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CN117463292A - An activated carbon fiber-based MOFs bulk hygroscopic agent and its mixed solvent thermal in-situ synthesis method and application - Google Patents

An activated carbon fiber-based MOFs bulk hygroscopic agent and its mixed solvent thermal in-situ synthesis method and application Download PDF

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CN117463292A
CN117463292A CN202310954153.9A CN202310954153A CN117463292A CN 117463292 A CN117463292 A CN 117463292A CN 202310954153 A CN202310954153 A CN 202310954153A CN 117463292 A CN117463292 A CN 117463292A
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方玉堂
黎敏
梁向晖
汪双凤
高学农
张正国
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South China University of Technology SCUT
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Abstract

本发明公开了一种活性碳纤维基MOFs块体吸湿剂及其混合溶剂热原位合成方法和应用。该方法包括以下步骤:将活化的活性碳纤维浸入到含亲水改性成膜材料的水溶液中得亲水改性活性碳纤维;将有机二元羧酸的DMF溶液和铝盐水溶液混合得均匀反应液;将改性活性碳纤维浸没在反应液中反应,取出负载MOFs涂层的活性碳纤维,洗涤、干燥活化得MOFs块体吸湿剂。本发明制备的活性碳纤维基MOFs块体吸湿剂,MOFs晶粒与基材结合紧密、不掉粉;MOFs负载率高;MOFs块体吸湿剂具有低湿度(30%RH)下水蒸气吸附量高、解吸温度低和循环稳定好以及光热转换能力强等特征,可应用于干旱地区太阳能辅助驱动的大气集水领域。

The invention discloses an activated carbon fiber-based MOFs bulk hygroscopic agent and its mixed solvent thermal in-situ synthesis method and application. The method includes the following steps: immersing activated activated carbon fiber into an aqueous solution containing hydrophilic modified film-forming material to obtain hydrophilic modified activated carbon fiber; mixing a DMF solution of organic dicarboxylic acid and an aluminum aqueous solution to obtain a uniform reaction solution ; Immerse the modified activated carbon fiber in the reaction solution, take out the activated carbon fiber loaded with MOFs coating, wash, dry and activate it to obtain a MOFs bulk hygroscopic agent. The activated carbon fiber-based MOFs bulk hygroscopic agent prepared by the invention has a tight combination of MOFs crystal grains and the base material and does not lose powder; the MOFs loading rate is high; the MOFs bulk hygroscopic agent has a high water vapor adsorption capacity under low humidity (30% RH), It has the characteristics of low desorption temperature, good cycle stability, and strong photothermal conversion ability, and can be applied to the field of solar-assisted atmospheric water collection in arid areas.

Description

一种活性碳纤维基MOFs块体吸湿剂及其混合溶剂热原位合成 方法和应用Thermal in-situ synthesis of an activated carbon fiber-based MOFs bulk hygroscopic agent and its mixed solvent Methods and applications

技术领域Technical field

本发明涉及大气集水领域,具体涉及一种活性碳纤维基MOFs块体吸湿剂及其混合溶剂热原位合成方法和应用。The invention relates to the field of atmospheric water collection, and specifically relates to an activated carbon fiber-based MOFs bulk hygroscopic agent and its mixed solvent thermal in-situ synthesis method and application.

背景技术Background technique

尽管目前开发了各种水净化技术如过滤、反渗透、多级闪蒸等来利用海水或废水,但由于对天然水源的依赖,这些水净化技术仅适用于沿海地区,而内陆地区通常无法获得。据报道,大气中约有12900km3的水以蒸汽或液滴形式存在,如果将其利用起来,将可以有效缓解全球水资源短缺压力。虽然在潮湿的气候中通过雾收集或通过将空气冷却到露点以下进行冷凝很容易实现直接提取,但在干旱环境中不可取。因此,在干旱地区建立大气集水(AWH)成为一种有前景的分散式生产水的策略。Although various water purification technologies such as filtration, reverse osmosis, multi-stage flash evaporation, etc. have been developed to utilize seawater or wastewater, these water purification technologies are only applicable to coastal areas due to their dependence on natural water sources, and are generally not available in inland areas. get. According to reports, about 12,900km3 of water exists in the form of steam or liquid droplets in the atmosphere. If it is utilized, it will effectively alleviate the pressure of global water shortages. While direct extraction is easily achieved in humid climates by fog collection or by condensation by cooling the air below the dew point, it is not advisable in arid environments. Therefore, establishing atmospheric water harvesting (AWH) in arid regions becomes a promising strategy for decentralized water production.

与传统水蒸气吸附剂如硅胶、分子筛相比,具有大量均匀微孔的金属有机框架(MOF)由于其丰富的化学可变性和可调性而被确定为有前途的下一代新型水蒸气吸附剂。MOF能在较宽的相对湿度(RH)范围内展现出优异的水蒸气捕获能力和水热稳定性,其再生能耗也较低。与传统粉体吸附剂一样,粉末状MOF存在传质传热效率低的问题,若将MOF晶粒均匀负载在基材上制备所谓的块体吸附剂(Monolithic adsorbent)是提高其传质传热效率的关键;并且可通过调整涂层厚度(MOF负载率)来调节块体吸附剂的吸湿量。此外,为了节约运行能耗,特别是脱附能耗,选用太阳能驱动吸附剂解吸水是大气集水的重要策略。目前块体吸附剂的基材主要有无机纤维纸如石棉纤维纸、玻璃纤维纸、陶瓷纤维纸等;无机陶瓷多孔材料如海泡石、堇青石等;以及金属基薄片如铝箔、铜箔等。无机纤维纸孔隙率高,但脆性大,加工困难或需要加入无机胶定型从而降低了吸附剂的负载率;无机陶瓷多孔材料密度大,孔隙率低,吸附剂负载率相当低;金属基薄片与吸附剂作用力弱,且表面积小,吸附剂负载率低;并且,除金属箔外,它们导热率低,光热转化效率低。另一方面,大多数MOFs是白色或浅色的粉体,光吸收能力差,光热转化性能低,因此需要强化其光热性能。通常所采用的方法是添加光热剂以实现光热强化。目前所报道的光热剂有四类,分别是贵金属纳米颗粒、金属半导体纳米颗粒、碳基纳米材料以及聚合物等。其中常用的是金属半导体纳米颗粒和碳基纳米材料。但是这些光热剂的添加会一定程度降低MOF吸湿量(包括MOF负载率降低或部分堵塞MOF微孔孔隙)。因此,选择一个具有高的比表面积(孔隙率)、高导热率及高光热转化性能的基材作为吸附剂的载体,以提高MOF吸附剂负载率的同时,在太阳能的辅助下通过光热转化实现吸附剂快速脱水,从而降低吸附剂的脱附能耗是合理的设计策略。此外,如何均匀分散高负载率的MOF晶粒在基材中与MOF负载化工艺紧密相关。通常有两种方法来负载MOF,即直接浸涂法和原位合成法。浸涂法需要在外添加粘合剂的作用下将吸附剂粘附在基材上,常用的粘合剂有硅酸钠溶液、硅溶液和有机聚硅氧烷树脂等。该方法粘合剂易堵塞MOF吸附剂的孔隙,从而影响吸附效果。而原位合成法是让MOF在基材上原位生长,通过该方法可获得不同厚度、致密和均匀的吸附涂层,具有一步合成的简便性和优良的传热传质性能。Compared with traditional water vapor adsorbents such as silica gel and molecular sieves, metal-organic frameworks (MOFs) with large amounts of uniform micropores have been identified as promising next-generation new water vapor adsorbents due to their rich chemical variability and tunability. . MOF can exhibit excellent water vapor capture capability and hydrothermal stability over a wide relative humidity (RH) range, and its regeneration energy consumption is also low. Like traditional powder adsorbents, powdered MOF has the problem of low mass and heat transfer efficiency. If the MOF grains are uniformly loaded on the substrate to prepare a so-called monolithic adsorbent, its mass and heat transfer can be improved. The key to efficiency; and the moisture absorption of the bulk adsorbent can be adjusted by adjusting the coating thickness (MOF loading rate). In addition, in order to save operating energy consumption, especially desorption energy consumption, the use of solar-driven adsorbents to desorb water is an important strategy for atmospheric water collection. At present, the base materials of bulk adsorbents mainly include inorganic fiber paper such as asbestos fiber paper, glass fiber paper, ceramic fiber paper, etc.; inorganic ceramic porous materials such as sepiolite, cordierite, etc.; and metal-based sheets such as aluminum foil, copper foil, etc. . Inorganic fiber paper has high porosity, but is brittle and difficult to process or requires the addition of inorganic glue for shaping, which reduces the adsorbent loading rate; inorganic ceramic porous materials have high density, low porosity, and very low adsorbent loading rate; metal-based sheets and The adsorbents have weak force, small surface area, and low adsorbent loading rate; and, except for metal foils, they have low thermal conductivity and low photothermal conversion efficiency. On the other hand, most MOFs are white or light-colored powders with poor light absorption capabilities and low photothermal conversion performance, so their photothermal properties need to be enhanced. The commonly used method is to add photothermal agents to achieve photothermal strengthening. There are currently four types of photothermal agents reported, namely precious metal nanoparticles, metal semiconductor nanoparticles, carbon-based nanomaterials and polymers. Among them, metal semiconductor nanoparticles and carbon-based nanomaterials are commonly used. However, the addition of these photothermal agents will reduce the moisture absorption of MOF to a certain extent (including reducing the MOF loading rate or partially blocking the MOF micropores). Therefore, it is necessary to choose a substrate with high specific surface area (porosity), high thermal conductivity and high photothermal conversion performance as the carrier of the adsorbent to increase the loading rate of the MOF adsorbent and at the same time, use photothermal energy with the assistance of solar energy. It is a reasonable design strategy to achieve rapid dehydration of the adsorbent by conversion, thereby reducing the desorption energy consumption of the adsorbent. In addition, how to uniformly disperse high loading MOF grains in the substrate is closely related to the MOF loading process. There are generally two methods to load MOFs, namely direct dip coating and in-situ synthesis. The dip coating method requires the addition of an external adhesive to adhere the adsorbent to the substrate. Commonly used adhesives include sodium silicate solution, silicon solution and organopolysiloxane resin. In this method, the adhesive easily blocks the pores of the MOF adsorbent, thereby affecting the adsorption effect. The in-situ synthesis method allows MOF to grow in situ on the substrate. This method can obtain different thicknesses, dense and uniform adsorption coatings, with the simplicity of one-step synthesis and excellent heat and mass transfer performance.

