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CN103408011A - Preparation method of sargassum horneri matrix activated carbon - Google Patents

Preparation method of sargassum horneri matrix activated carbon Download PDF

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CN103408011A
CN103408011A CN2013103199154A CN201310319915A CN103408011A CN 103408011 A CN103408011 A CN 103408011A CN 2013103199154 A CN2013103199154 A CN 2013103199154A CN 201310319915 A CN201310319915 A CN 201310319915A CN 103408011 A CN103408011 A CN 103408011A
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曾淦宁
艾宁
周鸿艳
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Datong Jinsheng Haoda Carbon Industry Co ltd
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Zhejiang University of Technology ZJUT
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Abstract

The invention discloses a preparation method of sargassum horneri matrix activated carbon. The preparation method comprises the following steps: (1), mixing sargassum horneri powder and activator with water for impregnating treatment for 2-24 h; (2), placing the mixture I under an inert atmosphere, raising the temperature of the mixture I to 400-600 DEG C according to a rate of 10-30 DEG C/min; performing activating treatment on the mixture I for 1-3 h; then washing the mixture I with hot acid solution and hot distilled water in sequence until the pH value of the mixture does not change; drying the mixture I to obtain a product A; (3), mixing the product A with boiling oxidant solution to enable the product A to react with the boiling oxidant solution for 1-3 h; then, washing the mixture II with hot distilled water until the pH value of the mixture II does not change; drying the mixture II to obtain a product B; (4), performing high-heat treatment on the product B at 300-500 DEG C, so as to obtain the sargassum horneri matrix activated carbon. The activated carbon prepared through the preparation method has the advantages that most pores are mesoporous, the pores are well-developed, the ash content is low, and the adsorbability to hexavalent chromium is higher.

Description

一种铜藻基活性炭的制备方法A kind of preparation method of copper algae-based activated carbon

技术领域technical field

本发明涉及一种活性炭的制备方法,特点是以铜藻为原料制备活性炭的方法。The invention relates to a method for preparing activated carbon, which is characterized in that copper algae is used as a raw material to prepare activated carbon.

背景技术Background technique

活性炭是一种多孔性物质,具有发达的孔隙结构、巨大的比表面积、丰富的表面官能团、稳定的化学性质等优点,因而得到广泛的应用。但活性炭产业目前仍基本属于“资源消耗型”产业,因而,原料来源是限制活性炭产业发展的一个重要原因。目前,国内外选用的活性炭制备的原料主要分为:煤炭、木质和工业产品及工农业废料。近年来,传统原料受到资源、能源和环境等问题的限制,使得寻找活性炭原料的目光逐渐从陆地转向海洋。大量研究已经表明,大型海藻具有良好的重金属及有机污染物的吸附性能,且往往具备较高的纤维素含量,以及生长速度快、产量大、易于收割、不与粮争地等优势,因而在活性炭制备领域极具潜力。国际上,2009年以来,以两种大型海藻Sargassum Longifolium(S.L.)和Hypnea Valentiae(H.V.)为原料,通过调节活化剂氯化锌的配比控制活性炭孔径分布,制造出以中孔为主的活性炭,并且有机械强度高、灰分含量低的优点;以Posidonia Oceanic(L.)纤维为原料,分别采用水蒸汽活化法、氯化锌活化法进行活性炭的制备。但整体来看,目前将大型海藻作为活性炭制备原料的相关报道较少,所制得活性炭比表面积以铜藻为原料未见报道。Activated carbon is a kind of porous substance, which has the advantages of developed pore structure, huge specific surface area, abundant surface functional groups, and stable chemical properties, so it has been widely used. However, the activated carbon industry is still basically a "resource-consuming" industry. Therefore, the source of raw materials is an important reason that restricts the development of the activated carbon industry. At present, the raw materials for activated carbon preparation at home and abroad are mainly divided into: coal, wood and industrial products, and industrial and agricultural waste. In recent years, traditional raw materials are limited by issues such as resources, energy and the environment, making the search for activated carbon raw materials gradually shift from land to sea. A large number of studies have shown that macroalgae have good adsorption properties for heavy metals and organic pollutants, and often have high cellulose content, as well as advantages such as fast growth, large yield, easy harvesting, and no competition for land with food. The field of activated carbon preparation has great potential. Internationally, since 2009, two large seaweeds, Sargassum Longifolium (S.L.) and Hypnea Valentiae (H.V.), have been used as raw materials to control the pore size distribution of activated carbon by adjusting the ratio of activator zinc chloride to produce activated carbon with mainly mesopores. , and has the advantages of high mechanical strength and low ash content; using Posidonia Oceanic (L.) fiber as raw material, activated carbon is prepared by steam activation method and zinc chloride activation method. But on the whole, there are few related reports on the use of macroalgae as raw materials for the preparation of activated carbon, and there are no reports on the specific surface area of the prepared activated carbon using copper algae as raw materials.

