CN115318257A - Preparation method of sauce-flavor wine vinasse-based porous carbon composite ionic liquid gas adsorbent - Google Patents

Preparation method of sauce-flavor wine vinasse-based porous carbon composite ionic liquid gas adsorbent Download PDF

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CN115318257A
CN115318257A CN202210579292.3A CN202210579292A CN115318257A CN 115318257 A CN115318257 A CN 115318257A CN 202210579292 A CN202210579292 A CN 202210579292A CN 115318257 A CN115318257 A CN 115318257A
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赵天翔
罗兰
刘飞
杨春亮
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Guizhou University
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    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
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    • B01D53/00Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
    • B01D53/02Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols by adsorption, e.g. preparative gas chromatography
    • B01D53/04Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols by adsorption, e.g. preparative gas chromatography with stationary adsorbents
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Abstract

本发明公开了一种酱香酒酒糟基多孔炭复合离子液体气体吸附剂的制备方法,以白酒酿造大宗固废酱香酒酒糟为原料,经氢氟酸除杂预处理、高温碳化、二次活化获得比重轻、微孔结构发达、高比表面积的酒糟基多孔炭。同时,创新性地以质子型离子液体对多孔炭进行改性,创制热稳定性更高的酱香酒酒糟基多孔炭复合离子液体气体吸附剂,进而提高酒糟基多孔炭对低浓度气体的吸附容量和分离选择性,在CO2的选择性吸附分离应用中表现出优异的吸附分离性能,具有超高的比表面积、丰富的孔结构性质和丰富的活性位点,具备制备方法简单、易操作、成本低等优点,在天然气、沼气、低浓度煤层气及燃煤烟气等气体吸附分离领域表现出较好的工业应用前景。

Figure 202210579292

The invention discloses a preparation method of a Maoxiang distiller's grains-based porous carbon composite ionic liquid gas adsorbent. The bulk solid waste of liquor brewing is used as a raw material, and is subjected to hydrofluoric acid removal pretreatment, high-temperature carbonization, and secondary treatment. Activated to obtain vinasse-based porous carbon with light specific gravity, developed microporous structure and high specific surface area. At the same time, the porous carbon was innovatively modified with proton-type ionic liquid to create a composite ionic liquid gas adsorbent based on Maotai wine lees-based porous carbon with higher thermal stability, thereby improving the adsorption of low-concentration gas by the lees-based porous carbon. capacity and separation selectivity, showing excellent adsorption and separation performance in the application of selective adsorption and separation of CO2 , with ultra-high specific surface area, abundant pore structure properties and abundant active sites, with simple preparation method and easy operation , low cost and other advantages, it shows good industrial application prospects in the field of adsorption and separation of natural gas, biogas, low-concentration coalbed methane and coal-fired flue gas.

Figure 202210579292

Description

一种酱香酒酒糟基多孔炭复合离子液体气体吸附剂的制备 方法Preparation of Maotai-flavor wine lees-based porous carbon composite ionic liquid gas adsorbent method

技术领域technical field

本发明涉及一种酱香酒酒糟基多孔炭复合离子液体气体吸附剂的制备方 法,属于化工新材料及气体分离领域。The invention relates to a preparation method of a Maotai-flavored wine lees-based porous carbon composite ionic liquid gas adsorbent, which belongs to the field of new chemical materials and gas separation.

背景技术Background technique

气体吸附分离是各种原料气净化工段的一个重要步骤,同时也是缓解温 室气体排放有效的方法。典型的例子包括天然气净化、制氢、沼气纯化、乙 醇和氨的生产、以及来自工业燃烧排放源的气体分离等。天然气主要成分包 括70~95%的甲烷(CH4),其余为二氧化碳(CO2)、硫化氢(H2S)、二氧化 硫(SO2)等酸性气体和乙烷(C2H6)、丙烷(C3H8)轻质烃等气体。天然气 中存在的CO2、SO2、H2S等酸性气体,不利于储存和输送,应对其进行分离 富集,一方面减少管道腐蚀,提高天然气热值,另一方面酸性气体富集可为 物理利用、化工利用及生物利用提供基础资源。此外,CO2、SO2、H2S也广 泛存在于低浓度煤层气、沼气、工业燃煤烟气中,直接排放易加剧温室效应, 并造成碳资源浪费,面对这一类低浓度气体,高效实现气体选择性捕集是有 效利用碳资源的必经途径。工业上,基于物理作用的吸附分离具有能耗较低、 设备腐蚀性小、易于再生等优点,在气体分离中具有广阔的应用前景。在常 见的固体吸附剂中,多孔炭材料变压物理吸附分离CO2、H2S等气体具有明 显的便捷性和节能优势,可常温常压下操作,多孔炭吸附剂在降压或升温的 条件下即可再生循环利用。Gas adsorption separation is an important step in the purification process of various raw materials, and it is also an effective method to alleviate greenhouse gas emissions. Typical examples include natural gas purification, hydrogen production, biogas purification, ethanol and ammonia production, and gas separation from industrial combustion emission sources, among others. The main components of natural gas include 70-95% methane (CH 4 ), the rest are acid gases such as carbon dioxide (CO 2 ), hydrogen sulfide (H 2 S), sulfur dioxide (SO 2 ), ethane (C 2 H 6 ), propane (C 3 H 8 ) Gases such as light hydrocarbons. CO 2 , SO 2 , H 2 S and other acid gases in natural gas are not conducive to storage and transportation, so they should be separated and enriched. On the one hand, it can reduce pipeline corrosion and increase the calorific value of natural gas; Physical utilization, chemical utilization and biological utilization provide basic resources. In addition, CO 2 , SO 2 , and H 2 S also widely exist in low-concentration coalbed methane, methane, and industrial coal-fired flue gas. Direct emission will easily aggravate the greenhouse effect and cause waste of carbon resources. Faced with this type of low-concentration gas , Efficient selective gas capture is the only way to effectively utilize carbon resources. In industry, adsorption separation based on physical action has the advantages of low energy consumption, low equipment corrosion, easy regeneration, etc., and has broad application prospects in gas separation. Among the common solid adsorbents, the pressure swing physical adsorption of porous carbon materials has obvious convenience and energy-saving advantages in the separation of CO 2 , H 2 S and other gases. It can be operated under normal temperature and pressure. It can be regenerated and recycled under certain conditions.

