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CN104437394B - Dual-layer high-amino density plant fiber-based adsorption material and preparation method and application thereof - Google Patents

Dual-layer high-amino density plant fiber-based adsorption material and preparation method and application thereof Download PDF

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CN104437394B
CN104437394B CN201410580406.1A CN201410580406A CN104437394B CN 104437394 B CN104437394 B CN 104437394B CN 201410580406 A CN201410580406 A CN 201410580406A CN 104437394 B CN104437394 B CN 104437394B
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陈水挟
罗时荷
何辉
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Sun Yat Sen University
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Abstract

本发明公开了一种双层高氨基密度的植物纤维基吸附材料及其制备方法和应用。该双层高氨基密度植物纤维基吸附材料是以植物纤维为基体,具体为甘蔗渣、笋粉、玉米芯粉、剑麻、秸秆或棉纤维等,经过碱预处理、接枝反应、胺化反应、加成反应、PEI酰胺取代反应制备得到。本发明的纤维基吸附材料具有高的热稳定性、化学稳定性。该吸附材料对酸性气体具有高的吸附容量和良好的吸附捕集性能,可用于烟道气中CO2的吸附捕集领域。同时该材料也具有良好的抗菌性能,可应用于木塑材料领域,防止木纤维的霉变,在其它抗菌领域也具有良好的应用前景。而且该吸附材料在吸附气体后,可经过热脱附再生,是一种可循环再生吸附材料。

The invention discloses a double-layer high amino density plant fiber-based adsorption material as well as a preparation method and application thereof. The double-layer high amino density plant fiber-based adsorption material is based on plant fiber, specifically bagasse, bamboo shoot powder, corncob powder, sisal hemp, straw or cotton fiber, etc., after alkali pretreatment, grafting reaction, amination Reaction, addition reaction, PEI amide substitution reaction to prepare. The fiber-based adsorption material of the present invention has high thermal stability and chemical stability. The adsorption material has high adsorption capacity and good adsorption and capture performance for acid gas, and can be used in the field of adsorption and capture of CO2 in flue gas. At the same time, the material also has good antibacterial properties and can be applied in the field of wood-plastic materials to prevent mildew of wood fibers, and has good application prospects in other antibacterial fields. Moreover, after the adsorption material absorbs gas, it can be regenerated by thermal desorption, which is a recyclable and regenerated adsorption material.

Description

一种双层高氨基密度植物纤维基吸附材料及其制备方法和 应用A double-layer high amino density plant fiber-based adsorption material and its preparation method and application

技术领域technical field

本发明属于吸附材料技术领域。更具体地,涉及一种双层高氨基密度植物纤维基吸附材料及其制备方法和应用。The invention belongs to the technical field of adsorption materials. More specifically, it relates to a double-layer high amino density plant fiber-based adsorption material and its preparation method and application.

背景技术Background technique

温室效应已成为人类面临的最严重的环境问题之一。作为温室气体的主要组成,CO2在大气中的含量越来越高,这也使得CO2的减排成为了本领域研究的重点,CO2的捕获与封存技术(CCS)近年来成为国际上研究的热点课题。作为分离和富集CO2的固态吸附剂之一,固态胺吸附剂对CO2具有高选择性,并且不易受水或其他气体的干扰,可在比较宽的温度范围和压力范围内用于CO2的富集。而以纤维为基体的固态胺纤维,拥有高吸附容量、循环再生性能优异、原料来源广泛等优点,在气体分离领域有着广泛的应用前景。The greenhouse effect has become one of the most serious environmental problems faced by human beings. As the main component of greenhouse gases, the content of CO 2 in the atmosphere is getting higher and higher, which also makes the reduction of CO 2 emissions become the focus of research in this field. CO 2 capture and storage technology (CCS) has become an international hot topic of research. As one of the solid-state adsorbents for separating and enriching CO2 , solid-state amine adsorbent has high selectivity for CO2 and is not easily disturbed by water or other gases, and can be used for CO2 in a relatively wide temperature range and pressure range 2 enrichment. The solid amine fiber based on fiber has the advantages of high adsorption capacity, excellent recycling performance, and wide source of raw materials, and has broad application prospects in the field of gas separation.

对于改性的固态胺吸附剂而言,吸附剂具有不同碱性,且吸附容量和氨基利用率随着碱度的降低而减少。由此可见材料的碱度对对其吸附性能起到决定性作用:一方面,碱性的增加有利于材料吸附容量的提高;另一方面,碱性越低的材料,其脱附速率越快。也就是说在相同吸附条件下,含有伯胺的固态胺吸附材料对CO2快的吸附速率和较高吸附容量,但脱附就变得比仲胺及叔胺困难。因此可以通过在基体上同时负载多种功能胺基试剂来提高材料的吸附容量,其中,负载高分子量胺基化合物如PEI的固态胺吸附材料,氨基密度高,可以有效提高材料的吸附性能,但它的吸附性能可能受到PEI分子链的平均尺寸、支化度等的影响。这主要是由于聚合物分子链越长,制备过程中易抱团存在,就越难分散到基体中;支化度越大,CO2在吸附材料上的扩散和传质阻力也越大。因此,在同一基体上且负载量相同的情况下,负载了PEI所得吸附材料的吸附容量和氨基效率可能不如负载TEPA的吸附材料。如何在保证高的氨基密度的同时,不降低氨基效率和吸附容量,则变的尤为重要。For the modified solid amine adsorbents, the adsorbents have different basicity, and the adsorption capacity and amino group utilization rate decrease with the decrease of basicity. It can be seen that the alkalinity of the material plays a decisive role in its adsorption performance: on the one hand, the increase of alkalinity is beneficial to the improvement of the adsorption capacity of the material; on the other hand, the lower the alkalinity of the material, the faster the desorption rate. That is to say, under the same adsorption conditions, solid amine adsorption materials containing primary amines have a faster adsorption rate and higher adsorption capacity for CO2 , but desorption becomes more difficult than secondary and tertiary amines. Therefore, the adsorption capacity of the material can be improved by loading multiple functional amine-based reagents on the substrate at the same time. Among them, the solid-state amine adsorption material loaded with high-molecular-weight amine-based compounds such as PEI has a high amino density and can effectively improve the adsorption performance of the material. Its adsorption performance may be affected by the average size, branching degree, etc. of PEI molecular chains. This is mainly due to the fact that the longer the polymer molecular chain is, the easier it is to form clusters during the preparation process, and the more difficult it is to disperse into the matrix; the greater the degree of branching, the greater the diffusion and mass transfer resistance of CO2 on the adsorption material. Therefore, under the same substrate and the same loading capacity, the adsorption capacity and amino group efficiency of the adsorbents loaded with PEI may not be as good as those loaded with TEPA. How to ensure high amino density without reducing amino efficiency and adsorption capacity becomes particularly important.