基于上述讨论,在本发明中,选用活性碳纤维作为MOF负载的基材,相较于玻璃纤维等,它具有更优异的光热转换能力,不需要添加光热剂也能利用太阳能驱动解吸水。活性碳纤维其丰富的孔结构还赋予了MOF生长位点,同时具备提高传质效率和光热强化的双功能,在太阳能辅助脱水的大气集水领域具有广阔的应用背景。Based on the above discussion, in the present invention, activated carbon fiber is selected as the MOF-loaded substrate. Compared with glass fiber, it has better photothermal conversion capabilities and can use solar energy to drive desorption of water without adding photothermal agents. The rich pore structure of activated carbon fiber also gives MOF growth sites. It also has the dual functions of improving mass transfer efficiency and photothermal enhancement. It has a broad application background in the field of atmospheric water collection for solar-assisted dehydration.

发明内容Contents of the invention

为了克服粉体MOFs在使用过程中传质传热效率低、光热转换效率低等不足,本发明的目的提供一种MOFs块体吸湿剂及其混合溶剂热原位合成方法。本发明提供的混合溶剂热原位合成的活性碳纤维基MOFs块体吸湿剂具有水吸附量高、吸附速率快、MOFs与基材结合力强(不掉粉)、光热转换能力强等特点,可用于太阳能驱动解吸水的大气集水领域,实现低能耗。In order to overcome the shortcomings of low mass and heat transfer efficiency and low photothermal conversion efficiency of powder MOFs during use, the purpose of the present invention is to provide a thermal in-situ synthesis method of MOFs bulk hygroscopic agent and its mixed solvent. The activated carbon fiber-based MOFs bulk hygroscopic agent synthesized thermally in situ by mixed solvents provided by the present invention has the characteristics of high water adsorption capacity, fast adsorption rate, strong binding force between MOFs and the substrate (no powder falling off), and strong photothermal conversion ability. It can be used in the field of atmospheric water collection for solar-driven desorption of water to achieve low energy consumption.

本发明的目的通过以下技术方案实现。The object of the present invention is achieved through the following technical solutions.

本发明提供的一种活性碳纤维基MOFs块体吸湿剂的混合溶剂热原位合成方法,包括以下步骤:The invention provides a mixed solvent thermal in-situ synthesis method of activated carbon fiber-based MOFs bulk hygroscopic agent, which includes the following steps:

(1)活性碳纤维的亲水改性处理:将活性碳纤维浸入氧化剂中活化,再将其浸入到含亲水改性成膜材料的水溶液中,充分浸润后,清洗并烘干得亲水改性活性碳纤维;(1) Hydrophilic modification treatment of activated carbon fiber: Dip the activated carbon fiber into an oxidant for activation, and then immerse it into an aqueous solution containing hydrophilic modified film-forming materials. After sufficient infiltration, clean and dry to obtain hydrophilic modification. activated carbon fiber;

(2)反应液的配制:搅拌条件下,将有机二元羧酸的N,N-二甲基甲酰胺溶液和铝盐水溶液混合得均匀反应液;(2) Preparation of the reaction solution: Under stirring conditions, mix the N,N-dimethylformamide solution of the organic dicarboxylic acid and the aluminum salt solution to obtain a uniform reaction solution;

(3)MOFs块体吸湿剂混合溶剂热原位合成:将改性活性碳纤维浸没于反应液中进行晶化反应,反应结束后将负载MOFs涂层的活性碳纤维取出、洗涤并烘干后得活性碳纤维基MOFs块体吸湿剂。(3) MOFs bulk hygroscopic agent mixed solvent thermal in-situ synthesis: immerse the modified activated carbon fiber in the reaction solution for crystallization reaction. After the reaction, take out the activated carbon fiber loaded with MOFs coating, wash and dry to obtain the activity Carbon fiber-based MOFs bulk moisture absorber.

优选的,步骤(1)所述氧化剂包括浓硫酸、浓硝酸、过氧化氢、高锰酸钾和浓硫酸及浓硝酸混合物(v/v:1/1)中的一种。Preferably, the oxidizing agent in step (1) includes one of concentrated sulfuric acid, concentrated nitric acid, hydrogen peroxide, potassium permanganate, and a mixture (v/v: 1/1) of concentrated sulfuric acid and concentrated nitric acid.

进一步优选的,考虑活性碳纤维在以上氧化剂的氧化情况,所述氧化剂为浓硫酸。It is further preferred to consider the oxidation of the activated carbon fiber in the above oxidant, and the oxidant is concentrated sulfuric acid.

优选的,步骤(1)所述的亲水改性成膜材料包括壳聚糖季铵盐、壳聚糖盐酸盐、羧甲基壳聚糖、壳寡糖中的一种。Preferably, the hydrophilic modified film-forming material in step (1) includes one of chitosan quaternary ammonium salt, chitosan hydrochloride, carboxymethyl chitosan, and chitosan oligosaccharide.

进一步优选的,考虑到基材与亲水改性成膜材料的结合力、价格等因素,所述亲水改性成膜材料为壳聚糖盐酸盐。Further preferably, considering factors such as the binding force between the substrate and the hydrophilic modified film-forming material, price, etc., the hydrophilic modified film-forming material is chitosan hydrochloride.

优选的,步骤(2)所述有机二元羧酸包括3,5-吡唑二羧酸、富马酸、2,5-呋喃二甲酸和间苯二甲酸中的一种或两种。Preferably, the organic dicarboxylic acid in step (2) includes one or two of 3,5-pyrazoledicarboxylic acid, fumaric acid, 2,5-furandicarboxylic acid and isophthalic acid.

优选的,步骤(2)所述铝盐为九水合硝酸铝、十八水合硫酸铝、六水氯化铝、乙酸铝中的一种。Preferably, the aluminum salt in step (2) is one of aluminum nitrate nonahydrate, aluminum sulfate octahydrate, aluminum chloride hexahydrate, and aluminum acetate.

步骤(2)所述MOF包括由上述有机二元羧酸,3,5-吡唑二羧酸、富马酸、2,5-呋喃二甲酸和间苯二甲酸与铝盐配合分别形成的MOF-303、Al-fumarate(A520)、MIL-160(Al)、CAU-10-H中的一种MOF或二种混合MOFs。The MOF in step (2) includes MOFs formed respectively from the above-mentioned organic dicarboxylic acids, 3,5-pyrazoledicarboxylic acid, fumaric acid, 2,5-furandicarboxylic acid and isophthalic acid combined with aluminum salts One MOF or two mixed MOFs among -303, Al-fumarate (A520), MIL-160 (Al), and CAU-10-H.

进一步优选的,考虑到有机二元羧酸和铝盐的价格、反应难易程度以及干旱地区大气集水的应用背景(要求其在低湿度条件下应具有高吸湿量),所述的有机二元羧酸为3,5-吡唑二羧酸和富马酸,所述铝盐为九水合硝酸铝,形成的产物为MOF-303和MOF-303/Al-Fum混合MOFs。Further preferably, taking into account the price of organic dicarboxylic acids and aluminum salts, the ease of reaction, and the application background of atmospheric water collection in arid areas (requiring that they should have high moisture absorption under low humidity conditions), the organic dicarboxylic acid The carboxylic acids are 3,5-pyrazoledicarboxylic acid and fumaric acid, the aluminum salt is aluminum nitrate nonahydrate, and the products formed are MOF-303 and MOF-303/Al-Fum mixed MOFs.

优选的,步骤(2)所述有机二元羧酸与铝盐水溶液中铝离子摩尔配比为1:0.8~1.25。Preferably, the molar ratio of aluminum ions in the organic dicarboxylic acid and aluminum salt solution described in step (2) is 1:0.8-1.25.

进一步优选的,所述有机二元羧酸与铝盐水溶液中铝离子摩尔配比为1:0.9~1.2。Further preferably, the molar ratio of aluminum ions in the organic dicarboxylic acid and aluminum salt solution is 1:0.9-1.2.

优选的,步骤(2)所述DMF与铝盐水溶液中的水的体积比为1:5~10。Preferably, the volume ratio of DMF to water in the aluminum salt solution in step (2) is 1:5-10.

进一步优选的,有机二元羧酸在水中的溶解度低,DMF的加入可有效地溶解有机二元羧酸。由于DMF与H2O互溶,从而使有机二元羧酸均匀地分散在反应液中;通过固定DMF的添加量,增大或减小H2O的量来调节反应液中的DMF与H2O的体积比;H2O的量大,即DMF的浓度小,有机二元羧酸在反应液的溶解性差,体系分散性差,不利于有机二元羧酸与基材周边Al3+的结合和MOF在基材上的生长;H2O的量小,即DMF的浓度大,铝离子向基材迁移速率快,可与Al3+有效结合和负载基材上,所述DMF与铝盐水溶液中的水的体积比为1:6~8。Further preferably, the solubility of organic dicarboxylic acid in water is low, and the addition of DMF can effectively dissolve the organic dicarboxylic acid. Since DMF and H 2 O are mutually soluble, the organic dicarboxylic acid is evenly dispersed in the reaction solution; by fixing the added amount of DMF and increasing or decreasing the amount of H 2 O, the DMF and H 2 in the reaction solution can be adjusted. The volume ratio of O; the large amount of H 2 O, that is, the concentration of DMF is small, the solubility of organic dicarboxylic acid in the reaction solution is poor, and the dispersion of the system is poor, which is not conducive to the combination of organic dicarboxylic acid and Al 3+ around the substrate And the growth of MOF on the substrate; the amount of H 2 O is small, that is, the concentration of DMF is large, the aluminum ions migrate to the substrate quickly, and can effectively combine with Al 3+ and load the substrate, the DMF and aluminum salt The volume ratio of water in the aqueous solution is 1:6~8.