贵州“茅台酒”驰名中外,每年酱香白酒产值超千亿。然而,酱香白酒酿 造过程中产生的大宗固废酒糟,目前主要用于饲料或有机肥料,利用率低, 且由于产品环境安全可靠性差、处理量小等,限制了规模化利用。酒糟固废 富含生物质,生物质成本低、环境友好,是可再生资源,用于制备生物质炭 多孔吸附剂前景广阔。目前,专利CN109835897B公开了一种金属/杂原子改 性白酒糟基活性炭及其制备方法,将酒糟、含氮化合物和过渡金属化合物于 研钵中研磨混合均匀,然后于600~900℃炭化1~3h,将炭化后的活性炭于酸 中浸泡5~15h,再经CO2或水蒸气活化气体气氛700~900℃活化2~5h,得金 属/杂原子改性白酒糟基活性炭,并用于常温常压下催化过硫酸盐氧化降解水 体中酸性红、甲基橙等有机污染物。专利CN108975333A公开了一种改性酒 糟基活性炭的制备方法,将酒糟原料加入磷酸溶液中超声25~35min,烘干后 510~530℃活化2~3h,再经NaOH溶液浸渍4~6h,洗涤、干燥、研磨后, 将得到酒糟活性炭加入Fe(NO3)3溶液中,滴加NaOH溶液至pH为8.1-8.3, 密封静置71-73h,得到羟基铁改性酒糟基活性炭,并用于去除水中刚果红。 专利CN109928391A公开了一种改性白酒糟基活性炭及其制备方法,将白酒 糟700~900℃碳化3~5h,再与氢氧化钾、硝酸钾、碳酸钾或氢氧化钠等活化 剂超声混合进行100~200℃水热反应,得到活性炭,然后将活性炭放入双氰 胺、三聚氰胺、氯化铵或尿素溶液中850~950℃碳化3~5h,得到改性白酒糟 基活性炭,并用于有机废水中有机污染物的催化过硫酸盐氧化降解。专利CN11210447A公开了一种黄酒酒糟基活性炭的制备方法,将酒糟与盐酸溶液 混合成浆状液再水浴锅中100℃水解,然后在400~600℃碳化1~5h,在通过 氢氧化钾、氯化钾、碳酸钾、氯化锌等活化剂溶液浸渍,得到黄酒糟基活性 炭。专利CN113479879A公开了一种基于二次发酵酒糟的活性碳材料及其制 备方法和应用,将生物质两次发酵后低温预碳化材料和碱性无机物直接混合, 再通过煅烧制得基于二次发酵酒糟的活性碳材料,并用作超级电容器电极材 料。Guizhou "Moutai" is well-known at home and abroad, and the annual output value of Maotai-flavored liquor exceeds 100 billion. However, the large amount of waste distiller's grains produced in the brewing process of Maotai-flavored liquor is currently mainly used for feed or organic fertilizer, with low utilization rate, and the large-scale utilization is limited due to poor environmental safety and reliability of the product and small processing capacity. Distiller's grain solid waste is rich in biomass, and biomass is low in cost and environmentally friendly. It is a renewable resource and has broad prospects for the preparation of biochar porous adsorbents. At present, the patent CN109835897B discloses a metal/heteroatom modified distiller's grain-based activated carbon and its preparation method. The distiller's grains, nitrogen-containing compounds and transition metal compounds are ground and mixed in a mortar, and then carbonized at 600-900°C for 1- 3h, soak the carbonized activated carbon in acid for 5-15h, and then activate it with CO2 or water vapor at 700-900℃ for 2-5h to obtain metal/heteroatom modified distiller's grains-based activated carbon, and use it at room temperature Press down to catalyze persulfate oxidation to degrade organic pollutants such as acid red and methyl orange in water. Patent CN108975333A discloses a preparation method of modified distiller's grain-based activated carbon. Distiller's grain raw material is added to phosphoric acid solution and ultrasonically charged for 25-35 minutes. After drying, it is activated at 510-530°C for 2-3 hours, then soaked in NaOH solution for 4-6 hours, washed, After drying and grinding, add distiller's grain activated carbon to Fe(NO 3 ) 3 solution, add NaOH solution dropwise to pH 8.1-8.3, seal and stand for 71-73 hours to obtain hydroxyl iron modified distiller's grain-based activated carbon, and use it to remove water Congo red. Patent CN109928391A discloses a modified distiller's grain-based activated carbon and its preparation method. Distiller's grains are carbonized at 700-900°C for 3-5 hours, and then ultrasonically mixed with activators such as potassium hydroxide, potassium nitrate, potassium carbonate or sodium hydroxide. Hydrothermal reaction at 100-200°C to obtain activated carbon, then put the activated carbon into dicyandiamide, melamine, ammonium chloride or urea solution and carbonize at 850-950°C for 3-5 hours to obtain modified distiller's grains-based activated carbon, which can be used in organic wastewater Catalytic persulfate oxidative degradation of organic pollutants. Patent CN11210447A discloses a preparation method of rice wine distiller's grains-based activated carbon. Distiller's grains and hydrochloric acid solution are mixed to form a slurry, which is then hydrolyzed in a water bath at 100°C, and then carbonized at 400-600°C for 1-5 hours. Potassium chloride, potassium carbonate, zinc chloride and other activator solutions impregnated to obtain rice distiller's grains-based activated carbon. Patent CN113479879A discloses an activated carbon material based on secondary fermentation distiller's grains and its preparation method and application. The low-temperature pre-carbonized material and alkaline inorganic matter are directly mixed after the biomass is fermented twice, and then calcined to obtain the activated carbon material based on secondary fermentation. Activated carbon material of distiller's grains, and used as supercapacitor electrode material.

已有专利主要将酒糟通过水解、热解、物理活化、化学活化或杂原子改 性等方法制备成生物质基活性炭、催化剂载体,主要用于染料、有机废水中 有机污染物的去除、降解或超级电容器材料。目前,尚未有采用酱香酒酒糟 制备应用于气体吸附分离的酒糟基微孔结构多孔炭材料的明确技术路线。Existing patents mainly prepare distiller's grains into biomass-based activated carbon and catalyst carrier through hydrolysis, pyrolysis, physical activation, chemical activation or heteroatom modification, which are mainly used for the removal, degradation or degradation of organic pollutants in dyes and organic wastewater. supercapacitor material. At present, there is no clear technical route for preparing distiller's grain-based porous carbon materials for gas adsorption and separation using Maotai-flavored wine distiller's grains.

发明内容Contents of the invention

本发明针对上述技术问题,提供了一种酱香酒酒糟基多孔炭复合离子液 体气体吸附剂的制备方法技术,该技术路线对酱香酒酒糟进行回收再利用, 制备出性能优良的多孔炭气体吸附剂,并采用离子液体对吸附剂进行改性, 所制备的材料应用于低分压气体回收的常温常压捕集极具开发价值。Aiming at the above technical problems, the present invention provides a preparation method technology of Maotai-flavored wine lees-based porous carbon composite ionic liquid gas adsorbent. The technical route recycles Maotai-flavored wine lees to prepare porous carbon gas with excellent performance. Adsorbents, and ionic liquids are used to modify the adsorbents. The prepared materials are of great development value for the normal temperature and pressure capture of low partial pressure gas recovery.

本发明制备酱香酒酒糟基多孔炭复合离子液体气体吸附剂所采用的技术 方案分为三个步骤:(1)酱香酒酒糟首先用0.5~2mol·L-1氢氟酸除杂预处理 12~24h,大量去离子水洗涤,干燥,并粉碎至50~200目,然后在氮气流量 100~200ml·min-1的氮气气氛下,以5~10℃·min-1升温至500℃预碳化1~3h, 得到多孔炭前体;(2)将上述多孔炭前体与活化剂按特定质量比机械球磨混 合,然后于氮气流量50~100ml·min-1的氮气气氛下,以5~10℃·min-1升温至 600~800℃二次碳化1~3h,经0.1~0.5mol·L-1的盐酸和去离子水洗涤至中性, 过滤,干燥,得到酱香酒酒糟基多孔炭;(3)将上述酱香酒酒糟基多孔炭与 离子液体按特定质量比加入溶剂中,经己烷、甲苯或丙酮洗涤,分离,干燥, 得到酱香酒酒糟基多孔炭复合离子液体气体吸附剂。The technical scheme adopted in the present invention to prepare the Maotai-flavored wine distiller's grain-based porous carbon composite ionic liquid gas adsorbent is divided into three steps: (1) The Maotai-flavored wine distiller's grains are firstly treated with 0.5-2mol·L -1 hydrofluoric acid to remove impurities 12-24 hours, washed with a large amount of deionized water, dried, and crushed to 50-200 meshes, and then heated to 500°C at 5-10°C·min -1 under a nitrogen atmosphere with a nitrogen flow rate of 100-200ml·min -1 . Carbonize for 1-3 hours to obtain a porous carbon precursor; (2) Mix the above-mentioned porous carbon precursor and activator by mechanical ball milling according to a specific mass ratio, and then, under a nitrogen atmosphere with a nitrogen flow rate of 50-100ml ·min 10°C·min -1 heated up to 600-800°C for secondary carbonization for 1-3 hours, washed with 0.1-0.5 mol·L -1 hydrochloric acid and deionized water until neutral, filtered, and dried to obtain Maotai-flavored wine lees-based porous (3) Add the above-mentioned Maotai-flavored wine lees-based porous carbon and ionic liquid into the solvent according to a specific mass ratio, wash with hexane, toluene or acetone, separate, and dry to obtain Maotai-flavored wine lees-based porous carbon composite ionic liquid gas Adsorbent.