活性炭通常分为炭化和活化两步,传统的化学活化法对设备腐蚀性大、污染环境、活性炭中残留有化学药品活化剂,应用方面受到限制。炭化过程中最重要的因素是炭化最终温度和炭化升温速度,炭化产物品质还与原料化学性质及物理粒径等密切相关。活化温度是决定活性炭孔隙结构形成速度的主要因素之一。活化主反应为可逆吸热反应,提高反应温度有利于正反应进行,但温度过高,活性炭的孔隙结构易发生变化,微孔减小,大孔增加,强度下降,得率减小。因此,确保得率、减少能耗、优化工艺、提高品质始终是活性炭生产的基本要求。Activated carbon is usually divided into two steps: carbonization and activation. The traditional chemical activation method is highly corrosive to equipment, pollutes the environment, and there are chemical activators in the activated carbon, so its application is limited. The most important factors in the carbonization process are the final temperature of carbonization and the heating rate of carbonization. The quality of carbonization products is also closely related to the chemical properties and physical particle size of raw materials. Activation temperature is one of the main factors that determine the formation rate of activated carbon pore structure. The main reaction of activation is a reversible endothermic reaction. Increasing the reaction temperature is conducive to the forward reaction. However, if the temperature is too high, the pore structure of activated carbon will easily change, the micropores will decrease, the macropores will increase, the strength will decrease, and the yield will decrease. Therefore, ensuring yield, reducing energy consumption, optimizing process, and improving quality are always the basic requirements for activated carbon production.

铜藻(Sargassum Horneri)是我国东南沿海的优势物种,已被列为暖海温带海洋生态环境修复的首选物种和重建海底藻场的重要物种之一。但铜藻的工业化、资源化利用还远未成熟、亟待开发。因此,利用铜藻制备活性炭,成为铜藻开发应用领域的前沿课题。本专利所得的研究结果可为大型海藻基活性炭的研究提供基础和借鉴,同时也为海洋生态修复工程中大规模增养殖非食用性大型海藻后亟需的工业化利用进行前期准备。Copper algae (Sargassum Horneri) is a dominant species in the southeast coast of my country, and has been listed as the preferred species for the restoration of warm sea temperate marine ecological environment and one of the important species for rebuilding seabed algae farms. However, the industrialization and resource utilization of copper algae are still far from mature and urgently need to be developed. Therefore, the use of copper algae to prepare activated carbon has become a frontier topic in the development and application of copper algae. The research results obtained in this patent can provide the basis and reference for the research of macroalgae-based activated carbon, and also make preliminary preparations for the urgently needed industrial utilization after large-scale breeding of non-edible macroalgae in marine ecological restoration projects.

发明内容Contents of the invention

本发明所要解决的技术问题是提供一种铜藻基活性炭的制备方法,该方法制备的活性炭以中孔为主,并且孔隙发达,灰分含量低,对六价铬有较高的吸附性能。The technical problem to be solved by the present invention is to provide a method for preparing copper algae-based activated carbon. The activated carbon prepared by this method has mainly mesopores, well-developed pores, low ash content, and high adsorption performance for hexavalent chromium.

为解决上述技术问题,本发明所采用的技术方案是:In order to solve the problems of the technologies described above, the technical solution adopted in the present invention is:

一种用铜藻制备活性炭的方法,包括如下步骤:A method for preparing activated carbon with copper algae, comprising the steps of:

(1)将铜藻粉末、活化剂和水混合,进行浸渍处理2~24h;所述的活化剂为氯化锌或者磷酸或者氢氧化钾;其中铜藻粉末与活化剂的重量比为1:3~5;(1) Mix copper algae powder, activator and water, and perform immersion treatment for 2 to 24 hours; the activator is zinc chloride or phosphoric acid or potassium hydroxide; wherein the weight ratio of copper algae powder to the activator is 1: 3~5;

(2)将浸渍物置于惰性气氛下按10~30℃/min的速率升温至400~600℃,进行1~3h的活化处理,然后用热酸溶液洗涤,再用热蒸馏水洗涤至pH不变,干燥得到产物A;(2) Put the impregnation in an inert atmosphere and raise the temperature to 400-600°C at a rate of 10-30°C/min, perform an activation treatment for 1-3 hours, then wash with hot acid solution, and then wash with hot distilled water until the pH remains unchanged , drying to obtain product A;

(3)将产物A与沸腾的氧化剂溶液混合,反应1~3h,然后用热蒸馏水洗涤至pH不变并干燥得到产物B;(3) Mix product A with boiling oxidant solution, react for 1-3 hours, then wash with hot distilled water until the pH remains constant and dry to obtain product B;

(4)将产物B于300~500℃进行高温热处理1~3h,即得到铜藻基活性炭产品。(4) The product B is subjected to high-temperature heat treatment at 300-500°C for 1-3 hours to obtain copper algae-based activated carbon products.