另一方面,我国属于农业大国,每年都有大量的农业废弃物亟待处理回收。在这些农业废弃物中,包含大量的纤维素纤维,这些天然的纤维素纤维与其他合成纤维相比,具有来源广泛、价格低廉、密度小、可降解回收等特点。不仅如此,这些纤维素纤维由于表面粗糙、物、化结构的不均一性,可望用于各种吸附材料领域。近年来,也有大量的研究将其应用于印染工业、重金属离子吸附、工业废水处理等领域。目前未见有将这些植物纤维应用于温室气体吸附的研究和报道。On the other hand, my country is a large agricultural country, and there is a large amount of agricultural waste that needs to be processed and recycled every year. These agricultural wastes contain a large amount of cellulose fibers. Compared with other synthetic fibers, these natural cellulose fibers have the characteristics of wide sources, low price, low density, and degradable recycling. Not only that, these cellulose fibers are expected to be used in various fields of adsorption materials due to their rough surface and heterogeneity of physical and chemical structures. In recent years, a large number of studies have applied it to the fields of printing and dyeing industry, heavy metal ion adsorption, and industrial wastewater treatment. At present, there are no studies and reports on the application of these plant fibers to the adsorption of greenhouse gases.

发明内容Contents of the invention

本发明要解决的技术问题是克服现有CO2等气体吸附技术的不足,提供一种以植物纤维作为基体制备的双层高氨基密度的植物纤维基吸附材料,实现对农业废弃物的充分、合理利用,降低目前吸附剂领域成本高、原料来源少等不足,并在有限的基体上通过接枝、胺化等步骤,提高氨基密度,有效提高材料对CO2等酸性气体的吸附性能,实现此类双层高氨基密度植物纤维基吸附材料在吸附领域的高效应用。The technical problem to be solved in the present invention is to overcome the deficiencies of the existing gas adsorption technologies such as CO2 , and provide a double-layer high amino density plant fiber-based adsorption material prepared with plant fibers as a matrix, so as to realize the full and efficient absorption of agricultural waste. Reasonable utilization can reduce the shortcomings of high cost and few sources of raw materials in the field of adsorbents, and increase the density of amino groups through steps such as grafting and amination on a limited substrate, effectively improving the adsorption performance of materials for acid gases such as CO 2 , and realizing Efficient application of this kind of double-layer high amino density plant fiber-based adsorption material in the field of adsorption.

本发明另一目的是提供上述双层高氨基密度的植物纤维基吸附材料的制备方法。Another object of the present invention is to provide a method for preparing the above-mentioned double-layer high amino density plant fiber-based adsorption material.

本发明再一目的是提供上述双层高氨基密度的植物纤维基吸附材料的应用。Another object of the present invention is to provide the application of the above-mentioned double-layer high amino density plant fiber-based adsorption material.

本发明上述目的通过以下技术方案实现:The above object of the present invention is achieved through the following technical solutions:

本发明提供了一种双层高氨基密度植物纤维基吸附材料,是以植物纤维为基体,依次经过碱预处理、接枝反应、胺化反应、加成反应、PEI酰胺取代反应制备得到。该吸附材料的热分解温度在300℃以上,具有优异的酸性气体吸附捕集性能和优异的抗菌性能;该吸附材料在吸附气体后,可经过热脱附再生,循环再生10次后,对二氧化碳和/或二氧化硫的解析率仍然可达90%以上,再生效率在93%以上。The invention provides a double-layer high amino density plant fiber-based adsorption material, which is prepared by taking the plant fiber as a matrix and sequentially undergoing alkali pretreatment, grafting reaction, amination reaction, addition reaction and PEI amide substitution reaction. The thermal decomposition temperature of the adsorption material is above 300°C, and it has excellent acid gas adsorption and capture performance and excellent antibacterial performance; And/or the resolution rate of sulfur dioxide can still reach more than 90%, and the regeneration efficiency is more than 93%.

其中,优选地,所述植物纤维为甘蔗渣、笋粉、玉米芯粉、剑麻、秸秆或棉纤维。植物纤维表面具有大量的羟基反应基团,可进一步进行功能化。Wherein, preferably, the plant fiber is bagasse, bamboo shoot powder, corncob powder, sisal hemp, straw or cotton fiber. There are a large number of hydroxyl reactive groups on the surface of plant fibers, which can be further functionalized.

本发明还通过了一种上述双层高氨基密度植物纤维基吸附材料的制备方法,步骤如下:The present invention also adopts a method for preparing the above-mentioned double-layer high amino density plant fiber-based adsorption material, the steps are as follows:

S1.碱预处理:将植物纤维置于NaOH水溶液中超声震荡处理,烘干;S1. Alkali pretreatment: place the plant fibers in NaOH aqueous solution for ultrasonic vibration treatment, and dry;

S2.接枝反应:将碱预处理后植物纤维与不饱和接枝单体溶液混匀,再加入引发剂H2O2和硫酸亚铁胺溶液,进行接枝反应,得到接枝纤维;S2. Grafting reaction: mix the plant fiber after the alkali pretreatment with the unsaturated grafting monomer solution, then add the initiator H 2 O 2 and ferrous amine sulfate solution, and carry out the grafting reaction to obtain the grafted fiber;

S3.胺化反应:在接枝纤维中加入多胺,进行胺化反应,得到单层氨基植物纤维基材料;S3. Amination reaction: adding polyamine to the grafted fibers for amination reaction to obtain a single-layer amino plant fiber-based material;

S4.加成反应:将单层氨基植物纤维基材料与不饱和接枝单体溶液混合,超声处理后,进行加成反应(Michael加成反应),得到加成后的单层氨基植物纤维基材料;S4. Addition reaction: Mix the single-layer amino plant fiber-based material with the unsaturated graft monomer solution, and perform an addition reaction (Michael addition reaction) after ultrasonic treatment to obtain the added single-layer amino plant fiber base Material;

S5.PEI酰胺取代反应:将加成后的单层氨基植物纤维基材料与聚乙烯亚胺(PEI)混合,进行酰胺取代反应,得双层高氨基密度植物纤维基吸附材料。S5. PEI amide substitution reaction: Mix the added single-layer amino plant fiber-based material with polyethyleneimine (PEI) for amide substitution reaction to obtain a double-layer high amino density plant fiber-based adsorption material.

优选地,步骤S1所述碱预处理具体是:Preferably, the alkali pretreatment described in step S1 is specifically:

S11.将植物纤维置于10~20wt% NaOH水溶液中,100~400W超声震荡处理1~2h;S11. placing the plant fiber in 10-20wt% NaOH aqueous solution, and treating it with 100-400W ultrasonic vibration for 1-2 hours;

S12.超声处理后,于50℃浸泡10~24h;S12. After ultrasonic treatment, soak at 50°C for 10-24 hours;

S13.倾去溶液,所得纤维用水洗涤多次至中性,60℃烘干。S13. Pour off the solution, wash the obtained fiber several times with water until neutral, and dry at 60°C.