上述步骤(1)中,所述的酱香酒酒糟的主要成分为包括但不限于发酵后 的高粱、稻壳、小麦、玉米。In the above step (1), the main components of the Maotai-flavored wine lees include but are not limited to fermented sorghum, rice husk, wheat, and corn.

上述步骤(2)中,所述多孔炭前体与活化剂的质量比为1:0.5~3。In the above step (2), the mass ratio of the porous carbon precursor to the activator is 1:0.5-3.

上述步骤(2)中,所述活化剂包括但不限于KOH、K2CO3、KHCO3、 K3PO4、NaOH、H3PO4、ZnCl2和NaNH2In the above step (2), the activator includes but not limited to KOH, K 2 CO 3 , KHCO 3 , K 3 PO 4 , NaOH, H 3 PO 4 , ZnCl 2 and NaNH 2 .

上述步骤(2)中,所述机械球磨时间为5~15min。In the above step (2), the mechanical ball milling time is 5-15 minutes.

上述步骤(3)中,所述酱香酒酒糟基多孔炭与离子液体质量比为1:0.1~1, 改性方法包括但不限于浸渍法、原位修饰法和化学嫁接法。In the above step (3), the mass ratio of the Maotai-flavored wine lees-based porous carbon to the ionic liquid is 1:0.1-1, and the modification methods include but not limited to impregnation, in-situ modification and chemical grafting.

上述步骤(3)中,所述离子液体为羧酸盐质子型离子液体。In the above step (3), the ionic liquid is a carboxylate proton type ionic liquid.

上述步骤(3)中,所述羧酸盐质子型离子液体的合成所需有机胺结构包 括但不限于二乙烯三胺、四乙烯五胺、聚乙烯亚胺,所述羧酸盐质子型离子 液体的合成所需多元羧酸结构包括但不限于亚氨基二乙酸、乙二胺-N,N`-二乙 酸、氮川三乙酸。In the above step (3), the organic amine structure required for the synthesis of the carboxylate proton ionic liquid includes but not limited to diethylenetriamine, tetraethylenepentamine, polyethyleneimine, and the carboxylate proton ion The polycarboxylic acid structures required for liquid synthesis include but are not limited to iminodiacetic acid, ethylenediamine-N,N'-diacetic acid, and nitrilotriacetic acid.

本发明的优点在于:The advantages of the present invention are:

(1)本发明“以废治废”,可实现酱香酒糟固废资源化利用,同时制备的 多孔炭复合离子液体气体吸附剂可实现多种气源领域(天然气、沼气、煤层 气、燃煤烟气)中低浓度气体的高效捕集回收,吸附剂易于再生循环利用。(1) The present invention "uses waste to treat waste", which can realize the resource utilization of Maotai-flavored distiller's grain solid waste, and the porous carbon composite ionic liquid gas adsorbent prepared at the same time can realize various gas source fields (natural gas, biogas, coal bed methane, combustion gas, etc.) High-efficiency capture and recovery of low-concentration gases in coal flue gas), and the adsorbent is easy to regenerate and recycle.

(2)本发明制备方法简单,有利于工业化操作,制备的多孔炭复合离 子液体气体吸附剂比表面积高,比重轻,微孔结构发达,活性位点丰富。(2) The preparation method of the present invention is simple, is beneficial to industrial operation, and the prepared porous carbon composite ionic liquid gas adsorbent has high specific surface area, light specific gravity, well-developed microporous structure and abundant active sites.

(3)本发明制备的多孔炭气体吸附剂在气体吸附分离中体现出良好的 性能,常压下,对CO2、CH4、H2S、SO2等具有良好吸附性能,吸附量5.20~10.7 mmol/g。(3) The porous carbon gas adsorbent prepared by the present invention exhibits good performance in gas adsorption and separation. Under normal pressure, it has good adsorption performance for CO 2 , CH 4 , H 2 S, SO 2 , etc., and the adsorption capacity is 5.20- 10.7 mmol/g.

(4)采用白酒酿造大宗固废——酱香酒酒糟为原料,将酒糟经预处理, 预碳化,二次活化得到酒糟基多孔炭,并用于CO2吸附研究。酒糟经氢氟酸 预处理可去除原料中金属氧化物及二氧化硅等灰分。预碳化选择500℃/2h 可有效去除酒糟原料中的水分、有机物杂质、挥发分等,为二次活化提供优 质的多孔炭前驱体。采用机械球磨法,有利于物理混合过程中机械球磨强度、 固固混合均匀程度、球磨时间的控制。(4) Distiller's grains-based porous carbon was obtained by pretreatment, pre-carbonization, and secondary activation of Maotai-flavored wine distiller's grains, a bulk solid waste from liquor brewing, and used for CO 2 adsorption research. The distiller's grains are pretreated with hydrofluoric acid to remove ash such as metal oxides and silicon dioxide in the raw materials. Selecting 500°C/2h for pre-carbonization can effectively remove moisture, organic impurities, volatiles, etc. in distiller's grain raw materials, and provide high-quality porous carbon precursors for secondary activation. The mechanical ball milling method is beneficial to the control of the mechanical ball milling intensity, solid-solid mixing uniformity, and ball milling time during the physical mixing process.

(5)本发明提供了一种利用大宗固废酱香酒酒糟制备多孔炭气体吸附 剂的方法,促进酒糟固废资源化利用,同时,为提高传统多孔炭吸附容量和 分离选择性,本发明利用酒糟基多孔炭结构中含有的羟基、羧基、C-O键等 特征官能团,作为离子液体改性多孔炭作用位点,将具有较好CO2、H2S、 SO2等酸性气体吸附容量、热稳定性高、富含氢键位点的多元羧酸盐质子型 离子液体固载在酒糟基多孔炭上,以促进酒糟基多孔炭对低浓度温室气体的 吸附性能,实现基础碳资源的高效选择性捕集分离。(5) The present invention provides a method for preparing a porous carbon gas adsorbent by using bulk solid waste Maotai-flavored wine distiller's grains, which promotes the resource utilization of distiller's grains solid waste. At the same time, in order to improve the adsorption capacity and separation selectivity of traditional porous carbon, the present invention Utilizing the characteristic functional groups such as hydroxyl, carboxyl, and CO bonds contained in the distiller's grain-based porous carbon structure, as the action site of the ionic liquid modified porous carbon, it will have better acid gas adsorption capacity such as CO 2 , H 2 S , SO 2 , heat Polycarboxylate protic ionic liquids with high stability and rich hydrogen bonding sites are immobilized on distillers grains-based porous carbon to promote the adsorption performance of distillers grains-based porous carbon for low-concentration greenhouse gases and realize efficient selection of basic carbon resources Sex capture separation.