本发明中,所述铜藻粉末可通过如下处理获得:将采集的新鲜铜藻用水清洗去除杂质,烘干后切割,于粉碎机中粉碎,优选粉碎后铜藻粉末的粒径在20~100目。In the present invention, the copper algae powder can be obtained by the following treatment: the collected fresh copper algae is washed with water to remove impurities, cut after drying, and pulverized in a pulverizer. head.

所述步骤(1)中,所述的活化剂是氯化锌或者磷酸或者氢氧化钾,优选氯化锌或磷酸,最优选氯化锌。所述的浸渍处理在室温、搅拌下进行。所述的铜藻粉末与水的重量比一般在1:5。In the step (1), the activator is zinc chloride or phosphoric acid or potassium hydroxide, preferably zinc chloride or phosphoric acid, most preferably zinc chloride. The impregnation treatment is carried out at room temperature under stirring. The weight ratio of the copper algae powder to water is generally 1:5.

所述步骤(2)中,所述的惰性气氛优选为氮气,气体流量为50~150L/h。洗涤用的热酸溶液优选煮沸的盐酸溶液。洗涤用的热蒸馏水的温度一般在70~100℃。In the step (2), the inert atmosphere is preferably nitrogen, and the gas flow rate is 50-150 L/h. The hot acid solution for washing is preferably a boiled hydrochloric acid solution. The temperature of hot distilled water for washing is generally 70-100°C.

所述步骤(3)中,所述的氧化剂是10~50%质量分数的硝酸或硫酸或盐酸溶液,优选硝酸溶液。每1g产物A中,氧化剂溶液的加入量是5~20mL。洗涤用的热蒸馏水的温度一般在70~100℃。所述的氧化反应在室温下进行。In the step (3), the oxidizing agent is 10-50% by mass fraction of nitric acid or sulfuric acid or hydrochloric acid solution, preferably nitric acid solution. In every 1g of product A, the addition amount of oxidizing agent solution is 5~20mL. The temperature of hot distilled water for washing is generally 70-100°C. The oxidation reaction is carried out at room temperature.

所述步骤(2)、(3)中,所述的干燥分别在100~110℃的温度条件下进行,干燥时间为3~24h。In the steps (2) and (3), the drying is carried out at a temperature of 100-110° C., and the drying time is 3-24 hours.

本发明所述方法制备的铜藻基活性炭产品,其规格如下:比表面积1014~2314m2·g-1,碘值1005.7~1197.8mg·g-1,亚甲基蓝值9.0~12.0mL·0.1g-1,焦糖脱色率90~115%,六价铬饱和吸附量24.2~83.5mg·g-1,灰分含量0.2~0.8%。The copper algae-based activated carbon product prepared by the method of the present invention has the following specifications: specific surface area 1014-2314m2 ·g -1 , iodine value 1005.7-1197.8mg·g -1 , methylene blue value 9.0-12.0mL·0.1g -1 , the decolorization rate of caramel is 90-115%, the saturated adsorption capacity of hexavalent chromium is 24.2-83.5 mg·g -1 , and the ash content is 0.2-0.8%.

与现有技术相比,本发明的有益效果在于:Compared with prior art, the beneficial effect of the present invention is:

(a)本发明采用铜藻作为活性炭的制备原料,铜藻的含氧量高,炭化过程中由于含氧官能团的断裂,以H2O、CO、CO2等形态放出的氧进一步提高了扩孔性能;同时由于含氧量高,热分解时易与氢化合生成水,所生成的焦油或其他胶质体也将相对较少。(a) The present invention uses copper algae as the raw material for the preparation of activated carbon. The oxygen content of copper algae is high. During the carbonization process, due to the breakage of oxygen-containing functional groups, the oxygen released in the form of H 2 O, CO, and CO 2 further improves the expansion. Pore performance; at the same time, due to the high oxygen content, it is easy to combine with hydrogen to form water during thermal decomposition, and the generated tar or other colloids will be relatively small.