优选的,步骤(3)所述晶化反应的温度为80~120℃。Preferably, the temperature of the crystallization reaction in step (3) is 80-120°C.

进一步优选的,反应温度低,晶化速率慢,所形成的MOFs涂层薄,块体吸湿剂的吸水量低;反应温度高,晶化速率过快,形成的MOFs涂层厚,MOFs涂层与基材作用力弱,MOFs晶粒易脱落,所述晶化反应的温度为90~110℃。It is further preferred that the reaction temperature is low, the crystallization rate is slow, the MOFs coating formed is thin, and the water absorption capacity of the bulk hygroscopic agent is low; the reaction temperature is high, the crystallization rate is too fast, the MOFs coating formed is thick, and the MOFs coating is The interaction force with the substrate is weak, and the MOFs crystal grains are easy to fall off. The temperature of the crystallization reaction is 90 to 110°C.

优选的,步骤(3)所述晶化反应的时间为10~14h。Preferably, the crystallization reaction time in step (3) is 10 to 14 hours.

优选的,步骤(3)所述洗涤为使用乙醇和去离子水交替分别洗涤3次。Preferably, the washing in step (3) is to wash three times with ethanol and deionized water alternately.

优选的,步骤(3)所述的活化温度为100~150℃;活化时间为6~10h。Preferably, the activation temperature in step (3) is 100-150°C; the activation time is 6-10 hours.

本发明提供一种由上述制备方法制得的活性碳纤维基MOFs块体吸湿剂。The invention provides an activated carbon fiber-based MOFs bulk moisture absorbent prepared by the above preparation method.

本发明提供的混合溶剂热原位合成方法,以活性碳纤维为基材,使用氧化剂对其处理以增加基材上的含氧基团,并使用亲水改性成膜材料对活性碳纤维进行进一步亲水改性以增加基材上的氨基、羧基、羟基等亲水性基团,加强MOFs与基材之间的作用力。The mixed solvent thermal in-situ synthesis method provided by the invention uses activated carbon fiber as the base material, uses oxidant to treat it to increase the oxygen-containing groups on the base material, and uses hydrophilic modified film-forming materials to further hydrophilize the activated carbon fiber. Water modification is used to increase hydrophilic groups such as amino groups, carboxyl groups, and hydroxyl groups on the substrate to strengthen the interaction between MOFs and the substrate.

与现有技术相比,本发明具有如下优点和有益效果:Compared with the existing technology, the present invention has the following advantages and beneficial effects:

1、本发明提供的原位合成方法,所制得的活性碳纤维基MOFs块体吸湿剂,MOFs与基材结合力强,不易发生脱落现象,解决了粉体MOFs传质传热效果差的问题,同时原位合成工艺提高了MOFs负载率。1. The in-situ synthesis method provided by the present invention produces an activated carbon fiber-based MOFs bulk hygroscopic agent. The MOFs have strong binding force with the substrate and are not prone to falling off, thus solving the problem of poor mass and heat transfer effects of powdered MOFs. , while the in-situ synthesis process improves the loading rate of MOFs.

2、本发明提供的原位合成方法,没有使用胶粘剂,避免了胶粘剂堵塞MOFs吸附剂孔隙的问题,从而提高MOFs块体吸湿剂吸湿量。2. The in-situ synthesis method provided by the present invention does not use adhesives, which avoids the problem of adhesives blocking the pores of MOFs adsorbents, thereby increasing the moisture absorption capacity of MOFs bulk hygroscopic agents.

3、本发明提供的原位合成方法,所制得的MOFs块体吸湿剂相较于MOFs粉末来说具有更低的脱附温度,从而降低集水系统运行能耗。3. According to the in-situ synthesis method provided by the present invention, the MOFs bulk hygroscopic agent produced has a lower desorption temperature than MOFs powder, thereby reducing the energy consumption of the water collection system.

4、本发明使用的活性碳纤维基材,不仅有丰富的孔结构,还具有优异的光热转换性能,弥补了常规基材及MOFs光热转换效率差的缺陷,可利用太阳能驱动解吸MOFs吸附剂吸附的水分。4. The activated carbon fiber substrate used in the present invention not only has a rich pore structure, but also has excellent photothermal conversion performance, which makes up for the shortcomings of poor photothermal conversion efficiency of conventional substrates and MOFs, and can use solar energy to drive the desorption of MOFs adsorbents. Adsorbed moisture.

5、本发明以MOF-303和Al-Fum单体在活性碳纤维基材上原位合成了MOF-303/Al-Fum混合MOFs块体吸附剂,通过改变两种配体的比例制备了一系列不同含量的双配体混合MOFs块体吸附剂,可调节MOF水吸附等温曲线以适应与不同的应用场合。5. The present invention uses MOF-303 and Al-Fum monomers to in-situ synthesize MOF-303/Al-Fum mixed MOFs bulk adsorbents on activated carbon fiber substrates, and prepares a series of MOF-303/Al-Fum mixed MOFs bulk adsorbents by changing the ratio of the two ligands. Mixed MOFs bulk adsorbents with different contents of double ligands can adjust the MOF water adsorption isotherm curve to suit different applications.

6、本发明制备的块体吸湿剂在低湿度条件下(≤30%RH)具有高水蒸气吸附容量。6. The bulk hygroscopic agent prepared by the present invention has high water vapor adsorption capacity under low humidity conditions (≤30% RH).

附图说明Description of the drawings

图1为实施例1、8和比较例1、2制备得到的吸湿剂的XRD谱。Figure 1 is the XRD spectrum of the hygroscopic agents prepared in Examples 1 and 8 and Comparative Examples 1 and 2.

图2为实施例1制得的活性碳纤维基MOF-303块体吸湿剂、改性前的活性碳纤维、改性后的活性碳纤维的SEM图。Figure 2 is a SEM image of the activated carbon fiber-based MOF-303 bulk moisture absorbent prepared in Example 1, the activated carbon fiber before modification, and the activated carbon fiber after modification.

图3为实施例1和比较例1制备得到的吸湿剂的动态水吸附曲线。Figure 3 is the dynamic water adsorption curve of the hygroscopic agent prepared in Example 1 and Comparative Example 1.

图4为实施例6-10制备得到的混合MOFs块体吸湿剂的动态水吸附曲线。Figure 4 is the dynamic water adsorption curve of the mixed MOFs bulk hygroscopic agent prepared in Examples 6-10.

图5为实施例1、8和比较例1制备得到的吸湿剂的静态水吸附曲线。Figure 5 shows the static water adsorption curves of the hygroscopic agents prepared in Examples 1, 8 and Comparative Example 1.

图6为实施例1、8和比较例1制备得到的吸湿剂及未改性的活性碳纤维的UV-vis-NIR吸收谱。Figure 6 shows the UV-vis-NIR absorption spectra of the hygroscopic agents and unmodified activated carbon fibers prepared in Examples 1, 8 and Comparative Example 1.

图7为实施例1和比较例1制备得到的吸湿剂在模拟太阳光下样品表面温度随时间的变化曲线。Figure 7 is a curve of the surface temperature of the sample prepared in Example 1 and Comparative Example 1 under simulated sunlight as a function of time.

具体实施方式Detailed ways

以下结合附图和实施例对本发明的具体实施作进一步说明,但本发明的实施和保护不限于此。需指出的是,以下若有未特别详细说明之过程,均是本领域技术人员可参照现有技术实现或理解的。所用试剂或仪器未注明生产厂商者,视为可以通过市售购买得到的常规产品。The specific implementation of the present invention will be further described below in conjunction with the accompanying drawings and examples, but the implementation and protection of the present invention are not limited thereto. It should be pointed out that any process that is not specifically described in detail below can be implemented or understood by those skilled in the art with reference to the existing technology. If the manufacturer of the reagents or instruments used is not indicated, they are regarded as conventional products that can be purchased commercially.

活性碳纤维的预处理:将活性碳纤维剪成3×3×0.5cm3的薄布。首先,将剪裁好的活性碳纤维浸入浓硫酸中2h后使用去离子水清洗直至中性,放置烘箱干燥。然后,将活化后的活性碳纤维浸入25mg/mL壳聚糖盐酸盐溶液中使其充分润湿,取出用去离子水清洗基材上多余的溶液后在70℃干燥。Pretreatment of activated carbon fiber: Cut the activated carbon fiber into thin cloth of 3×3× 0.5cm3 . First, the cut activated carbon fiber was immersed in concentrated sulfuric acid for 2 hours, washed with deionized water until neutral, and placed in an oven to dry. Then, the activated activated carbon fiber was immersed in 25 mg/mL chitosan hydrochloride solution to fully moisten it, and the excess solution on the substrate was washed with deionized water and dried at 70°C.

壳聚糖盐酸盐也可使用壳聚糖季铵盐、羧甲基壳聚糖或壳寡糖代替。Chitosan hydrochloride can also be replaced by chitosan quaternary ammonium salt, carboxymethyl chitosan or chitosan oligosaccharide.

比较例1Comparative example 1

(1)室温及磁力搅拌下,取50mL烧杯,按照3,5-吡唑二羧酸与Al3+的摩尔配比1:1,DMF与H2O体积比1:7,取0.72g(4mmol)3,5-吡唑二羧酸溶于5mL DMF中形成3,5-吡唑二羧酸的DMF溶液;取1.52g(4mmol)Al(NO3)3·9H2O溶于35mL去离子水中形成Al(NO3)3的水溶液;将3,5-吡唑二羧酸的DMF溶液逐滴加入Al(NO3)3的水溶液中,持续搅拌20min得均匀反应液。(1) Under room temperature and magnetic stirring, take a 50mL beaker, according to the molar ratio of 3,5-pyrazoledicarboxylic acid to Al 3+ 1:1, the volume ratio of DMF to H 2 O 1:7, take 0.72g ( Dissolve 4mmol) 3,5-pyrazoledicarboxylic acid in 5mL DMF to form a DMF solution of 3,5-pyrazoledicarboxylic acid; take 1.52g (4mmol) Al(NO 3 ) 3 ·9H 2 O and dissolve it in 35mL. An aqueous solution of Al(NO 3 ) 3 is formed in the ionized water; add the DMF solution of 3,5-pyrazoledicarboxylic acid dropwise into the aqueous solution of Al(NO 3 ) 3 , and stir continuously for 20 minutes to obtain a uniform reaction solution.