(6)本发明重点考察了以下因素对酒糟多孔炭的制备及吸附性能的影 响。首先,考察活化剂用量对酒糟基多孔炭的影响,当KOH用量较少(<1 g)时酒糟基多孔炭中超微孔(<1nm)数量大,尤其是0.45~0.65nm范围内 的微孔结构分布较多,对应的常压下CO2吸附容量增大;反之,KOH用量 (>1g)增大,多孔炭比表面积显著增大,中介孔及大孔数量增多,而对应 的常压下CO2吸附容量减小。然后,考察了活化剂种类对酒糟基多孔炭的影 响,当在采用相同用量(0.5g)、不同活化剂条件下制备酒糟基多孔炭时, 多孔炭都具有大量微孔结构,但比表面积较低,相比而言,KOH的活化效 果具有显著优势,比表面积达到1059m2/g,对应的常压下CO2吸附容量最 大;最后,考察了二次活化温度对酒糟基多孔炭的影响,主要采用600-800℃ 进行因素考察,随温度升高,比表面积增大,但微孔数量先增大后减小,当活化温度为700℃时,酒糟基多孔炭具有最大的微孔(<1nm)数量,对应 的常压下CO2吸附容量最大。(6) The present invention focuses on the influence of the following factors on the preparation and adsorption performance of distiller's grain porous carbon. First, the effect of the amount of activator on distiller's grain-based porous carbon was investigated. When the amount of KOH was small (<1 g), the number of ultramicropores (<1 nm) in distiller's grain-based porous carbon was large, especially the micropores in the range of 0.45-0.65 nm. The structure distribution is more, and the CO 2 adsorption capacity under the corresponding normal pressure increases; on the contrary, the KOH dosage (>1g) increases, the specific surface area of the porous carbon increases significantly, and the number of mesopores and macropores increases, while the corresponding The CO2 adsorption capacity decreases. Then, the effect of the type of activator on distiller's grain-based porous carbon was investigated. When the distiller's grain-based porous carbon was prepared with the same amount (0.5 g) and different activators, the porous carbon had a large number of microporous structures, but the specific surface area was relatively small. In contrast, the activation effect of KOH has a significant advantage, the specific surface area reaches 1059m 2 /g, and the corresponding CO 2 adsorption capacity is the largest under normal pressure; finally, the influence of the secondary activation temperature on the distiller's grain-based porous carbon was investigated, Mainly use 600-800°C for factor investigation. As the temperature rises, the specific surface area increases, but the number of micropores first increases and then decreases. When the activation temperature is 700°C, distiller's grain-based porous carbon has the largest micropores (< 1nm) quantity, corresponding to the largest CO 2 adsorption capacity under normal pressure.

附图说明Description of drawings

图1为不同实施例制备得到的气体吸附剂SEM表征图:图1a为实施例 1;图1b为实施例2。Figure 1 is the SEM characterization diagram of the gas adsorbent prepared in different embodiments: Figure 1a is Example 1; Figure 1b is Example 2.

图2为实施例1制备得到气体吸附剂的TEM表征图。FIG. 2 is a TEM characterization diagram of the gas adsorbent prepared in Example 1.

图3为实施例1制备得到气体吸附剂的孔结构表征图:图3a为氮 气吸附脱附等温线;图3b为孔径分布曲线。Fig. 3 is the characterization diagram of the pore structure of the gas adsorbent prepared in Example 1: Fig. 3a is a nitrogen adsorption-desorption isotherm; Fig. 3b is a pore size distribution curve.

图4为实施例3[TEPAH][IDA]羧酸盐质子型离子液体合成路线示意图。Fig. 4 is a schematic diagram of the synthesis route of [TEPAH][IDA] carboxylate proton-type ionic liquid in Example 3.

图5为实施例4酒糟基多孔炭化学嫁接[SCA-2H][OOCR]羧酸盐质子型离 子液体改性示意图。Figure 5 is a schematic diagram of the chemical grafting of [SCA-2H][OOCR] carboxylate proton-type ionic liquid in Example 4 based on distiller's grains porous carbon.

图6为实施例1制备得到气体吸附剂的CO2、CH4、N2气体吸附曲线。FIG. 6 is the CO 2 , CH 4 , and N 2 gas adsorption curves of the gas adsorbent prepared in Example 1.

图7为实施例2制备得到气体吸附剂的SO2、H2S、CO2气体吸附曲线。Fig. 7 is the gas adsorption curves of SO 2 , H 2 S and CO 2 of the gas adsorbent prepared in Example 2.

图8为实施例2、实施例3、实施例4、实施例5制备得到气体吸附剂的 CO2气体吸附曲线,其中实施例2:KOH-C-1;实施例3: KOH-C-1/[TEPAH][IDA]0.2;实施例4:KOH-C-1/[SCA-2H][OOCR]0.2;实施 例5:KOH-C-1/[TEPAH][IDA]0.5Fig. 8 is the CO of gas adsorbent prepared by embodiment 2 , embodiment 3, embodiment 4, embodiment 5 Gas adsorption curve, wherein embodiment 2: KOH-C-1; Embodiment 3: KOH-C-1 /[TEPAH][IDA] 0.2 ; Example 4: KOH-C-1/[SCA-2H][OOCR] 0.2 ; Example 5: KOH-C-1/[TEPAH][IDA] 0.5 .

具体实施方式Detailed ways

在具体实施工艺方面,本发明重点考察了以下因素对酒糟多孔炭的制备 及吸附性能的影响。首先,考察活化剂用量对酒糟基多孔炭的影响,当KOH 用量较少(<1g)时酒糟基多孔炭中超微孔(<1nm)数量大,尤其是0.45~0.65 nm范围内的微孔结构分布较多,对应的常压下CO2吸附容量增大;反之, KOH用量(>1g)增大,多孔炭比表面积显著增大,中介孔及大孔数量增多, 而对应的常压下CO2吸附容量减小。然后,考察了活化剂种类对酒糟基多孔 炭的影响,当在采用相同用量(0.5g)、不同活化剂条件下制备酒糟基多孔炭 时,多孔炭都具有大量微孔结构,但比表面积较低,相比而言,KOH的活化 效果具有显著优势,比表面积达到1059m2/g,对应的常压下CO2吸附容量最 大;最后,考察了二次活化温度对酒糟基多孔炭的影响,主要采用600-800℃ 进行因素考察,随温度升高,比表面积增大,但微孔数量先增大后减小,当 活化温度为700℃时,酒糟基多孔炭具有最大的微孔(<1nm)数量,对应的常压下CO2吸附容量最大。In terms of specific implementation process, the present invention focuses on the influence of the following factors on the preparation and adsorption performance of distiller's grain porous carbon. First, the effect of the amount of activator on the distiller's grain-based porous carbon was investigated. When the amount of KOH was small (<1g), the number of ultra-micropores (<1nm) in the distiller's grain-based porous carbon was large, especially the micropore structure in the range of 0.45-0.65 nm more distribution, the corresponding CO 2 adsorption capacity under normal pressure increases; on the contrary, with the increase of KOH dosage (>1g), the specific surface area of porous carbon increases significantly, the number of mesopores and macropores increases, and the corresponding CO2 under normal pressure 2 The adsorption capacity is reduced. Then, the effect of the type of activator on distiller's grain-based porous carbon was investigated. When using the same amount (0.5g) and different activators to prepare distiller's grain-based porous carbon, the porous carbon has a large number of microporous structures, but the specific surface area is relatively small. In contrast, the activation effect of KOH has a significant advantage, the specific surface area reaches 1059m 2 /g, and the corresponding CO 2 adsorption capacity is the largest under normal pressure; finally, the influence of the secondary activation temperature on the distiller's grain-based porous carbon was investigated, Mainly use 600-800°C for factor investigation. As the temperature rises, the specific surface area increases, but the number of micropores first increases and then decreases. When the activation temperature is 700°C, distiller's grain-based porous carbon has the largest micropores (< 1nm) quantity, corresponding to the largest CO 2 adsorption capacity under normal pressure.