(b)本发明采用对化学活化后的活性炭进一步进行氧化改性、高温热处理,活性炭表面羧基、酚羟基、内酯基等酸性含氧官能团含量显著提高,且发现在经适当条件下高温处理一定时间之后,可以在不破坏氧化官能团的情况下使原先由于氧化而导致的孔道被堵塞现象得较好改善,使得制成的活性炭与其与现有技术相比具有比表面积高、特定吸附性能强和灰分含量低等优点,特别适用于含重金属离子废水的净化吸附,同时,也可以用于其它气体的吸附净化过程。(b) The present invention adopts further oxidative modification and high-temperature heat treatment on the activated carbon after chemical activation, and the content of acidic oxygen-containing functional groups such as carboxyl, phenolic hydroxyl, and lactone groups on the surface of the activated carbon is significantly increased, and it is found that after high-temperature treatment under appropriate conditions, certain After a period of time, the pore blockage caused by oxidation can be better improved without destroying the oxidation functional group, so that the activated carbon has high specific surface area, strong specific adsorption performance and With the advantages of low ash content, it is especially suitable for the purification and adsorption of wastewater containing heavy metal ions. At the same time, it can also be used for the adsorption and purification process of other gases.

附图说明Description of drawings

图1分别是实例1-4的铜藻基活性炭扫描电镜图,其中A-实施例1,B-实施例2,C-实施例3,D-实施例4。Fig. 1 is the scanning electron micrograph of the copper algae-based activated carbon of example 1-4 respectively, wherein A-embodiment 1, B-example 2, C-example 3, D-example 4.

具体实施方式Detailed ways

下面结合实例进一步描述本发明的技术特点,但本发明的保护范围不限于此。The technical characteristics of the present invention are further described below in conjunction with examples, but the protection scope of the present invention is not limited thereto.

实施例1Example 1

将采集于浙南温州海域的铜藻,简单风干后用自来水洗涤去除盐分、杂质,接着用去离子水洗涤数次后沥干,在100℃下烘24h至恒重。干燥的铜藻再进行粉碎,筛选出20~40目的粉末。称取10g干燥铜藻粉末,加入100g质量分数为50%的氯化锌溶液,25℃下搅拌2h。然后将浸渍混合物转移至真空管式炉中,在流量120L·h-1的氮气保护下,以10℃·min-1的速率升温至500℃,活化1h。活化得到的样品用1mol·L-1的HCl溶液煮沸30min,继续用煮沸HCl溶液洗涤数次,用95℃的去离子水洗涤至pH不变为止,然后在100℃下烘24h至恒重,得到产物A1The copper algae collected in the Wenzhou sea area in southern Zhejiang were simply air-dried, washed with tap water to remove salt and impurities, then washed several times with deionized water, drained, and dried at 100°C for 24 hours to constant weight. The dried copper algae is crushed again, and the powder of 20-40 meshes is screened out. Weigh 10g of dry copper algae powder, add 100g of zinc chloride solution with a mass fraction of 50%, and stir at 25°C for 2h. Then the impregnated mixture was transferred to a vacuum tube furnace, and under the protection of nitrogen with a flow rate of 120 L·h -1 , the temperature was raised to 500°C at a rate of 10°C·min -1 and activated for 1 h. The activated sample was boiled with 1 mol L - 1 HCl solution for 30 min, washed several times with boiled HCl solution, washed with deionized water at 95°C until the pH remained constant, and then baked at 100°C for 24 h to constant weight. The product A 1 is obtained.

向1g产物A1中加入10mL10%的沸腾硝酸溶液,25℃静置氧化2h。氧化的样品用95℃的去离子水洗涤至pH不变为止,然后在100℃下烘24h至恒重,得到产物B1。将产物B1放入300℃的马弗炉进行高温热处理2h,即得到活性炭产品C1,其性能见表1。Add 10mL of 10% boiling nitric acid solution to 1g of product A1 , and let it stand for oxidation at 25°C for 2h. The oxidized sample was washed with deionized water at 95°C until the pH remained constant, and then baked at 100°C for 24 hours to constant weight to obtain product B 1 . Put the product B 1 into a muffle furnace at 300°C for high-temperature heat treatment for 2 hours to obtain the activated carbon product C 1 , whose properties are shown in Table 1.