(2)将步骤(1)制备得到的反应液添加至100mL聚四氟乙烯内衬反应釜中,密封后置于马弗炉中100℃下反应12h,反应结束,冷却至室温。使用G4漏斗抽滤混合溶液后将得到的固体湿料使用无水乙醇和去离子水分别交替洗涤三次,在鼓风干燥箱120℃下干燥活化6h,得MOF-303吸湿剂粉末。(2) Add the reaction solution prepared in step (1) to a 100 mL polytetrafluoroethylene-lined reactor, seal it and place it in a muffle furnace at 100°C for 12 hours. After the reaction is completed, cool to room temperature. After filtering the mixed solution using a G4 funnel, the obtained solid wet material was washed three times with absolute ethanol and deionized water alternately, and dried and activated in a blast drying oven at 120°C for 6 hours to obtain MOF-303 hygroscopic agent powder.

比较例2Comparative example 2

(1)室温及磁力搅拌下,取50mL烧杯,按照配体与Al3+的摩尔配比1:1,DMF与H2O体积比1:8,取0.269g(1.5mmol)3,5-吡唑二羧酸和0.175g(1.5mmol)富马酸溶于5mL DMF中形成双配体的DMF溶液;取1.14g(3mmol)Al(NO3)3·9H2O溶于40mL去离子水中形成Al(NO3)3的水溶液;将双配体的DMF溶液逐滴加入Al(NO3)3的水溶液中,持续搅拌20min得均匀反应液。(1) Under room temperature and magnetic stirring, take a 50mL beaker, according to the molar ratio of ligand to Al 3+ 1:1, the volume ratio of DMF to H 2 O 1:8, take 0.269g (1.5mmol) 3,5- Dissolve pyrazole dicarboxylic acid and 0.175g (1.5mmol) fumaric acid in 5mL DMF to form a double-ligand DMF solution; take 1.14g (3mmol) Al(NO 3 ) 3 ·9H 2 O and dissolve it in 40mL deionized water. An aqueous solution of Al(NO 3 ) 3 is formed; add the double-ligand DMF solution dropwise into the aqueous solution of Al(NO 3 ) 3 , and stir continuously for 20 minutes to obtain a uniform reaction solution.

(2)将步骤(1)制备得到的反应液添加至100mL聚四氟乙烯内衬反应釜中,密封后置于马弗炉中110℃下反应12h,反应结束,冷却至室温。使用G4漏斗抽滤混合溶液后将得到的固体湿料使用无水乙醇和去离子水分别交替洗涤三次,在鼓风干燥箱120℃下干燥活化6h,得MOF-303/Al-Fum混合吸湿剂粉末。(2) Add the reaction solution prepared in step (1) to a 100 mL polytetrafluoroethylene-lined reactor, seal it and place it in a muffle furnace at 110°C for 12 hours. After the reaction is completed, cool to room temperature. After filtering the mixed solution using a G4 funnel, the obtained solid wet material was washed three times with absolute ethanol and deionized water alternately, and dried and activated in a blast drying oven at 120°C for 6 hours to obtain MOF-303/Al-Fum mixed hygroscopic agent. powder.

实施例1Example 1

(1)室温及磁力搅拌下,取50mL烧杯,按照3,5-吡唑二羧酸与Al3+的摩尔配比1:1,DMF与H2O体积比1:6,取0.72g(4mmol)3,5-吡唑二羧酸溶于5mL DMF中形成3,5-吡唑二羧酸的DMF溶液;取1.52g(4mmol)Al(NO3)3·9H2O溶于30mL去离子水中形成Al(NO3)3的水溶液;将3,5-吡唑二羧酸的DMF溶液逐滴加入Al(NO3)3的水溶液中,持续搅拌20min得均匀反应液。(1) Under room temperature and magnetic stirring, take a 50mL beaker, according to the molar ratio of 3,5-pyrazoledicarboxylic acid to Al 3+ 1:1, the volume ratio of DMF to H 2 O 1:6, take 0.72g ( Dissolve 4mmol) 3,5-pyrazoledicarboxylic acid in 5mL DMF to form a DMF solution of 3,5-pyrazoledicarboxylic acid; take 1.52g (4mmol) Al(NO 3 ) 3 ·9H 2 O and dissolve it in 30mL. An aqueous solution of Al(NO 3 ) 3 is formed in the ionized water; add the DMF solution of 3,5-pyrazoledicarboxylic acid dropwise into the aqueous solution of Al(NO 3 ) 3 , and stir continuously for 20 minutes to obtain a uniform reaction solution.

(2)将步骤(1)制备得到的反应液添加至100mL聚四氟乙烯内衬反应釜中,将预处理后的活性碳纤维倾斜地浸没在反应液中,密封后置于马弗炉中100℃下反应12h,反应结束,冷却至室温。取出块体,使用无水乙醇和去离子水分别交替洗涤三次,在鼓风干燥箱120℃下干燥活化6h,得活性碳纤维基MOF-303块体吸湿剂。(2) Add the reaction solution prepared in step (1) to a 100mL polytetrafluoroethylene-lined reactor, immerse the pretreated activated carbon fiber in the reaction solution obliquely, seal it and place it in a muffle furnace for 100 The reaction was carried out for 12 hours at ℃. After the reaction was completed, the mixture was cooled to room temperature. Take out the block, wash it three times with absolute ethanol and deionized water alternately, dry and activate it in a blast drying oven at 120°C for 6 hours to obtain the activated carbon fiber-based MOF-303 block moisture absorbent.

实施例2Example 2

(1)室温及磁力搅拌下,取50mL烧杯,按照3,5-吡唑二羧酸与Al3+的摩尔配比1:0.8,DMF与H2O体积比1:5,取0.72g(4mmol)3,5-吡唑二羧酸溶于5mL DMF中形成3,5-吡唑二羧酸的DMF溶液;取1.22g(3.2mmol)Al(NO3)3·9H2O溶于25mL去离子水中形成Al(NO3)3的水溶液;将3,5-吡唑二羧酸的DMF溶液逐滴加入Al(NO3)3的水溶液中,持续搅拌20min得均匀反应液。(1) Under room temperature and magnetic stirring, take a 50mL beaker, according to the molar ratio of 3,5-pyrazoledicarboxylic acid to Al 3+ 1:0.8, the volume ratio of DMF to H 2 O 1:5, take 0.72g ( Dissolve 4mmol) 3,5-pyrazoledicarboxylic acid in 5mL DMF to form a DMF solution of 3,5-pyrazoledicarboxylic acid; take 1.22g (3.2mmol) Al(NO 3 ) 3 ·9H 2 O and dissolve it in 25mL An aqueous solution of Al(NO 3 ) 3 is formed in deionized water; add the DMF solution of 3,5-pyrazoledicarboxylic acid dropwise into the aqueous solution of Al(NO 3 ) 3 , and stir continuously for 20 minutes to obtain a uniform reaction solution.

(2)将步骤(1)制备得到的反应液添加至100mL聚四氟乙烯内衬反应釜中,将预处理后的活性碳纤维倾斜地浸没在反应液中,密封后置于马弗炉中110℃下反应10h,反应结束,冷却至室温。取出块体,使用无水乙醇和去离子水分别交替洗涤三次,在鼓风干燥箱110℃下干燥活化8h,得活性碳纤维基MOF-303块体吸湿剂。(2) Add the reaction solution prepared in step (1) to a 100mL polytetrafluoroethylene-lined reactor, immerse the pretreated activated carbon fiber in the reaction solution obliquely, seal it and place it in a muffle furnace for 110 The reaction was carried out for 10 hours at ℃, the reaction was completed, and the mixture was cooled to room temperature. Take out the block, wash it three times with absolute ethanol and deionized water alternately, dry and activate it in a blast drying oven at 110°C for 8 hours to obtain the activated carbon fiber-based MOF-303 block moisture absorbent.

实施例3Example 3

(1)室温及磁力搅拌下,取50mL烧杯,按照3,5-吡唑二羧酸与Al3+的摩尔配比1:0.9,DMF与H2O体积比1:7,取0.72g(4mmol)3,5-吡唑二羧酸溶于5mL DMF中形成3,5-吡唑二羧酸的DMF溶液;取1.37g(3.6mmol)Al(NO3)3·9H2O溶于35mL去离子水中形成Al(NO3)3的水溶液;将3,5-吡唑二羧酸的DMF溶液逐滴加入Al(NO3)3的水溶液中,持续搅拌20min得均匀反应液。(1) Under room temperature and magnetic stirring, take a 50mL beaker, according to the molar ratio of 3,5-pyrazoledicarboxylic acid to Al 3+ 1:0.9, the volume ratio of DMF to H 2 O 1:7, take 0.72g ( Dissolve 4mmol) 3,5-pyrazoledicarboxylic acid in 5mL DMF to form a DMF solution of 3,5-pyrazoledicarboxylic acid; take 1.37g (3.6mmol) Al(NO 3 ) 3 ·9H 2 O and dissolve it in 35mL An aqueous solution of Al(NO 3 ) 3 is formed in deionized water; add the DMF solution of 3,5-pyrazoledicarboxylic acid dropwise into the aqueous solution of Al(NO 3 ) 3 , and stir continuously for 20 minutes to obtain a uniform reaction solution.

(2)将步骤(1)制备得到的反应液添加至100mL聚四氟乙烯内衬反应釜中,将预处理后的活性碳纤维倾斜地浸没在反应液中,密封后置于马弗炉中120℃下反应11h,反应结束,冷却至室温。取出块体,使用无水乙醇和去离子水分别交替洗涤三次,在鼓风干燥箱120℃下干燥活化10h,得活性碳纤维基MOF-303块体吸湿剂。(2) Add the reaction liquid prepared in step (1) to a 100 mL polytetrafluoroethylene-lined reactor, immerse the pretreated activated carbon fiber in the reaction liquid obliquely, seal it and place it in a muffle furnace for 120 The reaction was carried out for 11 hours at ℃, the reaction was completed, and the mixture was cooled to room temperature. Take out the block, wash it three times alternately with absolute ethanol and deionized water, and dry and activate it in a blast drying oven at 120°C for 10 hours to obtain an activated carbon fiber-based MOF-303 block moisture absorbent.