实施例1Example 1

一种酱香酒酒糟基多孔炭气体吸附剂的制备方法。将干燥后的酒糟在2 mol·L-1的氢氟酸溶液中搅拌预处理24h,经去离子水洗涤,105℃烘干,粉 碎至50~200目,然后在氮气流量100ml·min-1维持的惰性气氛下,以5℃·min-1升温至500℃预碳化2h得到多孔炭前体;将多孔炭前体与KOH活化剂按质 量比1:0.5经机械球磨10min,然后在氮气流量50ml·min-1维持的惰性气氛 下,以5℃·min-1升温至700℃二次碳化2h,经0.1mol·L-1的盐酸洗涤,再 经去离子水洗至中性,过滤,105℃烘干,得到酱香酒酒糟基多孔炭气体吸 附剂(KOH-C-0.5)。A preparation method of Maotai-flavored wine lees-based porous carbon gas adsorbent. Stir and pretreat the dried distiller's grains in 2 mol·L -1 hydrofluoric acid solution for 24 hours, wash with deionized water, dry at 105°C, pulverize to 50-200 mesh, and then dissolve the distiller's grains in a nitrogen flow rate of 100ml·min -1 Under the maintained inert atmosphere, pre-carbonize the porous carbon precursor at 5°C·min -1 to 500°C for 2h; the porous carbon precursor and the KOH activator are mechanically ball milled for 10min at a mass ratio of 1:0.5, and then Under an inert atmosphere maintained at 50ml·min -1 , heat up to 700℃ at 5°C·min -1 for secondary carbonization for 2h, wash with 0.1mol·L -1 hydrochloric acid, then wash with deionized water until neutral, filter, 105 °C drying to obtain Maotai-flavored wine lees-based porous carbon gas adsorbent (KOH-C-0.5).

对多孔炭气体吸附剂的微观形貌进行表征,由SEM图1a可知,多孔炭 表面形成了不规则孔洞,由TEM图2进一步分析可知,吸附剂中形成了大量 的类似于虫孔的微孔隙结构,且随机分布在碳骨架中。同时,对多孔炭气体 吸附剂进行比表面积和孔结构表征,结果如图3所示。其中,图3a为氮气吸 附脱附等温线,根据IUPAC对吸附等温线的分类可知,曲线属于Ⅰ型,在较 低相对压力下(P/P0<0.1),N2具有较大吸附量,并在拐点后较宽相对压力范围内(0.1<P/P0<1.0)保持相对水平,说明吸附剂具有大量微孔结构,从图3b 孔径分布曲线也可以看出,吸附剂孔径主要分布在0.45~1nm。通过分析可知, 制得的酱香酒酒糟基吸附剂比表面积为1059m2/g,总孔容0.57cm3/g,微孔 孔容0.50cm3/g。Characterize the microscopic morphology of the porous carbon gas adsorbent. It can be seen from SEM Figure 1a that irregular pores are formed on the surface of porous carbon. Further analysis from TEM Figure 2 shows that a large number of micropores similar to wormholes are formed in the adsorbent. structure, and are randomly distributed in the carbon skeleton. At the same time, the specific surface area and pore structure of the porous carbon gas adsorbent were characterized, and the results are shown in Figure 3. Among them, Fig. 3a is the nitrogen adsorption-desorption isotherm. According to the classification of adsorption isotherms by IUPAC, the curve belongs to type I. At lower relative pressure (P/P 0 <0.1), N2 has a larger adsorption capacity, And after the inflection point, it maintains a relative level in a wide relative pressure range (0.1<P/P 0 <1.0), indicating that the adsorbent has a large number of microporous structures. It can also be seen from the pore size distribution curve in Figure 3b that the pore size of the adsorbent is mainly distributed in the 0.45 ~ 1nm. It can be seen from the analysis that the prepared Maotai-flavored wine lees-based adsorbent has a specific surface area of 1059 m 2 /g, a total pore volume of 0.57 cm 3 /g, and a micropore volume of 0.50 cm 3 /g.

采用BSD-PM2物理吸附仪测试吸附剂的CO2、CH4、N2气体吸附性能, 吸附曲线如图6所示,在相同条件下,吸附容量根据气体不同而具有较大区 别,顺序为CO2>CH4>N2。在273.15K、1bar条件下,CO2吸附容量为6.34 mmol/g,通过IAST竞争吸附计算得到CO2选择性分别为24.1%(1bar, CO2:N2=15%:85%),5.6%(1bar,CO2:CH4=40%:60%)。BSD-PM2 physical adsorption instrument was used to test the CO 2 , CH 4 , and N 2 gas adsorption properties of the adsorbent. The adsorption curves are shown in Figure 6. Under the same conditions, the adsorption capacity varies greatly depending on the gas, and the order is CO 2 >CH 4 >N 2 . Under the conditions of 273.15K and 1 bar, the CO 2 adsorption capacity is 6.34 mmol/g, and the CO 2 selectivity calculated by IAST competitive adsorption is 24.1% (1 bar, CO 2 :N 2 =15%:85%), 5.6% (1 bar, CO 2 :CH 4 =40%:60%).

实施例2Example 2

一种酱香酒酒糟基多孔炭气体吸附剂的制备方法。将干燥后的酒糟在2 mol·L-1的氢氟酸溶液中搅拌预处理24h,经去离子水洗涤,105℃烘干,粉 碎至50~200目,然后在氮气流量100ml·min-1维持的惰性气氛下,以5℃·min-1升温至500℃预碳化2h得到多孔炭前体;将多孔炭前体与KOH活化剂按质 量比1:1经机械球磨15min,然后在氮气流量100ml·min-1维持的惰性气氛下, 以5℃·min-1升温至700℃二次碳化2h,经0.1mol·L-1的盐酸洗涤,再经去 离子水洗至中性,过滤,105℃烘干,得到酱香酒酒糟基多孔炭吸附剂 (KOH-C-1)。A preparation method of Maotai-flavored wine lees-based porous carbon gas adsorbent. Stir and pretreat the dried distiller's grains in 2 mol·L -1 hydrofluoric acid solution for 24 hours, wash with deionized water, dry at 105°C, pulverize to 50-200 mesh, and then dissolve the distiller's grains in a nitrogen flow rate of 100ml·min -1 Under the maintained inert atmosphere, pre-carbonize the porous carbon precursor at 5°C·min -1 to 500°C for 2h to obtain the porous carbon precursor; the porous carbon precursor and the KOH activator are mechanically ball milled for 15min at a mass ratio of 1:1, and then Under an inert atmosphere maintained at 100ml·min -1 , heat up to 700°C at 5°C·min -1 for secondary carbonization for 2h, wash with 0.1mol·L -1 hydrochloric acid, then wash with deionized water until neutral, filter, 105 °C to obtain Maotai-flavored wine lees-based porous carbon adsorbent (KOH-C-1).

