea-peanut shell-based activated carbon. 2.根据权利要求1所述的一种废茶叶-花生壳基活性炭的制备方法,其特征在于,所述花生壳粉末和废茶叶粉末的质量比为1:7~7:1。2. A method for preparing waste tea-peanut shell-based activated carbon according to claim 1, wherein the mass ratio of the peanut shell powder and waste tea powder is 1:7 to 7:1. 3.根据权利要求2所述的一种废茶叶-花生壳基活性炭的制备方法,其特征在于,所述花生壳粉末和废茶叶粉末的质量比为1:1。3. the preparation method of a kind of waste tealeaves-peanut shell-based activated carbon according to claim 2, is characterized in that, the mass ratio of described peanut shell powder and waste tealeaves powder is 1:1. 4.根据权利要求1所述的一种废茶叶-花生壳基活性炭的制备方法,其特征在于,所述活化剂溶液为氯化锌溶液。4. the preparation method of a kind of waste tea leaves-peanut shell base activated carbon according to claim 1, is characterized in that, described activator solution is zinc chloride solution. 5.根据权利要求1或4所述的一种废茶叶-花生壳基活性炭的制备方法,其特征在于,所述活化剂溶液的质量浓度为40%。5. A method for preparing waste tea leaves-peanut shell-based activated carbon according to claim 1 or 4, characterized in that the mass concentration of the activator solution is 40%. 6.根据权利要求1或4所述的一种废茶叶-花生壳基活性炭的制备方法,其特征在于,所述混合原料A与活化剂溶液的质量比为1:3。6. A method for preparing waste tea leaves-peanut shell-based activated carbon according to claim 1 or 4, wherein the mass ratio of the mixed raw material A to the activator solution is 1:3. 7.根据权利要求1所述的一种废茶叶-花生壳基活性炭的制备方法,其特征在于,所述浸渍时间为2小时。7. The preparation method of a kind of waste tea leaves-peanut shell-based activated carbon according to claim 1, characterized in that, the soaking time is 2 hours. 8.根据权利要求1所述的一种废茶叶-花生壳基活性炭的制备方法,其特征在于,所述煅烧温度为500℃。8. A method for preparing waste tea leaves-peanut shell-based activated carbon according to claim 1, characterized in that the calcination temperature is 500°C. 9.根据权利要求1或8所述的一种废茶叶-花生壳基活性炭的制备方法,其特征在于,所述煅烧时间为2小时。9. A method for preparing waste tea leaves-peanut shell-based activated carbon according to claim 1 or 8, characterized in that the calcination time is 2 hours.
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CN108658568A (en) * 2018-05-30 2018-10-16 安徽润晟建设有限公司 A kind of preparation method of cracking resistance insulating brick
CN109534339A (en) * 2018-11-21 2019-03-29 常熟理工学院 It is a kind of pine squama matrix activated carbon and its nanocomposite preparation method
CN111632576A (en) * 2020-05-12 2020-09-08 北京林业大学 A method for preparing a dual-functional material with adsorption and catalysis by using agricultural and forestry waste
CN115924915A (en) * 2022-11-18 2023-04-07 安徽农业大学 A kind of preparation method of Solidago canadensis activated carbon

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CN102530941A (en) * 2011-12-16 2012-07-04 北京工业大学 Sludge-based activated carbon and preparation method thereof
CN103771411A (en) * 2012-10-24 2014-05-07 南京席瑞斯化工有限公司 Preparation method for active carbon
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CN108658568A (en) * 2018-05-30 2018-10-16 安徽润晟建设有限公司 A kind of preparation method of cracking resistance insulating brick
CN109534339A (en) * 2018-11-21 2019-03-29 常熟理工学院 It is a kind of pine squama matrix activated carbon and its nanocomposite preparation method
CN111632576A (en) * 2020-05-12 2020-09-08 北京林业大学 A method for preparing a dual-functional material with adsorption and catalysis by using agricultural and forestry waste
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