实施例4Example 4

(1)室温及磁力搅拌下,取50mL烧杯,按照3,5-吡唑二羧酸与Al3+的摩尔配比1:1.1,DMF与H2O体积比1:8,取0.72g(4mmol)3,5-吡唑二羧酸溶于5mL DMF中形成3,5-吡唑二羧酸的DMF溶液;取1.67g(4.4mmol)Al(NO3)3·9H2O溶于40mL去离子水中形成Al(NO3)3的水溶液;将3,5-吡唑二羧酸的DMF溶液逐滴加入Al(NO3)3的水溶液中,持续搅拌20min得均匀反应液。(1) Under room temperature and magnetic stirring, take a 50mL beaker, according to the molar ratio of 3,5-pyrazoledicarboxylic acid to Al 3+ 1:1.1, the volume ratio of DMF to H 2 O 1:8, take 0.72g ( Dissolve 4mmol) 3,5-pyrazoledicarboxylic acid in 5mL DMF to form a DMF solution of 3,5-pyrazoledicarboxylic acid; take 1.67g (4.4mmol) Al(NO 3 ) 3 ·9H 2 O and dissolve it in 40mL An aqueous solution of Al(NO 3 ) 3 is formed in deionized water; add the DMF solution of 3,5-pyrazoledicarboxylic acid dropwise into the aqueous solution of Al(NO 3 ) 3 , and stir continuously for 20 minutes to obtain a uniform reaction solution.

(2)将步骤(1)制备得到的反应液添加至100mL聚四氟乙烯内衬反应釜中,将预处理后的活性碳纤维倾斜地浸没在反应液中,密封后置于马弗炉中80℃下反应13h,反应结束,冷却至室温。取出块体,使用无水乙醇和去离子水分别交替洗涤三次,在鼓风干燥箱100℃下干燥活化10h,得活性碳纤维基MOF-303块体吸湿剂。(2) Add the reaction solution prepared in step (1) to a 100mL polytetrafluoroethylene-lined reactor, immerse the pretreated activated carbon fiber in the reaction solution obliquely, seal it and place it in a muffle furnace for 80 The reaction was carried out for 13 hours at ℃, and then the reaction was completed and cooled to room temperature. Take out the block, wash it three times alternately with absolute ethanol and deionized water, and dry and activate it in a blast drying oven at 100°C for 10 hours to obtain an activated carbon fiber-based MOF-303 block moisture absorbent.

实施例5Example 5

(1)室温及磁力搅拌下,取50mL烧杯,按照3,5-吡唑二羧酸与Al3+的摩尔配比1:1.25,DMF与H2O体积比1:10,取0.72g(4mmol)3,5-吡唑二羧酸溶于5mL DMF中形成3,5-吡唑二羧酸的DMF溶液;取1.9g(5mmol)Al(NO3)3·9H2O溶于50mL去离子水中形成Al(NO3)3的水溶液;将3,5-吡唑二羧酸的DMF溶液逐滴加入Al(NO3)3的水溶液中,持续搅拌20min得均匀反应液。(1) Under room temperature and magnetic stirring, take a 50mL beaker, according to the molar ratio of 3,5-pyrazoledicarboxylic acid to Al 3+ 1:1.25, the volume ratio of DMF to H 2 O 1:10, take 0.72g ( Dissolve 4mmol) 3,5-pyrazoledicarboxylic acid in 5mL DMF to form a DMF solution of 3,5-pyrazoledicarboxylic acid; take 1.9g (5mmol) Al(NO 3 ) 3 ·9H 2 O and dissolve it in 50mL. An aqueous solution of Al(NO 3 ) 3 is formed in the ionized water; add the DMF solution of 3,5-pyrazoledicarboxylic acid dropwise into the aqueous solution of Al(NO 3 ) 3 , and stir continuously for 20 minutes to obtain a uniform reaction solution.

(2)将步骤(1)制备得到的反应液添加至100mL聚四氟乙烯内衬反应釜中,将预处理后的活性碳纤维倾斜地浸没在反应液中,密封后置于马弗炉中90℃下反应14h,反应结束,冷却至室温。取出块体,使用无水乙醇和去离子水分别交替洗涤三次,在鼓风干燥箱150℃下干燥活化6h,得活性碳纤维基MOF-303块体吸湿剂。(2) Add the reaction solution prepared in step (1) to a 100mL polytetrafluoroethylene-lined reactor, immerse the pretreated activated carbon fiber in the reaction solution obliquely, seal it and place it in a muffle furnace for 90 The reaction was carried out for 14 hours at ℃, and then the reaction was completed and cooled to room temperature. Take out the block, wash it three times with absolute ethanol and deionized water alternately, dry and activate it in a blast drying oven at 150°C for 6 hours to obtain the activated carbon fiber-based MOF-303 block moisture absorbent.

实施例6Example 6

(1)室温及磁力搅拌下,取50mL烧杯,按照配体与Al3+的摩尔配比1:0.8,DMF与H2O体积比1:6,取0.43g(2.4mmol)3,5-吡唑二羧酸和0.07g(0.6mmol)富马酸溶于5mL DMF中形成双配体的DMF溶液;取0.912g(3mmol)Al(NO3)3·9H2O溶于30mL去离子水中形成Al(NO3)3的水溶液;将双配体的DMF溶液逐滴加入Al(NO3)3的水溶液中,持续搅拌20min得均匀反应液。(1) Under room temperature and magnetic stirring, take a 50mL beaker, according to the molar ratio of ligand to Al 3+ 1:0.8, the volume ratio of DMF to H 2 O 1:6, take 0.43g (2.4mmol) 3,5- Pyrazole dicarboxylic acid and 0.07g (0.6mmol) fumaric acid were dissolved in 5mL DMF to form a double-ligand DMF solution; 0.912g (3mmol) Al(NO 3 ) 3 ·9H 2 O was dissolved in 30mL deionized water. An aqueous solution of Al(NO 3 ) 3 is formed; add the double-ligand DMF solution dropwise into the aqueous solution of Al(NO 3 ) 3 , and stir continuously for 20 minutes to obtain a uniform reaction solution.

(2)将步骤(1)制备得到的反应液添加至100mL聚四氟乙烯内衬反应釜中,将预处理后的活性碳纤维倾斜地浸没在反应液中,密封后置于马弗炉中110℃下反应14h,反应结束,冷却至室温。取出块体,使用无水乙醇和去离子水分别交替洗涤三次,在鼓风干燥箱120℃下干燥活化8h,得活性碳纤维基MOF-303/Al-Fum(8/2)混合MOFs块体吸湿剂。(2) Add the reaction solution prepared in step (1) to a 100mL polytetrafluoroethylene-lined reactor, immerse the pretreated activated carbon fiber in the reaction solution obliquely, seal it and place it in a muffle furnace for 110 The reaction was carried out for 14 hours at ℃, and then the reaction was completed and cooled to room temperature. Take out the block, wash it three times alternately with absolute ethanol and deionized water, and dry and activate it in a blast drying oven at 120°C for 8 hours to obtain an activated carbon fiber-based MOF-303/Al-Fum (8/2) mixed MOFs block that absorbs moisture. agent.

实施例7Example 7

(1)室温及磁力搅拌下,取50mL烧杯,按照配体与Al3+的摩尔配比1:0.9,DMF与H2O体积比1:7,取0.377g(2.1mmol)3,5-吡唑二羧酸和0.105g(0.9mmol)富马酸溶于5mL DMF中形成双配体的DMF溶液;取1.026g(3mmol)Al(NO3)3·9H2O溶于30mL去离子水中形成Al(NO3)3的水溶液;将双配体的DMF溶液逐滴加入Al(NO3)3的水溶液中,持续搅拌20min得均匀反应液。(1) Under room temperature and magnetic stirring, take a 50mL beaker, according to the molar ratio of ligand to Al 3+ 1:0.9, the volume ratio of DMF to H 2 O 1:7, take 0.377g (2.1mmol) 3,5- Pyrazole dicarboxylic acid and 0.105g (0.9mmol) fumaric acid were dissolved in 5mL DMF to form a double-ligand DMF solution; 1.026g (3mmol) Al(NO 3 ) 3 ·9H 2 O was dissolved in 30mL deionized water. An aqueous solution of Al(NO 3 ) 3 is formed; add the double-ligand DMF solution dropwise into the aqueous solution of Al(NO 3 ) 3 , and stir continuously for 20 minutes to obtain a uniform reaction solution.

(2)将步骤(1)制备得到的反应液添加至100mL聚四氟乙烯内衬反应釜中,将预处理后的活性碳纤维倾斜地浸没在反应液中,密封后置于马弗炉中110℃下反应13h,反应结束,冷却至室温。取出块体,使用无水乙醇和去离子水分别交替洗涤三次,在鼓风干燥箱130℃下干燥活化6h,得活性碳纤维基MOF-303/Al-Fum(7/3)混合MOFs块体吸湿剂。(2) Add the reaction solution prepared in step (1) to a 100mL polytetrafluoroethylene-lined reactor, immerse the pretreated activated carbon fiber in the reaction solution obliquely, seal it and place it in a muffle furnace for 110 The reaction was carried out for 13 hours at ℃, and then the reaction was completed and cooled to room temperature. Take out the block, wash it three times alternately with absolute ethanol and deionized water, and dry and activate it in a blast drying oven at 130°C for 6 hours to obtain an activated carbon fiber-based MOF-303/Al-Fum (7/3) mixed MOFs block that absorbs moisture. agent.