对多孔炭气体吸附剂的微观形貌进行表征,由SEM图1b可知,吸附剂 中形成了大量孔洞结构.对多孔炭气体吸附剂的孔结构进行表征,通过分析可 知,气体吸附剂孔径主要分布在0.45~3.5nm,比表面积为2079m2/g,总孔容 1.14cm3·g-1,微孔孔容0.94cm3·g-1Characterize the microscopic morphology of the porous carbon gas adsorbent. It can be seen from SEM Figure 1b that a large number of pore structures are formed in the adsorbent. The pore structure of the porous carbon gas adsorbent is characterized by analysis. It can be known that the pore size of the gas adsorbent mainly distributes At 0.45-3.5nm, the specific surface area is 2079m 2 /g, the total pore volume is 1.14cm 3 ·g -1 , and the micropore volume is 0.94cm 3 ·g -1 .

采用BSD-PM2物理吸附仪测试吸附剂的H2S、SO2、CO2气体吸附性能, 吸附曲线如图7所示。由图可知,在273.15K、1bar条件下,H2S吸附容量 为6.68mmol·g-1,SO2吸附容量为9.52mmol·g-1,CO2吸附容量为5.96mmol·g-1BSD-PM2 physical adsorption instrument was used to test the adsorption performance of H 2 S, SO 2 , CO 2 gas of the adsorbent, and the adsorption curve is shown in Fig. 7 . It can be seen from the figure that under the conditions of 273.15K and 1 bar, the adsorption capacity of H 2 S is 6.68mmol·g -1 , that of SO 2 is 9.52mmol·g -1 , and that of CO 2 is 5.96mmol·g -1 .

实施例3Example 3

一种酱香酒酒糟基多孔炭复合离子液体气体吸附剂的制备方法。将干燥 后的酒糟在2mol·L-1的氢氟酸溶液中搅拌预处理24h,经去离子水洗涤,105℃ 烘干,粉碎至50~200目,然后在氮气流量100ml·min-1维持的惰性气氛下, 以5℃·min-1升温至500℃预碳化2h得到多孔炭前体;将多孔炭前体与KOH 活化剂按质量比1:1经机械球磨15min,然后在氮气流量100ml·min-1维持的 惰性气氛下,以5℃·min-1升温至700℃二次碳化2h,经0.1mol·L-1的盐酸 洗涤,再经去离子水洗至中性,过滤,105℃烘干,得到酱香酒酒糟基多孔 炭吸附剂(KOH-C-1)。同时,将有机胺和羧酸按摩尔比1:2在乙醇中反应, 反应结束后去除乙醇,离子液体经己烷洗涤去除未反应的胺或酸,真空干燥 后得到羧酸盐质子型离子液体。例如:[TEPAH][IDA]羧酸盐质子型离子液体 合成路线如图4所示。然后,将酒糟基多孔炭与[TEPAH][IDA]羧酸盐质子型 离子液体按质量比1:0.2加入丙酮中充分搅拌浸渍,过滤、干燥后即得酒糟基 多孔炭复合离子液体气体吸附剂(KOH-C-1/[TEPAH][IDA]0.2)。A preparation method of Maotai-flavored wine lees-based porous carbon composite ionic liquid gas adsorbent. Stir and pretreat the dried distiller's grains in a 2mol·L -1 hydrofluoric acid solution for 24 hours, wash with deionized water, dry at 105°C, pulverize to 50-200 mesh, and then maintain under nitrogen flow of 100ml·min -1 Under an inert atmosphere, the porous carbon precursor was pre-carbonized at 5°C·min -1 to 500°C for 2 hours; the porous carbon precursor and the KOH activator were mechanically ball milled for 15 minutes at a mass ratio of 1:1, and then Under an inert atmosphere maintained at min -1 , heat up to 700°C at 5°C min -1 for secondary carbonization for 2 hours, wash with 0.1mol·L -1 hydrochloric acid, then wash with deionized water until neutral, filter, 105°C Dried to obtain Maotai-flavored wine lees-based porous carbon adsorbent (KOH-C-1). At the same time, the organic amine and carboxylic acid are reacted in ethanol at a molar ratio of 1:2, and the ethanol is removed after the reaction. The ionic liquid is washed with hexane to remove unreacted amine or acid, and the carboxylate proton ionic liquid is obtained after vacuum drying. . For example: [TEPAH] [IDA] carboxylate proton type ionic liquid synthesis route is shown in Figure 4. Then, add distiller's grain-based porous carbon and [TEPAH][IDA] carboxylate proton-type ionic liquid into acetone at a mass ratio of 1:0.2, stir and impregnate fully, filter and dry to obtain distiller's grain-based porous carbon composite ionic liquid gas adsorbent (KOH-C-1/[TEPAH][IDA] 0.2 ).

实施例4Example 4

一种酱香酒酒糟基多孔炭复合离子液体气体吸附剂的制备方法。将干燥 后的酒糟在2mol·L-1的氢氟酸溶液中搅拌预处理24h,经去离子水洗涤,105℃ 烘干,粉碎至50~200目,然后在氮气流量100ml·min-1维持的惰性气氛下, 以5℃·min-1升温至500℃预碳化2h得到多孔炭前体;将多孔炭前体与KOH 活化剂按质量比1:1经机械球磨15min,然后在氮气流量100ml·min-1维持的 惰性气氛下,以5℃·min-1升温至700℃二次碳化2h,经0.1mol·L-1的盐酸 洗涤,再经去离子水洗至中性,过滤,105℃烘干,得到酱香酒酒糟基多孔 炭吸附剂(KOH-C-1)。同时,通过酸碱中和反应,将有机胺和羧酸按摩尔比1:2混合,合成多种具有特征结构的伯胺类、叔胺类、硅烷偶联剂类、含羟基 或醚键类羧酸盐质子型离子液体。然后,将酒糟基多孔炭与离子液体按质量 比1:0.2加入甲苯中回流,通过化学嫁接法制得酒糟基多孔炭复合离子液体气 体吸附剂。例如:酒糟基多孔炭化学嫁接[SCA-2H][OOCR]羧酸盐质子型离子 液体改性,KOH-C-1/[SCA-2H][OOCR]0.2合成路线如图5所示。A preparation method of Maotai-flavored wine lees-based porous carbon composite ionic liquid gas adsorbent. Stir and pretreat the dried distiller's grains in a 2mol·L -1 hydrofluoric acid solution for 24 hours, wash with deionized water, dry at 105°C, pulverize to 50-200 mesh, and then maintain under nitrogen flow of 100ml·min -1 Under an inert atmosphere, the porous carbon precursor was pre-carbonized at 5°C·min -1 to 500°C for 2 hours; the porous carbon precursor and the KOH activator were mechanically ball milled for 15 minutes at a mass ratio of 1:1, and then Under an inert atmosphere maintained at min -1 , heat up to 700°C at 5°C min -1 for secondary carbonization for 2 hours, wash with 0.1mol·L -1 hydrochloric acid, then wash with deionized water until neutral, filter, 105°C Dried to obtain Maotai-flavored wine lees-based porous carbon adsorbent (KOH-C-1). At the same time, through acid-base neutralization reaction, organic amine and carboxylic acid are mixed at a molar ratio of 1:2 to synthesize a variety of primary amines, tertiary amines, silane coupling agents, hydroxyl or ether bond-containing products with characteristic structures Carboxylate protic ionic liquid. Then, distiller's grain-based porous carbon and ionic liquid were added into toluene at a mass ratio of 1:0.2 to reflux, and the distiller's grain-based porous carbon composite ionic liquid gas adsorbent was prepared by chemical grafting. For example: chemical grafting of [SCA-2H][OOCR] carboxylate proton type ionic liquid on vinasse-based porous carbon, the synthesis route of KOH-C-1/[SCA-2H][OOCR] 0.2 is shown in Figure 5.