实施例2Example 2

将采集于浙南温州海域的铜藻,简单风干后用自来水洗涤去除盐分、杂质,接着用去离子水洗涤数次后沥干,在100℃下烘24h至恒重。干燥的铜藻再进行粉碎,筛选出20~40目的粉末。称取10g干燥铜藻粉末,加入100g质量分数为50%的氯化锌溶液,25℃下搅拌10h。然后将浸渍混合物转移至真空管式炉中,在流量100L·h-1的氮气保护下,以20℃·min-1的速率升温至600℃,活化3h。活化得到的样品用1mol·L-1的HCl溶液煮沸30min,继续用煮沸HCl溶液洗涤数次,用95℃的去离子水洗涤至pH不变为止,然后在100℃下烘24h至恒重,得到产物A2The copper algae collected in the Wenzhou sea area in southern Zhejiang were simply air-dried, washed with tap water to remove salt and impurities, then washed several times with deionized water, drained, and dried at 100°C for 24 hours to constant weight. The dried copper algae is crushed again, and the powder of 20-40 meshes is screened out. Weigh 10g of dry copper algae powder, add 100g of zinc chloride solution with a mass fraction of 50%, and stir at 25°C for 10h. Then the impregnated mixture was transferred to a vacuum tube furnace, and under the protection of nitrogen with a flow rate of 100L·h -1 , the temperature was raised to 600°C at a rate of 20°C·min -1 for activation for 3h. The activated sample was boiled with 1 mol L - 1 HCl solution for 30 min, washed several times with boiled HCl solution, washed with deionized water at 95°C until the pH remained constant, and then baked at 100°C for 24 h to constant weight. The product A2 is obtained.

向1g产物A2中加入10mL20%的沸腾硝酸溶液,25℃静置氧化1h。氧化的样品用95℃的去离子水洗涤至pH不变为止,然后在100℃下烘24h至恒重,得到产物B2。将产物B2放入400℃的马弗炉进行高温热处理3h,即得到活性炭产品C2,其性能见表1。Add 10mL of 20% boiling nitric acid solution to 1g of product A2 , and let it stand for oxidation at 25°C for 1h. The oxidized sample was washed with deionized water at 95°C until the pH remained unchanged, and then baked at 100°C for 24 hours to constant weight to obtain product B 2 . The product B 2 was placed in a muffle furnace at 400°C for high temperature heat treatment for 3 hours to obtain the activated carbon product C 2 , and its properties are shown in Table 1.

实施例3Example 3

将采集于浙南温州海域的铜藻,简单风干后用自来水洗涤去除盐分、杂质,接着用去离子水洗涤数次后沥干,在100℃下烘24h至恒重。干燥的铜藻再进行粉碎,筛选出20~40目的粉末。称取10g干燥铜藻粉末,加入100g质量分数为30%的氯化锌溶液,25℃下搅拌10h。然后将浸渍混合物转移至真空管式炉中,在流量150L·h-1的氮气保护下,以30℃·min-1的速率升温至600℃,活化1h。活化得到的样品用1mol·L-1的HCl溶液煮沸30min,继续用煮沸HCl溶液洗涤数次,用95℃的去离子水洗涤至pH不变为止,然后在100℃下烘24h至恒重,得到产物A3The copper algae collected in the Wenzhou sea area in southern Zhejiang were simply air-dried, washed with tap water to remove salt and impurities, then washed several times with deionized water, drained, and dried at 100°C for 24 hours to constant weight. The dried copper algae is crushed again, and the powder of 20-40 meshes is screened out. Weigh 10g of dry copper algae powder, add 100g of zinc chloride solution with a mass fraction of 30%, and stir at 25°C for 10h. Then the impregnation mixture was transferred to a vacuum tube furnace, and under the protection of nitrogen with a flow rate of 150 L·h -1 , the temperature was raised to 600°C at a rate of 30°C·min -1 and activated for 1 h. The activated sample was boiled with 1 mol L - 1 HCl solution for 30 min, washed several times with boiling HCl solution, washed with deionized water at 95°C until the pH remained constant, and then baked at 100°C for 24 h to constant weight. The product A3 is obtained.

向1g产物A3中加入10mL10%的沸腾硝酸溶液,25℃静置氧化3h。氧化的样品用95℃的去离子水洗涤至pH不变为止,然后在100℃下烘24h至恒重,得到产物B3。将产物B3放入500℃的马弗炉进行高温热处理2h,即得到活性炭产品C3,其性能见表1。Add 10mL of 10% boiling nitric acid solution to 1g of product A3 , and let it stand for oxidation at 25°C for 3h. The oxidized sample was washed with deionized water at 95°C until the pH remained unchanged, and then baked at 100°C for 24 hours to constant weight to obtain product B 3 . Put the product B 3 into a muffle furnace at 500°C for high-temperature heat treatment for 2 hours to obtain the activated carbon product C 3 , whose properties are shown in Table 1.