实施例8Example 8

(1)室温及磁力搅拌下,取50mL烧杯,按照配体与Al3+的摩尔配比1:1,DMF与H2O体积比1:8,取0.269g(1.5mmol)3,5-吡唑二羧酸和0.175g(1.5mmol)富马酸溶于5mL DMF中形成双配体的DMF溶液;取1.14g(3mmol)Al(NO3)3·9H2O溶于40mL去离子水中形成Al(NO3)3的水溶液;将双配体的DMF溶液逐滴加入Al(NO3)3的水溶液中,持续搅拌20min得均匀反应液。(1) Under room temperature and magnetic stirring, take a 50mL beaker, according to the molar ratio of ligand to Al 3+ 1:1, the volume ratio of DMF to H 2 O 1:8, take 0.269g (1.5mmol) 3,5- Dissolve pyrazole dicarboxylic acid and 0.175g (1.5mmol) fumaric acid in 5mL DMF to form a double-ligand DMF solution; take 1.14g (3mmol) Al(NO 3 ) 3 ·9H 2 O and dissolve it in 40mL deionized water. An aqueous solution of Al(NO 3 ) 3 is formed; add the double-ligand DMF solution dropwise into the aqueous solution of Al(NO 3 ) 3 , and stir continuously for 20 minutes to obtain a uniform reaction solution.

(2)将步骤(1)制备得到的反应液添加至100mL聚四氟乙烯内衬反应釜中,将预处理后的活性碳纤维倾斜地浸没在反应液中,密封后置于马弗炉中120℃下反应12h,反应结束,冷却至室温。取出块体,使用无水乙醇和去离子水分别交替洗涤三次,在鼓风干燥箱150℃下干燥活化6h,得活性碳纤维基MOF-303/Al-Fum(5/5)混合MOFs块体吸湿剂。(2) Add the reaction liquid prepared in step (1) to a 100 mL polytetrafluoroethylene-lined reactor, immerse the pretreated activated carbon fiber in the reaction liquid obliquely, seal it and place it in a muffle furnace for 120 The reaction was carried out for 12 hours at ℃. After the reaction was completed, the mixture was cooled to room temperature. Take out the block, wash it three times alternately with absolute ethanol and deionized water, and dry and activate it in a blast drying oven at 150°C for 6 hours to obtain an activated carbon fiber-based MOF-303/Al-Fum (5/5) mixed MOFs block that absorbs moisture. agent.

实施例9Example 9

(1)室温及磁力搅拌下,取50mL烧杯,按照配体与Al3+的摩尔配比1:1.1,DMF与H2O体积比1:9,取0.162g(0.9mmol)3,5-吡唑二羧酸和0.245g(2.1mmol)富马酸溶于5mL DMF中形成双配体的DMF溶液;取1.254g(3mmol)Al(NO3)3·9H2O溶于50mL去离子水中形成Al(NO3)3的水溶液;将双配体的DMF溶液逐滴加入Al(NO3)3的水溶液中,持续搅拌20min得均匀反应液。(1) Under room temperature and magnetic stirring, take a 50mL beaker, according to the molar ratio of ligand to Al 3+ 1:1.1, the volume ratio of DMF to H 2 O 1:9, take 0.162g (0.9mmol) 3,5- Dissolve pyrazole dicarboxylic acid and 0.245g (2.1mmol) fumaric acid in 5mL DMF to form a double-ligand DMF solution; take 1.254g (3mmol) Al(NO 3 ) 3 ·9H 2 O and dissolve it in 50mL deionized water. An aqueous solution of Al(NO 3 ) 3 is formed; add the double-ligand DMF solution dropwise into the aqueous solution of Al(NO 3 ) 3 , and stir continuously for 20 minutes to obtain a uniform reaction solution.

(2)将步骤(1)制备得到的反应液添加至100mL聚四氟乙烯内衬反应釜中,将预处理后的活性碳纤维倾斜地浸没在反应液中,密封后置于马弗炉中130℃下反应11h,反应结束,冷却至室温。取出块体,使用无水乙醇和去离子水分别交替洗涤三次,在鼓风干燥箱100℃下干燥活化10h,得活性碳纤维基MOF-303/Al-Fum(3/7)混合MOFs块体吸湿剂。(2) Add the reaction solution prepared in step (1) to a 100mL polytetrafluoroethylene-lined reactor, immerse the pretreated activated carbon fiber in the reaction solution obliquely, seal it and place it in a muffle furnace for 130 The reaction was carried out for 11 hours at ℃, the reaction was completed, and the mixture was cooled to room temperature. Take out the block, wash it three times alternately with absolute ethanol and deionized water, and dry and activate it in a blast drying oven at 100°C for 10 hours to obtain an activated carbon fiber-based MOF-303/Al-Fum (3/7) mixed MOFs block that absorbs moisture. agent.

实施例10Example 10

(1)室温及磁力搅拌下,取50mL烧杯,按照配体与Al3+的摩尔配比1:1.25,DMF与H2O体积比1:10,取0.108g(0.6mmol)3,5-吡唑二羧酸和0.28g(2.4mmol)富马酸溶于5mL DMF中形成双配体的DMF溶液;取1.425g(3mmol)Al(NO3)3·9H2O溶于30mL去离子水中形成Al(NO3)3的水溶液;将双配体的DMF溶液逐滴加入Al(NO3)3的水溶液中,持续搅拌20min得均匀反应液。(1) Under room temperature and magnetic stirring, take a 50mL beaker, according to the molar ratio of ligand to Al 3+ 1:1.25, the volume ratio of DMF to H 2 O 1:10, take 0.108g (0.6mmol) 3,5- Dissolve pyrazole dicarboxylic acid and 0.28g (2.4mmol) fumaric acid in 5mL DMF to form a double-ligand DMF solution; take 1.425g (3mmol) Al(NO 3 ) 3 ·9H 2 O and dissolve it in 30mL deionized water. An aqueous solution of Al(NO 3 ) 3 is formed; add the double-ligand DMF solution dropwise into the aqueous solution of Al(NO 3 ) 3 , and stir continuously for 20 minutes to obtain a uniform reaction solution.

(2)将步骤(1)制备得到的反应液添加至100mL聚四氟乙烯内衬反应釜中,将预处理后的活性碳纤维倾斜地浸没在反应液中,密封后置于马弗炉中140℃下反应10h,反应结束,冷却至室温。取出块体,使用无水乙醇和去离子水分别交替洗涤三次,在鼓风干燥箱110℃下干燥活化8h,得活性碳纤维基MOF-303/Al-Fum(2/8)混合MOFs块体吸湿剂。(2) Add the reaction solution prepared in step (1) to a 100mL polytetrafluoroethylene-lined reactor, immerse the pretreated activated carbon fiber in the reaction solution obliquely, seal it and place it in a muffle furnace for 140 The reaction was carried out for 10 hours at ℃, the reaction was completed, and the mixture was cooled to room temperature. Take out the block, wash it three times alternately with absolute ethanol and deionized water, and dry and activate it in a blast drying oven at 110°C for 8 hours to obtain an activated carbon fiber-based MOF-303/Al-Fum (2/8) mixed MOFs block that absorbs moisture. agent.

测试条件及方法Test conditions and methods

块体吸湿剂(实施例)的负载量计算:Loading capacity calculation of bulk moisture absorbent (example):

设预处理后的活性碳纤维质量为m1,反应结束后经清洗和干燥后得到的活性碳纤维基MOFs块体吸湿剂质量为m2,则活性碳纤维基MOFs块体吸湿剂的负载量w为:Assume that the mass of the activated carbon fiber after pretreatment is m 1 and the mass of the activated carbon fiber-based MOFs bulk hygroscopic agent obtained after cleaning and drying after the reaction is m 2 , then the loading w of the activated carbon fiber-based MOFs bulk hygroscopic agent is:

X-射线衍射分析(XRD):X-ray diffraction analysis (XRD):

将所述的MOF-303粉末(比较例1)、MOF-303/Al-Fum混合MOFs粉末(比较例2)、活性碳纤维基MOF-303块体吸湿剂(实施例1)和活性碳纤维基MOF-303/Al-Fum混合MOFs块体吸湿剂(实施例8)研磨至粉末状,使用德国Bruker公司型号为D8 Advance的全自动X射线粉末衍射仪(XRD)对样品进行物相分析;测试条件为Cu靶,衍射角范围为5-60°,扫描速率为0.1秒/步,步长0.02°。The MOF-303 powder (Comparative Example 1), MOF-303/Al-Fum mixed MOFs powder (Comparative Example 2), activated carbon fiber-based MOF-303 bulk moisture absorber (Example 1) and activated carbon fiber-based MOF -303/Al-Fum mixed MOFs bulk hygroscopic agent (Example 8) was ground to powder, and a fully automatic X-ray powder diffractometer (XRD) model D8 Advance from Bruker Company of Germany was used to conduct phase analysis on the sample; test conditions It is a Cu target, the diffraction angle range is 5-60°, the scanning rate is 0.1 seconds/step, and the step size is 0.02°.

扫描电子显微镜(SEM):Scanning electron microscope (SEM):

采用日本Hitachi公司的SU8220型扫描电子显微镜(SEM)对预处理前后的活性碳纤维和活性碳纤维基MOF-303块体吸湿剂的表面形貌进行观察,在测试前对样品进行喷金处理,扫描电压5kV。The surface morphology of activated carbon fiber and activated carbon fiber-based MOF-303 bulk moisture absorbent before and after pretreatment was observed using the SU8220 scanning electron microscope (SEM) of Hitachi Company of Japan. The samples were sprayed with gold before testing, and the voltage was scanned. 5kV.