所述植物纤维为甘蔗渣、笋粉、玉米芯粉、剑麻、秸秆或棉纤维。The plant fiber is bagasse, bamboo shoot powder, corn cob powder, sisal hemp, straw or cotton fiber.

优选地,步骤S2所述接枝反应具体是:Preferably, the grafting reaction described in step S2 is specifically:

S21.按照碱预处理后植物纤维的重量与不饱和接枝单体溶液的体积的比例为1:10~1:50,将两者混匀;所述不饱和接枝单体溶液的浓度为2~20wt%;S21. According to the ratio of the weight of the plant fiber after the alkali pretreatment to the volume of the unsaturated graft monomer solution is 1:10~1:50, the two are mixed; the concentration of the unsaturated graft monomer solution is 2~20wt%;

S22.按照H2O2与不饱和接枝单体溶液的体积比为0.2:100~2:100,向S21混匀后的溶液中加入引发剂H2O2S22. According to the volume ratio of H 2 O 2 to the unsaturated graft monomer solution is 0.2:100 to 2:100, add initiator H 2 O 2 to the solution mixed in S21;

S23.按照硫酸亚铁胺溶液与不饱和接枝单体溶液的体积比为1:5,向S22处理后的溶液中加入硫酸亚铁胺溶液;所述硫酸亚铁胺的浓度为1×10-3~1×10-1g/mL;S23. According to the volume ratio of ferrous amine sulfate solution and unsaturated graft monomer solution is 1:5, add ferrous amine sulfate solution in the solution after S22 treatment; The concentration of described ferrous amine sulfate is 1×10 -3 ~1×10 -1 g/mL;

S24.在30~80℃条件下反应1~24h后,用乙醇浸洗抽滤2~5次,再用水浸洗抽滤2~5次,除去均聚物,60℃真空烘干,得到接枝纤维。S24. After reacting for 1 to 24 hours at 30 to 80°C, soak and filter with ethanol for 2 to 5 times, then wash and filter with water for 2 to 5 times to remove the homopolymer, and dry in vacuum at 60°C to obtain the stick fibers.

优选地,步骤S3所述胺化反应具体是:Preferably, the amination reaction described in step S3 is specifically:

S31.按照多胺与接枝纤维的重量比为2:1~100:1,在接枝纤维中加入多胺;S31. According to the weight ratio of polyamine to graft fiber is 2:1~100:1, add polyamine to graft fiber;

S32.在100~150℃条件下反应6~10h,用水浸洗多次(2~5次),最后用乙醇冲洗,抽滤,60℃烘干,得到单层氨基植物纤维基材料。S32. React at 100-150°C for 6-10 hours, soak with water for several times (2-5 times), finally rinse with ethanol, filter with suction, and dry at 60°C to obtain a single-layer amino plant fiber-based material.

优选地,步骤S4所述加成反应具体是:Preferably, the addition reaction described in step S4 is specifically:

S41.按照单层氨基植物纤维基材料的重量与不饱和接枝单体溶液的体积的比例为1:10~1:60,将两者混合,所述不饱和接枝单体溶液的浓度为5~50wt%;S41. According to the ratio of the weight of the single-layer amino plant fiber-based material to the volume of the unsaturated graft monomer solution is 1:10~1:60, the two are mixed, and the concentration of the unsaturated graft monomer solution is 5~50wt%;

S42.于100~400W超声条件下处理1~2h后,在10~60℃水浴中继续反应1~24h,使纤维发生迈克尔加成反应(Michael加成反应);S42. After treating for 1-2 hours under 100-400W ultrasonic conditions, continue to react in a 10-60°C water bath for 1-24 hours, so that the fibers undergo Michael addition reaction (Michael addition reaction);

S43.用水浸洗多次(2~5次),最后用乙醇冲洗,抽滤,60℃烘干,得到加成后的单层氨基植物纤维基材料。S43. Soak and wash with water for several times (2-5 times), finally rinse with ethanol, filter with suction, and dry at 60°C to obtain a single-layer amino plant fiber-based material after addition.

优选地,步骤S5所述PEI酰胺取代反应具体是:Preferably, the PEI amide substitution reaction described in step S5 is specifically:

S51.按照加成后的单层氨基植物纤维基材料的重量与聚乙烯亚胺(PEI)的体积的比例为1:5~1:60,将两者混合,所述聚乙烯亚胺的浓度为5~15wt%;S51. According to the ratio of the weight of the added single-layer amino plant fiber-based material to the volume of polyethyleneimine (PEI) is 1:5 to 1:60, mix the two, and the concentration of polyethyleneimine 5~15wt%;

S52.在20~60℃反应10~48h,使纤维与聚乙烯亚胺进行酰胺取代反应;S52. Reacting at 20-60° C. for 10-48 hours, so that the fiber and polyethyleneimine undergo an amide substitution reaction;

S53.乙醇洗涤除去多余的聚乙烯亚胺,抽滤,60℃烘干,得双层高氨基密度植物纤维基吸附材料。S53. Wash with ethanol to remove excess polyethyleneimine, filter with suction, and dry at 60°C to obtain a double-layer high amino density plant fiber-based adsorption material.

另外,优选地,上述的不饱和接枝单体溶液为:丙烯酰胺溶液、丙烯酸甲酯溶液、丙烯腈溶液、丙烯酸溶液或甲基丙烯酸缩水甘油酯溶液。In addition, preferably, the above-mentioned unsaturated grafting monomer solution is: acrylamide solution, methyl acrylate solution, acrylonitrile solution, acrylic acid solution or glycidyl methacrylate solution.

上述的多胺为乙二胺、二乙胺、二乙烯三胺、三乙烯四胺、四乙烯五胺或五乙烯六胺。The aforementioned polyamines are ethylenediamine, diethylamine, diethylenetriamine, triethylenetetramine, tetraethylenepentamine or pentaethylenehexamine.

本发明还提供上述双层高氨基密度植物纤维基吸附材料在吸附酸性气体方面的应用,尤其是应用于CO2和/或SO2的吸附。The present invention also provides the application of the above-mentioned double-layer high amino density plant fiber-based adsorption material in the adsorption of acid gas, especially in the adsorption of CO2 and/or SO2.

另外,本发明还提供上述双层高氨基密度植物纤维基吸附材料在木塑材料抗菌或防止木纤维霉变方面的应用。优选地是应用于抗金黄色葡萄球菌、大肠杆菌或白色念珠菌。In addition, the present invention also provides the application of the above-mentioned double-layer high amino density plant fiber-based adsorption material in the aspects of antibacterial wood-plastic materials or preventing mildew of wood fibers. Preferably it is applied against Staphylococcus aureus, Escherichia coli or Candida albicans.