实施例4Example 4

将采集于浙南温州海域的铜藻,简单风干后用自来水洗涤去除盐分、杂质,接着用去离子水洗涤数次后沥干,在100℃下烘24h至恒重。干燥的铜藻再进行粉碎,筛选出20~40目的粉末。称取10g干燥铜藻粉末,加入100g质量分数为50%的磷酸溶液,25℃下搅拌10h。然后将浸渍混合物转移至真空管式炉中,在流量100L·h-1的氮气保护下,以10℃·min-1的速率升温至400℃,活化1h。活化得到的样品用1mol·L-1的HCl溶液煮沸30min,继续用煮沸HCl溶液洗涤数次,用95℃的去离子水洗涤至pH不变为止,然后在100℃下烘24h至恒重,得到产物A4The copper algae collected in the Wenzhou sea area in southern Zhejiang were simply air-dried, washed with tap water to remove salt and impurities, then washed several times with deionized water, drained, and dried at 100°C for 24 hours to constant weight. The dried copper algae is crushed again, and the powder of 20-40 meshes is screened out. Weigh 10g of dry copper algae powder, add 100g of phosphoric acid solution with a mass fraction of 50%, and stir at 25°C for 10h. Then the impregnation mixture was transferred to a vacuum tube furnace, and under the protection of nitrogen with a flow rate of 100 L·h -1 , the temperature was raised to 400°C at a rate of 10°C·min -1 and activated for 1 h. The activated sample was boiled with 1 mol L - 1 HCl solution for 30 min, washed several times with boiled HCl solution, washed with deionized water at 95°C until the pH remained constant, and then baked at 100°C for 24 h to constant weight. The product A4 is obtained.

向1g产物A4中加入10mL30%的沸腾硝酸溶液,25℃静置氧化2h。氧化的样品用95℃的去离子水洗涤至pH不变为止,然后在100℃下烘24h至恒重,得到产物B4。将产物B4放入400℃的马弗炉进行高温热处理1h,即得到活性炭产品C4,其性能见表1。Add 10mL of 30% boiling nitric acid solution to 1g of product A4 , and let it stand for oxidation at 25°C for 2h. The oxidized sample was washed with deionized water at 95°C until the pH remained unchanged, and then baked at 100°C for 24 hours to constant weight to obtain product B 4 . Put the product B 4 into a muffle furnace at 400°C for high-temperature heat treatment for 1 hour to obtain the activated carbon product C 4 , whose properties are shown in Table 1.

实施例5Example 5

将采集于浙南温州海域的铜藻,简单风干后用自来水洗涤去除盐分、杂质,接着用去离子水洗涤数次后沥干,在100℃下烘24h至恒重。干燥的铜藻再进行粉碎,筛选出20~40目的粉末。称取10g干燥铜藻粉末,加入100g质量分数为30%的磷酸溶液,25℃下搅拌10h。然后将浸渍混合物转移至真空管式炉中,在流量100L·h-1的氮气保护下,以20℃·min-1的速率升温至400℃,活化2h。活化得到的样品用1mol·L-1的HCl溶液煮沸30min,继续用煮沸HCl溶液洗涤数次,用95℃的去离子水洗涤至pH不变为止,然后在100℃下烘24h至恒重,得到产物A5The copper algae collected in the Wenzhou sea area in southern Zhejiang were briefly air-dried, washed with tap water to remove salt and impurities, then washed several times with deionized water, drained, and dried at 100°C for 24 hours to constant weight. The dried copper algae is crushed again, and the powder of 20-40 meshes is screened out. Weigh 10g of dry copper algae powder, add 100g of phosphoric acid solution with a mass fraction of 30%, and stir at 25°C for 10h. Then the impregnation mixture was transferred to a vacuum tube furnace, and under the protection of nitrogen with a flow rate of 100L·h -1 , the temperature was raised to 400°C at a rate of 20°C·min -1 for activation for 2h. The activated sample was boiled with 1 mol L - 1 HCl solution for 30 min, washed several times with boiling HCl solution, washed with deionized water at 95°C until the pH remained constant, and then baked at 100°C for 24 h to constant weight. The product A5 is obtained.

向1g产物A5中加入10mL20%的沸腾硝酸溶液,25℃静置氧化3h。氧化的样品用95℃的去离子水洗涤至pH不变为止,然后在100℃下烘24h至恒重,得到产物B5。将产物B5放入300℃的马弗炉进行高温热处理2h,即得到活性炭产品C5,其性能见表1。Add 10mL of 20% boiling nitric acid solution to 1g of product A5 , and let it stand for oxidation at 25°C for 3h. The oxidized sample was washed with deionized water at 95°C until the pH remained constant, and then baked at 100°C for 24 hours to constant weight to obtain product B 5 . Put the product B 5 into a muffle furnace at 300°C for high-temperature heat treatment for 2 hours to obtain the activated carbon product C 5 , whose properties are shown in Table 1.