实施例5Example 5

一种酱香酒酒糟基多孔炭复合离子液体气体吸附剂的制备方法。将干燥 后的酒糟在2mol·L-1的氢氟酸溶液中搅拌预处理24h,经去离子水洗涤,105℃ 烘干,粉碎至50~200目,然后在氮气流量100ml·min-1维持的惰性气氛下, 以5℃·min-1升温至500℃预碳化2h得到多孔炭前体;将多孔炭前体与KOH 活化剂按质量比1:1经机械球磨15min,然后在氮气流量100ml·min-1维持的 惰性气氛下,以5℃·min-1升温至700℃二次碳化2h,经0.1mol·L-1的盐酸 洗涤,再经去离子水洗至中性,过滤,105℃烘干,得到酱香酒酒糟基多孔 炭吸附剂(KOH-C-1)。同时,将有机胺和羧酸按摩尔比1:2在乙醇中反应, 反应结束后去除乙醇,离子液体经己烷洗涤去除未反应的胺或酸,真空干燥 后得到羧酸盐质子型离子液体。然后,将酒糟基多孔炭与[TEPAH][IDA]羧酸 盐质子型离子液体按质量比1:0.5加入丙酮中充分搅拌浸渍,过滤、干燥后即 得酒糟基多孔炭复合离子液体气体吸附剂(KOH-C-1/[TEPAH][IDA]0.5)。A preparation method of Maotai-flavored wine lees-based porous carbon composite ionic liquid gas adsorbent. Stir and pretreat the dried distiller's grains in a 2mol·L -1 hydrofluoric acid solution for 24 hours, wash with deionized water, dry at 105°C, pulverize to 50-200 mesh, and then maintain under nitrogen flow of 100ml·min -1 Under an inert atmosphere, the porous carbon precursor was pre-carbonized at 5°C·min -1 to 500°C for 2 hours; the porous carbon precursor and the KOH activator were mechanically ball milled for 15 minutes at a mass ratio of 1:1, and then Under an inert atmosphere maintained at min -1 , heat up to 700°C at 5°C min -1 for secondary carbonization for 2 hours, wash with 0.1mol·L -1 hydrochloric acid, then wash with deionized water until neutral, filter, 105°C Dried to obtain Maotai-flavored wine lees-based porous carbon adsorbent (KOH-C-1). At the same time, the organic amine and carboxylic acid are reacted in ethanol at a molar ratio of 1:2, and the ethanol is removed after the reaction. The ionic liquid is washed with hexane to remove unreacted amine or acid, and the carboxylate proton ionic liquid is obtained after vacuum drying. . Then, add distiller's grain-based porous carbon and [TEPAH][IDA] carboxylate proton-type ionic liquid into acetone at a mass ratio of 1:0.5, stir and impregnate fully, filter and dry to obtain distiller's grain-based porous carbon composite ionic liquid gas adsorbent (KOH-C-1/[TEPAH][IDA] 0.5 ).

实施例6Example 6

采用BSD-PM2物理吸附仪测试实施例2、实施例3、实施例4和实施例 5制得气体吸附剂的CO2吸附性能,吸附曲线如图8所示。由图可知,在273.15 K、1bar条件下,KOH-C-1吸附容量为5.96mmol·g-1, KOH-C-1/[TEPAH][IDA]0.2吸附容量为8.85mmol·g-1,KOH-C-1/[SCA-2H][OOCR]0.2吸附容量为7.79mmol·g-1,提高离子液体的固 载量后,KOH-C-1/[TEPAH][IDA]0.5吸附容量高达10.7mmol·g-1The CO2 adsorption performance of the gas adsorbent prepared in Example 2, Example 3, Example 4 and Example 5 was tested by BSD-PM2 physical adsorption instrument, and the adsorption curve is shown in Figure 8. It can be seen from the figure that under the conditions of 273.15 K and 1 bar, the adsorption capacity of KOH-C-1 is 5.96 mmol·g -1 , the adsorption capacity of KOH-C-1/[TEPAH][IDA] 0.2 is 8.85 mmol·g -1 , The adsorption capacity of KOH-C-1/[SCA-2H][OOCR] 0.2 is 7.79mmol ·g -1 . 10.7 mmol·g -1 .

本发明方法以固废资源化利用为出发点,以白酒酿造大宗固废——酱香 酒酒糟为原料,经氢氟酸除杂预处理、高温碳化、二次活化获得比重轻、微 孔结构发达、比表面积高达3657.6m2·g-1的酒糟基多孔炭,常压下,CO2吸 附容量6.34mmol·g-1,H2S吸附容量6.68mmol·g-1,SO2吸附容量9.52mmol·g-1。 同时,创新性地以质子型离子液体对多孔炭进行改性,创制热稳定性更高的 酱香酒酒糟基多孔炭复合离子液体气体吸附剂,进而提高酒糟基多孔炭对低 浓度气体的吸附容量和分离选择性。本发明所制备的酱香酒酒糟基多孔炭复 合离子液体气体吸附剂,在CO2的选择性吸附分离应用中表现出优异的吸附 分离性能,常压下,CO2吸附容量提升至10.7mmol·g-1。由于所制备的多孔 炭复合离子液体气体吸附剂因具有超高的比表面积、丰富的孔结构性质和丰 富的活性位点,制备方法简单、易操作、成本低等优点(约为木屑类商业活性 炭成本的87%),使其在天然气、沼气、低浓度煤层气及燃煤烟气等气体吸附 分离领域表现出较好的工业应用前景。The method of the present invention starts from the utilization of solid waste as a resource, and uses Maotai-flavored wine distiller's grains as a large solid waste from liquor brewing as a raw material, and undergoes impurity removal pretreatment with hydrofluoric acid, high-temperature carbonization, and secondary activation to obtain light specific gravity and developed microporous structure Distiller's grains-based porous carbon with a specific surface area of 3657.6m 2 ·g -1 , under normal pressure, the adsorption capacity of CO 2 is 6.34mmol·g -1 , the adsorption capacity of H 2 S is 6.68mmol·g -1 , and the adsorption capacity of SO 2 is 9.52mmol • g −1 . At the same time, the porous carbon is innovatively modified with proton-type ionic liquids to create a more thermally stable Maotai-flavor wine distiller's grain-based porous carbon composite ionic liquid gas adsorbent, thereby improving the adsorption of distiller's grain-based porous carbon to low-concentration gases capacity and separation selectivity. The Maotai-flavored wine lees-based porous carbon composite ionic liquid gas adsorbent prepared by the present invention exhibits excellent adsorption and separation performance in the selective adsorption and separation of CO2 , and the CO2 adsorption capacity is increased to 10.7mmol· g -1 . Because the prepared porous carbon composite ionic liquid gas adsorbent has the advantages of super high specific surface area, rich pore structure properties and abundant active sites, the preparation method is simple, easy to operate, and low cost (approximately wood chips commercial activated carbon 87% of the cost), making it show a good industrial application prospect in the fields of gas adsorption and separation of natural gas, biogas, low-concentration coal bed methane and coal-fired flue gas.