本发明首次尝试将天然、可再生的植物纤维用于CO2吸附富集领域,制备出植物纤维基吸附材料;并根据CO2吸附的要求,针对植物纤维的特性,对吸附材料的制备工艺进行了优化和创新,首先以植物纤维为基体,依次经过碱预处理、接枝反应、胺化反应,得到单层氨基植物纤维基材料;再引入加成反应和PEI酰胺取代反应,通过与丙烯酰胺、丙烯酸甲酯、丙烯腈、丙烯酸或甲基丙烯酸缩水甘油酯等不饱和接枝单体溶液进行Michael加成反应,再与PEI进行酰胺取代反应,最终得到一种双层高氨基密度植物纤维基吸附材料;该吸附材料不仅对酸性气体具有优良的吸附捕集性能,还具有优良的抗菌性能,而且是一种可循环再生环保吸附材料,应用前景广泛。The present invention is the first attempt to use natural and renewable plant fibers in the field of CO2 adsorption and enrichment to prepare plant fiber-based adsorption materials ; In order to optimize and innovate, firstly, the plant fiber is used as the substrate, followed by alkali pretreatment, grafting reaction, and amination reaction to obtain a single-layer amino plant fiber-based material; then the addition reaction and PEI amide substitution reaction are introduced to obtain a , methyl acrylate, acrylonitrile, acrylic acid or glycidyl methacrylate and other unsaturated grafting monomer solutions for Michael addition reaction, and then amide substitution reaction with PEI, and finally a double-layer high amino density plant fiber base Adsorption material: The adsorption material not only has excellent adsorption and capture performance for acid gas, but also has excellent antibacterial performance, and is a recyclable and environmentally friendly adsorption material with broad application prospects.

本发明具有以下有益效果:The present invention has the following beneficial effects:

本发明公开了一种双层高氨基密度的植物纤维基吸附材料及其制备方法和应用。该双层高氨基密度植物纤维基吸附材料是以植物纤维为基体,经过碱预处理、接枝反应、胺化反应、加成反应、PEI酰胺取代反应制备得到。所用的植物纤维为天然、可再生的甘蔗渣、笋粉、玉米芯粉、剑麻、秸秆或棉纤维等,绿色环保,并从原料上降低成本,在不给全球大气造成二次污染的前提下,为CO2的分离富集提供了一定的技术支撑,将这些植物纤维应用于温室气体的吸附,具有重要的意义。The invention discloses a double-layer high amino density plant fiber-based adsorption material as well as a preparation method and application thereof. The double-layer high amino density plant fiber-based adsorption material is prepared by taking plant fiber as a matrix and undergoing alkali pretreatment, grafting reaction, amination reaction, addition reaction and PEI amide substitution reaction. The plant fibers used are natural and renewable bagasse, bamboo shoot powder, corncob powder, sisal hemp, straw or cotton fiber, etc., which are green and environmentally friendly, and reduce the cost of raw materials without causing secondary pollution to the global atmosphere. Under the circumstances, it provides a certain technical support for the separation and enrichment of CO 2 , and it is of great significance to apply these plant fibers to the adsorption of greenhouse gases.

与此同时,本发明适当的增加了类似PEI的支化结构,制备得到的双层高氨基密度的植物纤维基吸附材料,在增加氨基密度的同时,也可提高吸附容量和氨基效率。该吸附材料对酸性气体具有良好的吸附容量和良好的吸附捕集性能,可用于烟道气中CO2的吸附捕集领域,对CO2的吸附容量在2.0mmol CO2/g以上;对SO2的吸附容量在100mg/g以上。At the same time, the present invention appropriately increases the branched structure similar to PEI, and the prepared double-layered plant fiber-based adsorption material with high amino density can increase the adsorption capacity and amino efficiency while increasing the amino density. The adsorption material has good adsorption capacity and good adsorption and capture performance for acid gases, and can be used in the field of adsorption and capture of CO 2 in flue gas. The adsorption capacity for CO 2 is above 2.0mmol CO 2 /g; for SO 2 The adsorption capacity is above 100mg/g.

另外,本发明的植物纤维基吸附材料不但具有良好的吸附性能,还具有良好的抗菌性能,对金黄色葡萄球菌的抗菌率在98.3%以上,对大肠杆菌的抗菌率在96.4%以上,对白色念珠菌的抗菌率在95.6%以上。可应用于木塑材料领域,对于防止木纤维的霉变,提升木塑材料的质量,具有重要的应用前景。在其它抗菌领域也具有良好的应用前景。In addition, the plant fiber-based adsorption material of the present invention not only has good adsorption performance, but also has good antibacterial performance. The antibacterial rate against Staphylococcus aureus is above 98.3%, and the antibacterial rate against Escherichia coli is above 96.4%. The antibacterial rate of Candida is above 95.6%. It can be applied to the field of wood-plastic materials, and has important application prospects for preventing mildew of wood fibers and improving the quality of wood-plastic materials. It also has good application prospects in other antibacterial fields.

本发明的纤维基吸附材料的热分解温度在300℃以上,具有高的热稳定性、化学稳定性。而且该吸附材料在吸附气体后,可经过热脱附再生,再生10次后,二氧化碳和二氧化硫的解析率仍然可达90%以上,再生效率在93%以上,再生性能良好,是一种可循环再生环保吸附材料。The thermal decomposition temperature of the fiber-based adsorption material of the present invention is above 300° C., and has high thermal stability and chemical stability. Moreover, the adsorption material can be regenerated by thermal desorption after adsorbing gas. After 10 regenerations, the resolution rate of carbon dioxide and sulfur dioxide can still reach more than 90%, the regeneration efficiency is more than 93%, and the regeneration performance is good. It is a recyclable Recycled environmentally friendly absorbent material.

附图说明Description of drawings

图1为甘蔗渣基双层高氨基密度纤维基吸附材料在氮气下的热失重情况。Figure 1 is the thermal weight loss of bagasse-based double-layer high amino density fiber-based adsorbent material under nitrogen.

具体实施方式detailed description

以下结合说明书附图和具体实施例来进一步说明本发明,但实施例并不对本发明做任何形式的限定。除非特别说明,本发明采用的试剂、方法和设备为本技术领域常规试剂、方法和设备。The present invention will be further described below in conjunction with the accompanying drawings and specific embodiments, but the embodiments do not limit the present invention in any form. Unless otherwise specified, the reagents, methods and equipment used in the present invention are conventional reagents, methods and equipment in the technical field.

除非特别说明,本发明所用试剂和材料均为市购。Unless otherwise specified, the reagents and materials used in the present invention are commercially available.