动态和静态等温水蒸气吸附曲线:Dynamic and static isothermal water vapor adsorption curves:

该测试采用可程式恒温恒湿试验箱和电子天平来分析MOF-303粉末(比较例1)、MOF-303/Al-Fum混合MOFs粉末(比较例2)、活性碳纤维基MOF-303块体吸湿剂(实施例1)和活性碳纤维基MOF-303/Al-Fum混合MOFs块体吸湿剂(实施例8)的动态和静态等温水蒸气吸附曲线。对于动态吸附,设置温度25℃,将样品置于恒温恒湿箱中在相对湿度30-90%范围内吸附至饱和后,取出并记录样品质量。对于静态吸附,将样品置于恒温恒湿箱(25℃,30%RH)中,每隔2min取出记录样品的质量变化,直至样品水吸附饱和(样品质量不在发生变化且稳定一段时间)。在测试之前样品放置于120℃烘箱中完全干燥。This test uses a programmable constant temperature and humidity test chamber and an electronic balance to analyze the moisture absorption of MOF-303 powder (Comparative Example 1), MOF-303/Al-Fum mixed MOFs powder (Comparative Example 2), and activated carbon fiber-based MOF-303 blocks. Dynamic and static isothermal water vapor adsorption curves of the agent (Example 1) and activated carbon fiber-based MOF-303/Al-Fum mixed MOFs bulk moisture absorbent (Example 8). For dynamic adsorption, set the temperature to 25°C, place the sample in a constant temperature and humidity box, and adsorb to saturation in the relative humidity range of 30-90%, then take out and record the sample mass. For static adsorption, place the sample in a constant temperature and humidity chamber (25°C, 30% RH), take out the sample every 2 minutes and record the mass change until the sample water adsorption is saturated (the sample mass no longer changes and is stable for a period of time). The samples were placed in a 120°C oven to dry completely before testing.

将测试之前干燥样品的质量记为M1,一定时刻下的样品质量记为M2,吸附饱和后的样品质量记为M3。则吸湿剂的吸附率R和饱和吸附率Rs可表示为The mass of the dried sample before the test is recorded as M 1 , the mass of the sample at a certain time is recorded as M 2 , and the mass of the sample after adsorption saturation is recorded as M 3 . Then the adsorption rate R and saturation adsorption rate R s of the hygroscopic agent can be expressed as

微分热重分析(DTG):Differential Thermogravimetry (DTG):

采用德国Netzsch公司的TG 209F3热重分析仪(TG)对比较例1和实施例1的脱附活化能进行分析。将升温速率分别设置为4℃/min、6℃/min、8℃/min、10℃/min、12℃/min,从室温升温至150℃。测量前,先将样品放置测试条件为25℃、90%RH的恒温恒湿箱中吸附至饱和。根据基辛格方程计算脱附活化能(Ed)。The desorption activation energy of Comparative Example 1 and Example 1 was analyzed using a TG 209F3 thermogravimetric analyzer (TG) from Netzsch Company of Germany. Set the heating rate to 4°C/min, 6°C/min, 8°C/min, 10°C/min, and 12°C/min, respectively, from room temperature to 150°C. Before measurement, the sample was first placed in a constant temperature and humidity chamber with test conditions of 25°C and 90% RH to adsorb to saturation. The desorption activation energy (E d ) was calculated according to the Kissinger equation.

其中,Ed为脱附活化能,单位为kJ·mol-1;R为气体常数,8.314J/(mol·K);T表示脱附温度(K);β为升温速率(℃/min),K为常数。Among them, E d is the desorption activation energy, the unit is kJ·mol -1 ; R is the gas constant, 8.314J/(mol·K); T represents the desorption temperature (K); β is the heating rate (℃/min) , K is a constant.

UV-vis-NIR光吸收:UV-vis-NIR light absorption:

使用UV-vis-NIR漫反射仪(Lambda 750S,PerkinElmer,美国)在200-2500nm范围内记录活性碳纤维、MOF-303粉末(比较例1)和块体吸湿剂(实施例)的反射光谱,分析其光吸收性能。A UV-vis-NIR diffuse reflectometer (Lambda 750S, PerkinElmer, USA) was used to record the reflection spectra of activated carbon fiber, MOF-303 powder (Comparative Example 1) and bulk hygroscopic agent (Example) in the range of 200-2500nm, and analyze Its light absorption properties.

热成像分析:Thermal imaging analysis:

使用热成像相机记录了模拟太阳光照射下MOF-303粉末(比较例1)和块体吸湿剂(实施例)的表面温度随时间的变化。A thermal imaging camera was used to record the surface temperature changes with time of MOF-303 powder (Comparative Example 1) and bulk hygroscopic agent (Example) under simulated sunlight irradiation.

图1为比较例(1、2)和实施例(1、8)制备得到的吸湿剂的XRD谱。从图1可以得出,混合溶剂热法原位合成制备的活性碳纤维基MOFs块体吸湿剂(实施例1、8)的XRD衍射峰位置分别与MOFs粉末(比较例1、2)保持一致,证明采用混合溶剂热法能将MOF-303成功地负载在活性碳纤维基材上,没有改变其晶型结构。Figure 1 is the XRD spectrum of the hygroscopic agents prepared in Comparative Examples (1, 2) and Examples (1, 8). It can be concluded from Figure 1 that the XRD diffraction peak positions of the activated carbon fiber-based MOFs bulk hygroscopic agent (Examples 1 and 8) synthesized in situ by the mixed solvothermal method are consistent with those of the MOFs powder (Comparative Examples 1 and 2). It is proved that the mixed solvothermal method can be used to successfully load MOF-303 on the activated carbon fiber substrate without changing its crystal structure.

图2为改性前、改性后(放大倍数分别为1k和5k)的活性碳纤维和实施例1(放大倍数分别为2k和5k)制备的活性碳纤维基MOF-303块体吸湿剂的SEM图。从图2可以看出,未改性的活性碳纤维为光滑纤维棒状,其内部存在着大量的孔道,为MOF-303颗粒提供了着位点;预处理后的活性碳纤维棒上负载着壳聚糖颗粒,增强了活性碳纤维的亲水性和与MOF-303颗粒之间的作用力;MOF-303晶体负载在活性碳纤维棒上,呈正方体型,说明成功制备了MOF-303块体吸湿剂。Figure 2 is an SEM image of the activated carbon fiber before and after modification (magnification: 1k and 5k, respectively) and the activated carbon fiber-based MOF-303 bulk moisture absorbent prepared in Example 1 (magnification: 2k and 5k, respectively) . As can be seen from Figure 2, the unmodified activated carbon fiber is in the shape of a smooth fiber rod with a large number of pores inside it, which provides attachment sites for MOF-303 particles; the pretreated activated carbon fiber rod is loaded with chitosan particles, which enhances the hydrophilicity of the activated carbon fiber and the interaction force with the MOF-303 particles; the MOF-303 crystals are loaded on the activated carbon fiber rods and appear in a cube shape, indicating that the MOF-303 bulk hygroscopic agent has been successfully prepared.

图3为比较例1和实施例1制备得到的吸湿剂的动态水吸附曲线。结果表明,所述活性碳纤维基MOF-303块体吸湿剂(实施例1)与MOF-303粉末(比较例)保持一致的吸附行为,在低湿条件下(30%RH)具有较高的水吸附量,分别为0.23g/g和0.32g/g。Figure 3 shows the dynamic water adsorption curves of the hygroscopic agents prepared in Comparative Example 1 and Example 1. The results show that the activated carbon fiber-based MOF-303 bulk hygroscopic agent (Example 1) maintains consistent adsorption behavior with MOF-303 powder (Comparative Example), and has higher water adsorption under low humidity conditions (30% RH) The amounts are 0.23g/g and 0.32g/g respectively.

图4为实施例6-10制备得到的吸湿剂的动态水吸附曲线。结果表明,通过改变配体的含量可调控MOFs水吸附等温线,使其应用于更多场合。实施例都具有较高的水吸附量,最佳配体为5/5即实施例8,其在30%RH、60%RH和90%RH的吸湿量分别是0.16g/g、0.23g/g和0.28g/g。Figure 4 is a dynamic water adsorption curve of the hygroscopic agent prepared in Examples 6-10. The results show that the water adsorption isotherm of MOFs can be adjusted by changing the ligand content, making it applicable to more applications. The examples all have higher water adsorption capacity. The best ligand is 5/5, that is, Example 8. Its moisture absorption capacity at 30% RH, 60% RH and 90% RH is 0.16g/g and 0.23g/g respectively. g and 0.28g/g.

图5为比较例1和实施例1、8制备得到的吸湿剂的静态水吸附曲线(25℃,30%RH)。结果表明,所制备的吸湿剂在30min内都达到了吸附饱和,具有快速的水吸附速率。Figure 5 is the static water adsorption curve (25°C, 30% RH) of the hygroscopic agents prepared in Comparative Example 1 and Examples 1 and 8. The results show that the prepared hygroscopic agent reaches adsorption saturation within 30 minutes and has a rapid water adsorption rate.

图6为未改性活性碳纤维基材、比较例和实施例在200-2500nm波长范围内的光吸收曲线。结果表明,实施例在紫外、可见光和近红外波长范围内都表现出优于比较例的光吸收能力,说明将MOFs载体化可增强块体吸湿剂的光吸收能力。Figure 6 shows the light absorption curves of the unmodified activated carbon fiber substrate, comparative examples and examples in the wavelength range of 200-2500 nm. The results show that the examples show better light absorption capabilities than the comparative examples in the ultraviolet, visible and near-infrared wavelength ranges, indicating that carrier-based MOFs can enhance the light absorption capabilities of the bulk hygroscopic agent.

图7为模拟一个太阳光照射下比较例1和实施例1的表面温度随时间的变化曲线。结果表明,比较例1的表面温度上升得比较缓慢,最高峰温度为41.2℃;实施例1在1min内温度从室温快速上升到55℃,随后保持一定速率上升,在30min内温度趋于稳定,最高峰温度达87.6℃,峰温度是比较例1的2倍。这意味着活性碳纤维赋予了块体吸湿剂强的光热转换能力,可实现太阳光驱动解吸水,从而降低能耗。Figure 7 is a simulated surface temperature change curve with time of Comparative Example 1 and Example 1 under sunlight irradiation. The results show that the surface temperature of Comparative Example 1 rises relatively slowly, with the highest peak temperature being 41.2°C; in Example 1, the temperature rises rapidly from room temperature to 55°C within 1 minute, and then maintains a certain rate of increase, and the temperature stabilizes within 30 minutes. The highest peak temperature reached 87.6°C, which was twice that of Comparative Example 1. This means that the activated carbon fiber gives the bulk hygroscopic agent strong light-to-heat conversion ability, which can realize solar-driven desorption of water, thereby reducing energy consumption.