Claims (8)

1. A preparation method of a sauce-flavor wine vinasse-based porous carbon composite ionic liquid gas adsorbent is characterized by comprising the following steps of:
(1) 0.1-0.5 mol/L of sauce-flavor wine vinasse is firstly used -1 Removing impurities with hydrofluoric acid for 0.5-2 h, washing with deionized water, filtering, drying, pulverizing to 50-200 meshes, and introducing nitrogen at 100-200 ml/min -1 Under the nitrogen atmosphere at 5-10 ℃ for min -1 Heating to 500 ℃ for pre-carbonization for 1-3 h to obtain a porous carbon precursor;
(2) The porous carbon precursor and the activating agent are mechanically ball-milled and mixed according to a specific mass ratio, and then the flow is 50-100 ml.min -1 Under the nitrogen atmosphere at 5-10 ℃ for min -1 The temperature is raised to 600 to 800 ℃ at the temperature raising speed, secondary carbonization treatment is carried out for 1 to 3 hours, and then the secondary carbonization treatment is carried out for 0.1 to 0.5 mol.L -1 Washing the mixture with hydrochloric acid and deionized water to be neutral, filtering and drying to obtain the sauce-flavor wine vinasse-based porous carbon;
(3) The sauce-flavored wine vinasse-based porous carbon is compounded with ionic liquid according to specific mass, and then the sauce-flavored wine vinasse-based porous carbon composite ionic liquid gas adsorbent is obtained.
2. The preparation method of the sauce-flavored wine lees-based porous carbon composite ionic liquid gas adsorbent according to claim 1, wherein the main components of the sauce-flavored wine lees include, but are not limited to, fermented sorghum, rice hulls, wheat and corn.
3. The preparation method of the ionic liquid gas adsorbent compounded by the sauce-flavored wine lees-based porous carbon as claimed in claim 1, wherein the mass ratio of the porous carbon precursor to the activating agent is 1.
4. The preparation method of the Maotai-flavor wine vinasse-based porous carbon composite ionic liquid gas adsorbent according to claim 1 or 3, wherein the activating agent comprises but is not limited to KOH and K 2 CO 3 、KHCO 3 、K 3 PO 4 、NaOH、H 3 PO 4 、ZnCl 2 And NaNH 2
5. The preparation method of the sauce-flavored wine lees-based porous carbon composite ionic liquid gas adsorbent according to claim 1, wherein the mass ratio of the sauce-flavored wine lees-based porous carbon to the ionic liquid is 1.
6. The preparation method of the ionic liquid gas adsorbent compounded from the Maotai-flavor wine lees-based porous carbon according to claim 1 or 5, wherein the ionic liquid is carboxylate proton type ionic liquid.
7. The preparation method of the Maotai-flavor wine lees-based porous carbon composite ionic liquid gas adsorbent according to claim 6, wherein the organic amine structure required by the synthesis of the carboxylate proton type ionic liquid comprises but is not limited to ethylenediamine, diethylenetriamine, tetraethylenepentamine, polyethyleneimine, N- [3- (trimethoxysilyl) propyl ] ethylenediamine, 3-aminopropyltrimethoxysilane, tris (2-dimethylaminoethyl) amine, triethanolamine, tris (3, 6-dioxaheptyl) amine.
8. The preparation method of the Maotai-flavor wine vinasse-based porous carbon composite ionic liquid gas adsorbent according to claim 6, wherein the polycarboxylic acid structure required by the synthesis of the carboxylate proton type ionic liquid comprises but is not limited to iminodiacetic acid, ethylenediamine-N, N' -diacetic acid, nitrilotriacetic acid, 1,2,3, 4-butanetetracarboxylic acid and benzimidazole-5-carboxylic acid.
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Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN116395669A (en) * 2023-04-20 2023-07-07 宜宾五粮液股份有限公司 Distilled grain biological charcoal and application thereof

Citations (11)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101993378A (en) * 2010-09-10 2011-03-30 中国石油大学(北京) Amido-containing ionic liquid used for absorbing acidic gases and preparation method and application thereof
CN103949216A (en) * 2014-05-13 2014-07-30 农业部环境保护科研监测所 Preparation method of carbon material for adsorbing hydrophilic ionic liquid
CN107651651A (en) * 2017-09-29 2018-02-02 浙江工业大学 A kind of porosu solid supported ion liquid of absorption HCl gases
WO2018099173A1 (en) * 2016-12-02 2018-06-07 建添企业有限公司 Method for preparing nitrogen-doped porous carbon material by using coal as raw material
CN109550484A (en) * 2018-11-20 2019-04-02 浙江海洋大学 A kind of preparation method of instruction plant stem foot chromium ion adsorbent
CN109734089A (en) * 2019-03-15 2019-05-10 浙江理工大学 A kind of preparation method of high specific surface area distiller's grains activated carbon
CN109928391A (en) * 2019-04-02 2019-06-25 四川轻化工大学 Modified distiller's grain-based activated carbon and preparation method thereof
CN110841606A (en) * 2019-11-21 2020-02-28 浙江大学 A composite material for capturing carbon dioxide and its preparation method and application
CN113070040A (en) * 2021-04-22 2021-07-06 浙江工业大学 Carbon material-loaded ionic liquid adsorption material for removing carbonyl sulfide and application thereof
CN113546609A (en) * 2020-04-26 2021-10-26 国家能源投资集团有限责任公司 Preparation method and application of adsorption material
CN113856627A (en) * 2021-11-01 2021-12-31 贵州大学 Preparation method and application of vinasse-based biochar for deep dechromization of wet-process phosphoric acid

Patent Citations (11)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101993378A (en) * 2010-09-10 2011-03-30 中国石油大学(北京) Amido-containing ionic liquid used for absorbing acidic gases and preparation method and application thereof
CN103949216A (en) * 2014-05-13 2014-07-30 农业部环境保护科研监测所 Preparation method of carbon material for adsorbing hydrophilic ionic liquid
WO2018099173A1 (en) * 2016-12-02 2018-06-07 建添企业有限公司 Method for preparing nitrogen-doped porous carbon material by using coal as raw material
CN107651651A (en) * 2017-09-29 2018-02-02 浙江工业大学 A kind of porosu solid supported ion liquid of absorption HCl gases
CN109550484A (en) * 2018-11-20 2019-04-02 浙江海洋大学 A kind of preparation method of instruction plant stem foot chromium ion adsorbent
CN109734089A (en) * 2019-03-15 2019-05-10 浙江理工大学 A kind of preparation method of high specific surface area distiller's grains activated carbon
CN109928391A (en) * 2019-04-02 2019-06-25 四川轻化工大学 Modified distiller's grain-based activated carbon and preparation method thereof
CN110841606A (en) * 2019-11-21 2020-02-28 浙江大学 A composite material for capturing carbon dioxide and its preparation method and application
CN113546609A (en) * 2020-04-26 2021-10-26 国家能源投资集团有限责任公司 Preparation method and application of adsorption material
CN113070040A (en) * 2021-04-22 2021-07-06 浙江工业大学 Carbon material-loaded ionic liquid adsorption material for removing carbonyl sulfide and application thereof
CN113856627A (en) * 2021-11-01 2021-12-31 贵州大学 Preparation method and application of vinasse-based biochar for deep dechromization of wet-process phosphoric acid

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN116395669A (en) * 2023-04-20 2023-07-07 宜宾五粮液股份有限公司 Distilled grain biological charcoal and application thereof

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