实施例1Example 1

1、以甘蔗渣纤维为基体,制备吸附材料,步骤如下:1. Using bagasse fiber as the matrix to prepare the adsorption material, the steps are as follows:

(1)碱预处理:将甘蔗渣纤维粉碎后,浸入20wt% NaOH水溶液中,放入超声波震荡反应器中,在超声功率100W的条件下处理1.5h,超声处理结束后,取出于50℃的温度条件下浸泡24h,倾去溶液,所得纤维用水洗涤多次至中性,在60℃的烘箱真空干燥,至恒重。(1) Alkali pretreatment: After pulverizing the bagasse fiber, immerse it in 20wt% NaOH aqueous solution, put it into an ultrasonic shock reactor, and treat it under the condition of ultrasonic power 100W for 1.5h. After the ultrasonic treatment, take out the Soak under temperature conditions for 24 hours, pour off the solution, wash the obtained fiber with water for several times until neutral, and vacuum dry in an oven at 60°C until constant weight.

(2)接枝反应:将步骤(1)中所得甘蔗渣纤维与10wt%丙烯酰胺混合,控制甘蔗渣纤维的重量与丙烯酰胺的体积的比例为1:50,混合均匀后,加入30v/v% H2O2和2×10-2g/mL硫酸亚铁胺溶液;H2O2所需体积与丙烯酰胺的体积比例为0.8:100,硫酸亚铁胺溶液所需体积与丙烯酰胺的体积比例为1:5;在60℃下回流反应4h后,用乙醇浸洗抽滤3次,再用水浸洗抽滤3次,在60℃烘箱真空干燥,至恒重,得甘蔗渣基接枝纤维。(2) Grafting reaction: Mix the bagasse fiber obtained in step (1) with 10wt% acrylamide, and control the ratio of the weight of the bagasse fiber to the volume of acrylamide to be 1:50. After mixing evenly, add 30v/v % H 2 O 2 and 2×10 -2 g/mL ferrous amine sulfate solution; the volume ratio of the required volume of H 2 O 2 to acrylamide is 0.8:100, the required volume of ferrous amine sulfate solution to the volume ratio of acrylamide The volume ratio is 1:5; after reflux reaction at 60°C for 4 hours, soak and filter with ethanol for 3 times, then with water for 3 times, dry in a vacuum oven at 60°C until constant weight, and obtain bagasse-based stick fibers.

(3)胺化反应:在步骤(2)中所得甘蔗渣基接枝纤维中加入三乙烯四胺,接枝纤维的重量与三乙烯四胺的体积的比为1:100。混合物在130℃条件下反应8h。反应结束后用水浸洗若干次,最后用乙醇冲洗,抽滤,置于60℃烘箱内干燥。得甘蔗渣基单层氨基纤维材料。(3) Amination reaction: Add triethylenetetramine to the bagasse-based grafted fiber obtained in step (2), and the ratio of the weight of the grafted fiber to the volume of triethylenetetramine is 1:100. The mixture was reacted at 130°C for 8h. After the reaction, soak and wash with water several times, and finally rinse with ethanol, filter with suction, and dry in an oven at 60°C. A bagasse-based single-layer amino fiber material is obtained.

(4)加成反应:将步骤(3)中所得甘蔗渣基单层氨基纤维材料与5wt%丙烯酰胺溶液混合,控制甘蔗渣基单层氨基纤维材料的重量与丙烯酰胺溶液的体积的比例为1:60,放入超声波震荡反应器中,在超声功率400W的条件下处理2h,超声处理结束后取出,在水浴中继续反应,反应时间为1h,反应温度为60℃,使纤维发生Michael加成反应,反应结束后用水浸洗若干次,最后用乙醇冲洗,抽滤,置于60℃烘箱内干燥,得到加成后的甘蔗渣基单层氨基纤维材料。(4) Addition reaction: Mix the bagasse-based single-layer amino fiber material obtained in step (3) with a 5wt% acrylamide solution, and control the ratio of the weight of the bagasse-based single-layer amino fiber material to the volume of the acrylamide solution to be 1:60, put it into an ultrasonic shock reactor, treat it under the condition of ultrasonic power 400W for 2 hours, take it out after the ultrasonic treatment, and continue the reaction in a water bath for 1 hour, and the reaction temperature is 60°C, so that the fibers will undergo Michael addition. After the reaction, the mixture was rinsed with water for several times, finally rinsed with ethanol, filtered with suction, and dried in an oven at 60°C to obtain a bagasse-based single-layer amino fiber material after addition.

(5)PEI酰胺取代反应:将步骤(4)中所得加成后的甘蔗渣基单层氨基纤维材料与聚乙酰胺(PEI)混合,控制加成后甘蔗渣基单层氨基纤维材料的重量与PEI体积的比例为1:40,PEI的浓度为7wt%,反应时间为12h,反应温度为60℃,使纤维与多胺试剂PEI进行酰胺取代反应,反应结束后,乙醇洗涤除去多余的多胺试剂,抽滤,置于60℃烘箱内干燥,得甘蔗渣基双层高氨基密度纤维基吸附材料。(5) PEI amide substitution reaction: mix the added bagasse-based single-layer amino fiber material obtained in step (4) with polyacetamide (PEI), and control the weight of the added bagasse-based single-layer amino fiber material The ratio of PEI to volume is 1:40, the concentration of PEI is 7wt%, the reaction time is 12h, and the reaction temperature is 60°C, so that the fiber and the polyamine reagent PEI undergo amide substitution reaction. After the reaction, wash with ethanol to remove excess polyamide The amine reagent was suction filtered and dried in an oven at 60°C to obtain a bagasse-based double-layer high amino density fiber-based adsorption material.

2、经过检测,甘蔗渣基双层高氨基密度纤维基吸附材料在氮气下的热失重情况如附图1所示。附图1可以看出,甘蔗渣基双层高氨基密度纤维在100℃之前有轻微的失重,这主要是由于纤维表面对水、CO2等的物理吸附,100℃之后甘蔗渣基双层高氨基密度纤维的重量保持稳定,到直至230℃左右,甘蔗渣基双层高氨基密度纤维出现明显的失重。可认为甘蔗渣基双层高氨基密度纤维的胺化、接枝产物开始降解,到350℃左右,纤维基体开始降解,与前者的失重段发生重叠。所得甘蔗渣基双层高氨基密度纤维基吸附材料基本可以保持热稳定性在200℃左右。换言之,吸附材料在200℃下使用时,不会发生吸附材料降解的情况。可用于常规烟道气中CO2的吸附分离富集。2. After testing, the thermal weight loss of the bagasse-based double-layer high amino density fiber-based adsorption material under nitrogen is shown in Figure 1. It can be seen from Figure 1 that the bagasse-based double-layer high amino density fiber has a slight weight loss before 100°C, which is mainly due to the physical adsorption of water, CO2 , etc. on the fiber surface, after 100°C the bagasse-based double-layer high The weight of the amino density fiber remains stable until about 230°C, the bagasse-based double-layer high amino density fiber appears obvious weight loss. It can be considered that the amination and grafting products of bagasse-based double-layer high-amino-density fibers begin to degrade, and the fiber matrix begins to degrade at about 350°C, overlapping with the weight-loss section of the former. The obtained bagasse-based double-layer high amino density fiber-based adsorption material can basically maintain thermal stability at about 200°C. In other words, when the adsorption material is used at 200°C, no degradation of the adsorption material will occur. It can be used for adsorption, separation and enrichment of CO2 in conventional flue gas.