表1Table 1

表1为实施例1-10制备得到的活性碳纤维基MOFs块体吸湿剂的负载量。可以看出,混合溶剂热原位合成的活性碳纤维基MOFs块体吸湿剂都具有较高的负载量,并以实施例1最高70.49%。Table 1 shows the loading capacity of the activated carbon fiber-based MOFs bulk moisture absorbent prepared in Examples 1-10. It can be seen that the activated carbon fiber-based MOFs bulk moisture absorbent synthesized by mixed solvothermal in situ all has a higher loading capacity, with the highest loading capacity of 70.49% in Example 1.

表2Table 2

表2为实施例1与比较例1制备得到的吸湿剂在不同升温速率下的脱附峰温(T)以及对应的脱附活化能(Ed)。通过对比可知,在相同的升温速率下,活性碳纤维基MOF-303块体吸湿剂(实施例1)的脱附峰温远低于MOF-303粉末(比较例1)的脱附峰温,表明活性碳纤维基材可以有效提高吸湿剂传热传质速率。同时,块体吸湿剂在不同升温速率下的脱附峰温都低于模拟太阳光照射下的峰温度(图5),验证了太阳光驱动水解吸的可行性。通过Kissinger方程计算,活性碳纤维基MOF-303块体吸湿剂(实施例1)和MOF-303粉末吸湿剂(比较例1)的脱附活化能分别为56.99kJ/mol和67.11kJ/mol,说明前者脱附需要更低的能耗,进一步表明将MOF载体化是实现节能脱附的有效途径。Table 2 shows the desorption peak temperatures (T) and corresponding desorption activation energies (E d ) of the hygroscopic agents prepared in Example 1 and Comparative Example 1 at different heating rates. By comparison, it can be seen that at the same heating rate, the desorption peak temperature of activated carbon fiber-based MOF-303 bulk moisture absorbent (Example 1) is much lower than that of MOF-303 powder (Comparative Example 1), indicating that The activated carbon fiber substrate can effectively improve the heat and mass transfer rate of the hygroscopic agent. At the same time, the desorption peak temperature of the bulk hygroscopic agent at different heating rates is lower than the peak temperature under simulated sunlight irradiation (Figure 5), which verifies the feasibility of sunlight-driven water desorption. Calculated by the Kissinger equation, the desorption activation energies of activated carbon fiber-based MOF-303 bulk moisture absorbent (Example 1) and MOF-303 powder moisture absorbent (Comparative Example 1) are 56.99kJ/mol and 67.11kJ/mol respectively, indicating The former requires lower energy consumption for desorption, further indicating that carrierizing MOF is an effective way to achieve energy-saving desorption.

以上实施例仅为本发明较优的实施方式,仅用于解释本发明,而非限制本发明,本领域技术人员在未脱离本发明精神实质下所作的改变、替换、修饰等均应属于本发明的保护范围。The above embodiments are only preferred embodiments of the present invention and are only used to explain the present invention rather than limit the present invention. Changes, substitutions, modifications, etc. made by those skilled in the art without departing from the spirit and essence of the present invention shall all belong to this invention. protection scope of the invention.

Claims (10)

1.一种活性碳纤维基MOFs块体吸湿剂及其混合溶剂热原位合成方法,其特征在于,具体步骤如下:1. An activated carbon fiber-based MOFs bulk hygroscopic agent and its mixed solvent thermal in-situ synthesis method, which is characterized in that the specific steps are as follows: (1)活性碳纤维的亲水改性处理:将活性碳纤维浸入氧化剂中活化,再将其浸入到含亲水改性成膜材料的水溶液中,充分浸润后,清洗并烘干得亲水改性活性碳纤维;(1) Hydrophilic modification treatment of activated carbon fiber: Dip the activated carbon fiber into an oxidant for activation, and then immerse it into an aqueous solution containing hydrophilic modified film-forming materials. After sufficient infiltration, clean and dry to obtain hydrophilic modification. activated carbon fiber; (2)反应液的配制:搅拌条件下,将有机二元羧酸的N,N-二甲基甲酰胺溶液和铝盐水溶液混合得均匀反应液;(2) Preparation of the reaction solution: Under stirring conditions, mix the N,N-dimethylformamide solution of the organic dicarboxylic acid and the aluminum salt solution to obtain a uniform reaction solution; (3)MOFs块体吸湿剂混合溶剂热原位合成:将改性活性碳纤维浸没于反应液中进行晶化反应,反应结束后将负载MOFs涂层的活性碳纤维取出、洗涤并烘干后得活性碳纤维基MOFs块体吸湿剂。(3) MOFs bulk hygroscopic agent mixed solvent thermal in-situ synthesis: immerse the modified activated carbon fiber in the reaction solution for crystallization reaction. After the reaction, take out the activated carbon fiber loaded with MOFs coating, wash and dry to obtain the activity Carbon fiber-based MOFs bulk moisture absorber. 2.根据权利要求1所述的一种活性碳纤维基MOFs块体吸湿剂混合溶剂热原位合成方法,其特征在于,步骤(1)所述氧化剂包括浓硫酸、浓硝酸、过氧化氢、高锰酸钾和浓硫酸及浓硝酸混合物(v/v:1/1)中的一种。2. A kind of activated carbon fiber-based MOFs bulk hygroscopic agent mixed solvent thermal in-situ synthesis method according to claim 1, characterized in that the oxidant in step (1) includes concentrated sulfuric acid, concentrated nitric acid, hydrogen peroxide, high One of the mixtures of potassium manganate, concentrated sulfuric acid and concentrated nitric acid (v/v: 1/1). 3.根据权利要求1所述的一种活性碳纤维基MOFs块体吸湿剂混合溶剂热原位合成方法,其特征在于,步骤(1)所述亲水改性成膜材料包括壳聚糖季铵盐、壳聚糖盐酸盐、羧甲基壳聚糖、壳寡糖中的一种。3. A kind of activated carbon fiber-based MOFs bulk hygroscopic agent mixed solvent thermal in-situ synthesis method according to claim 1, characterized in that the hydrophilic modified film-forming material in step (1) includes chitosan quaternary ammonium One of salt, chitosan hydrochloride, carboxymethyl chitosan, and chitosan oligosaccharide. 4.根据权利要求1所述的一种活性碳纤维基MOFs块体吸湿剂混合溶剂热原位合成方法,其特征在于,步骤(2)所述有机二元羧酸包括3,5-吡唑二羧酸、富马酸、2,5-呋喃二甲酸和间苯二甲酸中的一种或两种。4. A kind of activated carbon fiber-based MOFs bulk hygroscopic agent mixed solvent thermal in-situ synthesis method according to claim 1, characterized in that the organic dicarboxylic acid in step (2) includes 3,5-pyrazole bis One or two of carboxylic acid, fumaric acid, 2,5-furandicarboxylic acid and isophthalic acid. 5.根据权利要求1所述的一种活性碳纤维基MOFs块体吸湿剂混合溶剂热原位合成方法,其特征在于,步骤(2)所述铝盐为九水合硝酸铝、十八水合硫酸铝、六水氯化铝、乙酸铝中的一种。5. A kind of activated carbon fiber-based MOFs bulk hygroscopic agent mixed solvent thermal in-situ synthesis method according to claim 1, characterized in that the aluminum salt in step (2) is aluminum nitrate nonahydrate, aluminum sulfate octahydrate , one of aluminum chloride hexahydrate and aluminum acetate. 6.根据权利要求1所述的一种活性碳纤维基MOFs块体吸湿剂混合溶剂热原位合成方法,其特征在于,步骤(2)所述有机二元羧酸与铝盐水溶液中铝离子摩尔配比为1:0.8~1.25。6. A kind of activated carbon fiber-based MOFs bulk hygroscopic agent mixed solvent thermal in-situ synthesis method according to claim 1, characterized in that the mole of aluminum ions in the organic dicarboxylic acid and aluminum salt solution in step (2) The ratio is 1:0.8~1.25. 7.根据权利要求1所述的一种活性碳纤维基MOFs体吸湿剂混合溶剂热原位合成方法,其特征在于,步骤(2)所述N,N-二甲基甲酰胺与铝盐水溶液中的水的体积比为1:5~10。7. A kind of activated carbon fiber-based MOFs bulk hygroscopic agent mixed solvent thermal in-situ synthesis method according to claim 1, characterized in that, in the N, N-dimethylformamide and aluminum aqueous solution in step (2) The volume ratio of water is 1:5~10. 8.根据权利要求1所述的一种活性碳纤维基MOFs体吸湿剂混合溶剂热原位合成方法,其特征在于,步骤(3)所述晶化反应的温度为80~120℃;步骤(3)所述晶化反应的时间为10~14h;步骤(3)所述洗涤为使用乙醇和去离子水交替分别洗涤3次;步骤(3)所述的活化温度为100~150℃;活化时间为6~10h。8. A thermal in-situ synthesis method of activated carbon fiber-based MOFs bulk hygroscopic agent mixed solvent according to claim 1, characterized in that the temperature of the crystallization reaction in step (3) is 80-120°C; step (3) ) The crystallization reaction time is 10 to 14 hours; the washing in step (3) is to wash 3 times with ethanol and deionized water alternately; the activation temperature in step (3) is 100 to 150°C; the activation time It is 6~10h. 9.权利要求1-8任一项所述的一种活性碳纤维基MOFs块体吸湿剂及其混合溶剂热原位合成方法合成得到的一种活性碳纤维基MOFs块体吸湿剂。9. An activated carbon fiber-based MOFs bulk hygroscopic agent according to any one of claims 1 to 8 and an activated carbon fiber-based MOFs bulk hygroscopic agent synthesized by a mixed solvent thermal in-situ synthesis method. 10.权利要求9所述的一种活性碳纤维基MOFs块体吸湿剂在在干旱地区太阳能辅助驱动的大气集水领域中的应用。10. The application of an activated carbon fiber-based MOFs bulk hygroscopic agent according to claim 9 in the field of solar-assisted atmospheric water collection in arid areas.
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