铜藻基活性炭结构性能测试:Structural performance test of copper algae-based activated carbon:

采用美国Micromeritics公司ASAP2020自动吸附仪测定活性炭的比表面积,其比表面积由标准BET法计算。采用日本Hitachi公司HitachiS-4700扫描电子显微镜观察活性炭的表面形貌和孔隙结构。The specific surface area of activated carbon was measured by ASAP2020 automatic adsorption instrument from American Micromeritics Company, and its specific surface area was calculated by the standard BET method. The surface morphology and pore structure of activated carbon were observed with a Hitachi S-4700 scanning electron microscope from Hitachi, Japan.

活性炭灰分含量的测定参照“GB/T12496.3-1999”木质活性炭灰分含量测定方法进行;碘吸附值的测定参照“GB/T12496.8-1999”木质活性炭碘吸附值测定方法进行;焦糖脱色率的测定参照“GB/T12496.9-1999”木质活性炭焦糖脱色率测定方法进行;亚甲基蓝的吸附值测定参照“GB/T12496.10-1999”木质活性炭碘吸附值测定方法进行;Cr6+浓度的测定采用邻苯碳酰二肼显色法,根据朗伯-比尔定律计算Cr6+浓度,并计算活性炭的吸附容量。The determination of activated carbon ash content is carried out according to the "GB/T12496.3-1999" determination method of wood activated carbon ash content; The determination of the rate is carried out according to the "GB/T12496.9-1999" method for the determination of the caramel decolorization rate of woody activated carbon; the determination of the adsorption value of methylene blue is carried out according to the "GB/T12496.10-1999" method for the determination of the iodine adsorption value of woody activated carbon; Cr 6+ The concentration was determined by o-phenylcarbazide chromogenic method, and the Cr 6+ concentration was calculated according to the Lambert-Beer law, and the adsorption capacity of activated carbon was calculated.

表1铜藻基活性炭性能Table 1 Performance of copper algae-based activated carbon

Figure BDA00003567542300071
Figure BDA00003567542300071

Claims (8)

1. the preparation method of a Sargassum horneri matrix activated carbon, comprise the steps:
(1) Sargassum horneri powder, activator and water are mixed, carry out dip treating 2~24h; Described activator is zinc chloride or phosphoric acid or potassium hydroxide; Wherein the weight ratio of Sargassum horneri powder and activator is 1:3~5;
(2) macerate is placed in to the speed by 10~30 ℃/min under inert atmosphere and is warming up to 400~600 ℃, carry out the activation treatment of 1~3h, then use the hot acid solution washing, the reusable heat distilled water wash is constant to pH, and drying obtains product A;
(3) product A is mixed with the oxidizing agent solution of boiling, reaction 1~3h, then wash the constant and dry product B that obtains to pH with hot distilled water;
(4) product B is carried out to high-temperature heat treatment 1~3h in 300~500 ℃, namely obtain Sargassum horneri matrix activated carbon product.
2. according to preparation method claimed in claim 1, it is characterized in that: the median size of the Sargassum horneri powder described in step (1) is 20~100 orders.
3. according to preparation method claimed in claim 1, it is characterized in that: the activator described in step (1) is zinc chloride or phosphoric acid.
4. according to preparation method claimed in claim 1, it is characterized in that: the inert atmosphere described in step (2) is nitrogen.
5. according to preparation method claimed in claim 1, it is characterized in that: the oxidizing agent solution described in step (3) is nitric acid or sulfuric acid or the hydrochloric acid soln of 10~50% massfractions.
6. according to preparation method claimed in claim 1, it is characterized in that: the oxidizing agent solution described in step (3) is the salpeter solution of 10~50% massfractions.
7. according to the described preparation method of claim 1 or 5, it is characterized in that: in step (3), in every 1g product A, the add-on of oxidizing agent solution is 5~20mL.
8. according to preparation method claimed in claim 1, it is characterized in that: the drying in step (2), (3) is carried out respectively under the temperature condition of 100~110 ℃, and be 3~24h time of drying.
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Cited By (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN103771408A (en) * 2013-12-30 2014-05-07 上海交通大学 Preparation method of algae-based active carbon for supercapacitor
CN108059161A (en) * 2017-12-19 2018-05-22 太原理工大学 Activated carbon for methane in concentrate coal bed gas and preparation method thereof
CN108298535A (en) * 2018-03-15 2018-07-20 浙江工业大学 A kind of continuous production method of Sargassum horneri mesopore activated carbon
CN109261137A (en) * 2018-09-30 2019-01-25 江苏斯沃得环保科技有限公司 A kind of composite reactive Carbon Materials and preparation method
CN117019120A (en) * 2023-09-12 2023-11-10 天津大学 High-flame-retardance honeycomb composite material and preparation method and application thereof
CN118307073A (en) * 2024-06-03 2024-07-09 天津永续新材料有限公司 Interface evaporation device with Sargassum horneri-melamine sponge double-cambered-surface structure, and preparation method and application thereof
CN118527116A (en) * 2024-07-19 2024-08-23 中国农业科学院农业环境与可持续发展研究所 Modified biomass charcoal-sodium alginate gel and preparation method and application thereof