3、经过测定,上述甘蔗渣基双层高氨基密度纤维基吸附材料对CO2的吸附容量为7.42 mmol CO2/g,对SO2的吸附容量为103 mg SO2/g。3. After measurement, the above-mentioned bagasse-based double-layer high amino density fiber-based adsorption material has an adsorption capacity of 7.42 mmol CO 2 /g for CO 2 and an adsorption capacity of 103 mg SO 2 /g for SO 2 .

循环再生10次后,二氧化碳、二氧化硫的解析率90%,再生效率在93%。After 10 cycles of regeneration, the resolution rate of carbon dioxide and sulfur dioxide is 90%, and the regeneration efficiency is 93%.

甘蔗渣基双层高氨基密度纤维基吸附材料对金黄色葡萄球菌的抗菌率为98.3%,对大肠杆菌的抗菌率为96.4%,对白色念珠菌的抗菌率为95.6%。The antibacterial rate of bagasse-based double-layer high amino density fiber-based adsorbent material against Staphylococcus aureus was 98.3%, the antibacterial rate against Escherichia coli was 96.4%, and the antibacterial rate against Candida albicans was 95.6%.

实施例2Example 2

1、以秸秆纤维为基体,制备吸附材料,步骤如下:1. Using straw fiber as the matrix to prepare the adsorption material, the steps are as follows:

(1)碱预处理:将秸秆纤维粉碎后,浸入10wt% NaOH水溶液中,放入超声波震荡反应器中,在超声功率400W的条件下处理1h,超声处理结束后,取出于50℃的温度条件下浸泡10h,倾去溶液,所得纤维用水洗涤,多次至中性,在60℃的烘箱真空干燥,至恒重。(1) Alkali pretreatment: crush the straw fibers, immerse them in 10wt% NaOH aqueous solution, put them into an ultrasonic shock reactor, and treat them for 1 hour under the condition of ultrasonic power 400W. After the ultrasonic treatment, take them out at a temperature of 50°C Soak under water for 10 hours, pour off the solution, wash the obtained fiber with water for several times until neutral, and dry it in a vacuum oven at 60°C until it reaches a constant weight.

(2)接枝反应:将步骤(1)中所得秸秆纤维与2wt%甲基丙烯酸甲酯混合,控制秸秆纤维的重量与甲基丙烯酸甲酯的体积的比例为1:10,混合均匀后,加入30v/v% H2O2和1×10-3g/mL硫酸亚铁胺溶液;H2O2所需体积与甲基丙烯酸甲酯的体积比例为0.2:100,,硫酸亚铁胺溶液所需体积与甲基丙烯酸甲酯的体积比例为1:5;在30℃下回流反应24h后,用乙醇浸洗抽滤4次,再用水浸洗抽滤4次,在60℃烘箱真空干燥,至恒重,得秸秆基接枝纤维。(2) Grafting reaction: mix the straw fibers obtained in step (1) with 2wt% methyl methacrylate, control the ratio of the weight of straw fibers to the volume of methyl methacrylate to be 1:10, and mix well, Add 30v/v% H 2 O 2 and 1×10 -3 g/mL ferrous amine sulfate solution; the volume ratio of the required volume of H 2 O 2 to methyl methacrylate is 0.2:100, and ferrous amine sulfate The volume ratio of the required volume of the solution to methyl methacrylate is 1:5; after reflux reaction at 30°C for 24 hours, soak and filter with ethanol for 4 times, then wash with water for 4 times, vacuum in an oven at 60°C Dry to constant weight to obtain straw-based grafted fibers.

(3)胺化反应:在步骤(2)中所得秸秆基接枝纤维中加入二乙烯三胺,接枝纤维的重量与二乙烯三胺的体积的比为1:10。混合物在100℃条件下反应10h。反应结束后用水浸洗若干次,最后用乙醇冲洗,抽滤,置于60℃烘箱内干燥。得秸秆基单层氨基纤维材料。(3) Amination reaction: Add diethylenetriamine to the straw-based graft fibers obtained in step (2), and the ratio of the weight of the graft fibers to the volume of diethylenetriamine is 1:10. The mixture was reacted at 100 °C for 10 h. After the reaction, soak and wash with water several times, and finally rinse with ethanol, filter with suction, and dry in an oven at 60°C. A straw-based single-layer amino fiber material is obtained.

(4)加成反应:将步骤(3)中所得秸秆基单层氨基纤维材料与50wt%丙烯酰胺溶液混合,控制秸秆基单层氨基纤维材料的重量与丙烯酰胺溶液的体积的比例为1:10,放入超声波震荡反应器中,在超声功率100W的条件下处理1h,超声处理结束后取出,在水浴中继续反应,反应时间为24h,反应温度为10℃,使纤维发生Michael加成反应,反应结束后用水浸洗若干次,最后用乙醇冲洗,抽滤,置于60℃烘箱内干燥,得到加成后的秸秆基单层氨基纤维材料。(4) Addition reaction: Mix the straw-based single-layer amino fiber material obtained in step (3) with 50wt% acrylamide solution, and control the ratio of the weight of the straw-based single-layer amino fiber material to the volume of the acrylamide solution to be 1: 10. Put it into an ultrasonic shock reactor, treat it under the condition of ultrasonic power 100W for 1h, take it out after the ultrasonic treatment, and continue the reaction in the water bath. The reaction time is 24h, and the reaction temperature is 10°C, so that Michael addition reaction occurs on the fiber , after the reaction is completed, soak and wash with water for several times, finally wash with ethanol, filter with suction, and dry in an oven at 60°C to obtain the added straw-based single-layer amino fiber material.

(5)PEI酰胺取代反应:将步骤(4)中所得加成后的秸秆基单层氨基纤维材料与PEI混合,控制加成后秸秆基单层氨基纤维材料的重量与PEI体积比例为1:5,PEI的浓度为5 wt%,反应时间为10h,反应温度为60℃,使纤维与多胺试剂PEI进行酰胺取代反应,反应结束后,乙醇洗涤除去多余的多胺试剂抽滤,置于60℃烘箱内干燥,得秸秆基双层高氨基密度纤维基吸附材料。(5) PEI amide substitution reaction: mix the added straw-based single-layer amino fiber material obtained in step (4) with PEI, and control the ratio of the weight of the added straw-based single-layer amino fiber material to the volume of PEI to be 1: 5. The concentration of PEI is 5 wt%, the reaction time is 10h, and the reaction temperature is 60°C, so that the fiber and polyamine reagent PEI undergo amide substitution reaction. After the reaction, wash with ethanol to remove excess polyamine reagent and suction filter, and place in Dry in an oven at 60°C to obtain a straw-based double-layer high amino density fiber-based adsorption material.

2、经过测定,上述秸秆基双层高氨基密度纤维基吸附材料对CO2的吸附容量为2.0mmol CO2/g。对SO2的吸附容量为100mg SO2/g。2. It has been determined that the CO 2 adsorption capacity of the straw-based double-layer high amino density fiber-based adsorption material is 2.0 mmol CO 2 /g. The adsorption capacity for SO 2 is 100 mg SO 2 /g.

循环再生10次后,二氧化碳、二氧化硫的解析率93%,再生效率在95%。After 10 cycles of regeneration, the resolution rate of carbon dioxide and sulfur dioxide is 93%, and the regeneration efficiency is 95%.

秸秆基双层高氨基密度纤维基吸附材料对金黄色葡萄球菌的抗菌率为98.7%,对大肠杆菌的抗菌率为96.9%,对白色念珠菌的抗菌率为95.7%。The antibacterial rate of the straw-based double-layer high amino density fiber-based absorbent material was 98.7% against Staphylococcus aureus, 96.9% against Escherichia coli, and 95.7% against Candida albicans.

实施例3Example 3

1、以剑麻原纤维为基体,制备吸附材料,步骤如下:1. Using sisal fibrils as the substrate to prepare the adsorption material, the steps are as follows:

(1)碱预处理:将剑麻原纤维裁剪成约2-4cm左右的小段,浸入20wt% NaOH水溶液中,放入超声波震荡反应器中,在超声功率300W的条件下处理2h,超声处理结束后,取出于50℃的温度条件下浸泡20h,倾去溶液,所得纤维用水洗涤,多次至中性,在60℃的烘箱真空干燥,至恒重。(1) Alkali pretreatment: Cut sisal fibrils into small pieces of about 2-4cm, immerse them in 20wt% NaOH aqueous solution, put them in an ultrasonic shock reactor, and treat them for 2 hours under the condition of ultrasonic power 300W. , take it out and soak it for 20 hours at a temperature of 50°C, pour off the solution, wash the obtained fiber with water several times until it becomes neutral, and dry it in a vacuum oven at 60°C until it reaches a constant weight.

(2)接枝反应:将步骤(1)中所得剑麻原纤维与20wt%丙烯酸甲酯混合,控制剑麻原纤维的重量与丙烯酸甲酯的体积的比例为1:50,混合均匀后,加入30% H2O2和1×10-1g/mL硫酸亚铁胺溶液;H2O2所需体积与丙烯酸甲酯的体积比例为2:100,硫酸亚铁胺溶液所需体积与丙烯酸甲酯的体积比例为1:5;在80℃下回流反应1h后,用乙醇浸洗抽滤5次,再用水浸洗抽滤5次,在60℃烘箱真空干燥,至恒重,得剑麻基接枝纤维。(2) Grafting reaction: Mix the sisal fibrils obtained in step (1) with 20wt% methyl acrylate, and control the ratio of the weight of the sisal fibrils to the volume of methyl acrylate to be 1:50. After mixing evenly, add 30 % H 2 O 2 and 1×10 -1 g/mL ferrous amine sulfate solution; the volume ratio of H 2 O 2 required volume to methyl acrylate is 2:100, the required volume of ferrous amine sulfate solution to methyl acrylate The volume ratio of the ester is 1:5; after reflux reaction at 80°C for 1 hour, soak and filter with ethanol for 5 times, then soak with water for 5 times, dry in a 60°C oven under vacuum until constant weight, and obtain sisal base graft fiber.

(3)胺化反应:在步骤(2)中所得剑麻基接枝纤维中加入乙二胺,接枝纤维的重量与乙二胺的体积的比为1:2。混合物在150℃条件下反应6h。反应结束后用水浸洗若干次,最后用乙醇冲洗,抽滤,置于60℃烘箱内干燥。得剑麻基单层氨基纤维材料。(3) Amination reaction: Add ethylenediamine to the sisal-based grafted fiber obtained in step (2), and the ratio of the weight of the grafted fiber to the volume of ethylenediamine is 1:2. The mixture was reacted at 150°C for 6h. After the reaction, soak and wash with water several times, and finally rinse with ethanol, filter with suction, and dry in an oven at 60°C. A sisal-based single-layer amino fiber material was obtained.

(4)加成反应:将步骤(3)中所得剑麻基单层氨基纤维材料与15%wt甲基丙酸甲酯溶液混合,控制剑麻基单层氨基纤维材料的重量与甲基丙烯酸甲酯溶液的体积的比例为1:100,放入超声波震荡反应器中,在超声功率300W的条件下处理2h,超声处理结束后取出,在水浴中继续反应,反应时间为24h,反应温度为70℃,使纤维发生Michael加成反应,反应结束后用水浸洗若干次,最后用乙醇冲洗,抽滤,置于60℃烘箱内干燥,得到加成后的剑麻基单层氨基纤维材料。(4) Addition reaction: Mix the sisal-based single-layer amino fiber material obtained in step (3) with a 15%wt methyl methacrylate solution to control the weight of the sisal-based single-layer amino fiber material and methacrylic acid The ratio of the volume of the methyl ester solution is 1:100, put it into an ultrasonic vibration reactor, process it under the condition of ultrasonic power 300W for 2h, take it out after the ultrasonic treatment ends, and continue to react in a water bath, the reaction time is 24h, and the reaction temperature is At 70°C, the fiber undergoes Michael addition reaction. After the reaction, the fiber is soaked several times with water, finally rinsed with ethanol, filtered with suction, and dried in an oven at 60°C to obtain a sisal-based single-layer amino fiber material after addition.

(5)PEI酰胺取代反应:将步骤(4)中所得加成后的剑麻基单层氨基纤维材料与PEI混合,控制加成后剑麻基单层氨基纤维材料的重量与PEI体积比例为1:60,PEI的浓度为15wt %,反应时间为48h,反应温度为20℃,使纤维与PEI进行酰胺取代反应,反应结束后,乙醇洗涤除去多余的多胺试剂抽滤,置于60℃烘箱内干燥,得剑麻基双层高氨基密度纤维基吸附材料。(5) PEI amide substitution reaction: mix the added sisal-based single-layer amino fiber material obtained in step (4) with PEI, and control the weight ratio of the added sisal-based single-layer amino fiber material to the PEI volume ratio as follows: 1:60, the concentration of PEI is 15wt%, the reaction time is 48h, and the reaction temperature is 20°C, so that the fiber and PEI undergo an amide substitution reaction. After the reaction, wash with ethanol to remove excess polyamine reagent and suction filter, and place at 60°C drying in an oven to obtain a sisal-based double-layer high amino density fiber-based adsorption material.