Citations (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US20080152577A1 (en) * 2006-12-21 2008-06-26 Addiego William P Ordered mesoporous carbons and method for manufacturing same
CN101298327A (en) * 2008-01-24 2008-11-05 云南大学 Blue algae bloom activated char and preparation thereof
WO2010053959A2 (en) * 2008-11-04 2010-05-14 Donaldson Company, Inc Custom water adsorption material
CN101777652A (en) * 2010-01-13 2010-07-14 东南大学 Production method of active carbon of direct carbon conversion fuel cell
CN102627277A (en) * 2012-04-11 2012-08-08 太原理工大学 Modified active carbon and method for removing ammonia gas in intensive livestock farm
CN102774834A (en) * 2012-07-16 2012-11-14 太仓市联林活性炭厂 Method for preparing vinyl acetate supporter activated carbon from bamboo
CN102838111A (en) * 2012-09-25 2012-12-26 滑县大潮林物产有限责任公司 Method for removing potassium from activated carbon of super capacitor

Patent Citations (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US20080152577A1 (en) * 2006-12-21 2008-06-26 Addiego William P Ordered mesoporous carbons and method for manufacturing same
CN101298327A (en) * 2008-01-24 2008-11-05 云南大学 Blue algae bloom activated char and preparation thereof
WO2010053959A2 (en) * 2008-11-04 2010-05-14 Donaldson Company, Inc Custom water adsorption material
CN101777652A (en) * 2010-01-13 2010-07-14 东南大学 Production method of active carbon of direct carbon conversion fuel cell
CN102627277A (en) * 2012-04-11 2012-08-08 太原理工大学 Modified active carbon and method for removing ammonia gas in intensive livestock farm
CN102774834A (en) * 2012-07-16 2012-11-14 太仓市联林活性炭厂 Method for preparing vinyl acetate supporter activated carbon from bamboo
CN102838111A (en) * 2012-09-25 2012-12-26 滑县大潮林物产有限责任公司 Method for removing potassium from activated carbon of super capacitor

Non-Patent Citations (1)

* Cited by examiner, † Cited by third party
Title
R. ARAVINDHAN等: "Preparation and characterization of activated carbon from marine macro-algal biomass", 《JOURNAL OF HAZARDOUS MATERIALS》 *

Cited By (11)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN103771408A (en) * 2013-12-30 2014-05-07 上海交通大学 Preparation method of algae-based active carbon for supercapacitor
CN103771408B (en) * 2013-12-30 2015-10-28 上海交通大学 Based on the preparation method of the activated carbon for super capacitors of marine alga
CN108059161A (en) * 2017-12-19 2018-05-22 太原理工大学 Activated carbon for methane in concentrate coal bed gas and preparation method thereof
CN108298535A (en) * 2018-03-15 2018-07-20 浙江工业大学 A kind of continuous production method of Sargassum horneri mesopore activated carbon
CN109261137A (en) * 2018-09-30 2019-01-25 江苏斯沃得环保科技有限公司 A kind of composite reactive Carbon Materials and preparation method
CN117019120A (en) * 2023-09-12 2023-11-10 天津大学 High-flame-retardance honeycomb composite material and preparation method and application thereof
CN117019120B (en) * 2023-09-12 2025-03-21 天津大学 A highly flame-retardant honeycomb composite material and its preparation method and application
CN118307073A (en) * 2024-06-03 2024-07-09 天津永续新材料有限公司 Interface evaporation device with Sargassum horneri-melamine sponge double-cambered-surface structure, and preparation method and application thereof
CN118307073B (en) * 2024-06-03 2024-08-09 天津永续新材料有限公司 Interface evaporation device with Sargassum horneri-melamine sponge double-cambered-surface structure, and preparation method and application thereof
CN118527116A (en) * 2024-07-19 2024-08-23 中国农业科学院农业环境与可持续发展研究所 Modified biomass charcoal-sodium alginate gel and preparation method and application thereof
CN118527116B (en) * 2024-07-19 2024-09-27 中国农业科学院农业环境与可持续发展研究所 Modified biomass charcoal-sodium alginate gel and preparation method and application thereof

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