2、经过测定,上述剑麻基双层高氨基密度纤维基吸附材料对CO2的吸附容量为3.22 mmol CO2/g,对SO2的吸附容量为106 mg SO2/g。2. After measurement, the adsorption capacity of the above-mentioned sisal-based double-layer high amino density fiber-based adsorption material for CO 2 is 3.22 mmol CO 2 /g, and the adsorption capacity for SO 2 is 106 mg SO 2 /g.

循环再生10次后,二氧化碳、二氧化硫的解析率95%,再生效率在98%。After 10 cycles of regeneration, the resolution rate of carbon dioxide and sulfur dioxide is 95%, and the regeneration efficiency is 98%.

剑麻基双层高氨基密度纤维基吸附材料对金黄色葡萄球菌的抗菌率为98.6%,对大肠杆菌的抗菌率为96.5%,对白色念珠菌的抗菌率为96.0%。The antibacterial rate of the sisal-based double-layer high amino density fiber-based absorbent material against Staphylococcus aureus was 98.6%, the antibacterial rate against Escherichia coli was 96.5%, and the antibacterial rate against Candida albicans was 96.0%.

实施例4Example 4

1、以棉纤维为基体,制备吸附材料,步骤如下:1. Use cotton fiber as the matrix to prepare the adsorption material. The steps are as follows:

(1)碱预处理:将棉纤维剪碎后,浸入20wt% NaOH水溶液中,放入超声波震荡反应器中,在超声功率300W的条件下处理1.5h,超声处理结束后,取出于50℃的温度条件下浸泡24h,倾去溶液,所得纤维用水洗涤,多次至中性,在60℃的烘箱真空干燥,至恒重。(1) Alkali pretreatment: Cut the cotton fibers into pieces, immerse them in 20wt% NaOH aqueous solution, put them into an ultrasonic shock reactor, and treat them for 1.5h under the condition of ultrasonic power of 300W. After the ultrasonic treatment, take out the Soak for 24 hours under temperature conditions, pour off the solution, wash the obtained fiber with water for several times until it becomes neutral, and dry it in a vacuum oven at 60°C until it reaches constant weight.

(2)接枝反应:将步骤(1)中所得棉纤维与10wt%丙烯酸混合,控制棉纤维的重量与丙烯酸的体积的比例为1:40,混合均匀后,加入30% H2O2和5×10-3g/mL硫酸亚铁胺溶液;H2O2所需体积与丙烯酸的体积比例为1:100,硫酸亚铁胺溶液所需体积与丙烯酸的体积比例为1:5;在70℃下回流反应15h后,用乙醇浸洗抽滤3次,再用水浸洗抽滤3次,在60℃烘箱真空干燥,至恒重,得棉纤基接枝纤维。(2) Grafting reaction: mix the cotton fiber obtained in step (1) with 10wt% acrylic acid, control the ratio of the weight of cotton fiber to the volume of acrylic acid to be 1:40, after mixing evenly, add 30% H 2 O 2 and 5×10 -3 g/mL ferrous amine sulfate solution; the volume ratio of the required volume of H 2 O 2 to acrylic acid is 1:100, and the volume ratio of the required volume of ferrous amine sulfate solution to acrylic acid is 1:5; After reflux reaction at 70°C for 15 hours, soak and filter with ethanol for 3 times, then with water for 3 times, dry in a 60°C oven in vacuum until constant weight to obtain cotton fiber-based grafted fiber.

(3)胺化反应:在步骤(2)中所得棉纤基接枝纤维中加入五乙烯六胺,接枝纤维的重量与五乙烯六胺的体积的比为1:40。混合物在120℃条件下反应8h。反应结束后用水浸洗若干次,最后用乙醇冲洗,抽滤,置于60℃烘箱内干燥。得棉纤基单层氨基纤维材料。(3) Amination reaction: Add pentaethylene hexamine to the cotton fiber-based graft fiber obtained in step (2), and the ratio of the weight of the graft fiber to the volume of pentaethylene hexamine is 1:40. The mixture was reacted at 120°C for 8h. After the reaction, soak and wash with water several times, and finally rinse with ethanol, filter with suction, and dry in an oven at 60°C. A cotton fiber-based single-layer amino fiber material is obtained.

(4)加成反应:将步骤(3)中所得棉纤基单层氨基纤维材料与15wt%丙烯酸溶液混合,控制棉纤基单层氨基纤维材料的重量与丙烯酸溶液的体积的比例为1:50,放入超声波震荡反应器中,在超声功率400W的条件下处理1h,超声处理结束后取出,在水浴中继续反应,反应时间为15h,反应温度为50℃,使纤维发生Michael加成反应,反应结束后用水浸洗若干次,最后用乙醇冲洗,抽滤,置于60℃烘箱内干燥,得到加成后的棉纤基单层氨基纤维材料。(4) Addition reaction: the cotton fiber-based single-layer amino fiber material obtained in step (3) is mixed with 15wt% acrylic acid solution, and the ratio of the weight of the cotton fiber-based single-layer amino fiber material to the volume of the acrylic acid solution is 1: 50, put it into an ultrasonic shock reactor, treat it under the condition of ultrasonic power 400W for 1h, take it out after the ultrasonic treatment, and continue the reaction in the water bath, the reaction time is 15h, and the reaction temperature is 50°C, so that Michael addition reaction occurs on the fiber , After the reaction is completed, soak and wash with water for several times, and finally wash with ethanol, filter with suction, and dry in an oven at 60°C to obtain a cotton fiber-based single-layer amino fiber material after addition.

(5)PEI酰胺取代反应:将步骤(4)中所得加成后的棉纤基单层氨基纤维材料与PEI混合,控制加成后棉纤基单层氨基纤维材料的重量与PEI体积比例为1:40,PEI的浓度为10wt %,反应时间为15h,反应温度为60℃,使纤维与多胺试剂PEI进行酰胺取代反应,反应结束后,乙醇洗涤除去多余的多胺试剂抽滤,置于60℃烘箱内干燥,得棉纤基双层高氨基密度纤维基吸附材料。(5) PEI amide substitution reaction: mix the added cotton fiber-based single-layer amino fiber material obtained in step (4) with PEI, and control the weight ratio of the added cotton fiber-based single-layer amino fiber material to PEI volume ratio as 1:40, the concentration of PEI is 10wt%, the reaction time is 15h, and the reaction temperature is 60°C, so that the fiber and the polyamine reagent PEI undergo amide substitution reaction. Dry in an oven at 60°C to obtain a cotton fiber-based double-layer high amino density fiber-based absorbent material.

2、经过测定,上述棉纤基双层高氨基密度纤维基吸附材料对CO2的吸附容量为6.11 mmol CO2/g,对SO2的吸附容量为100mg SO2/g。2. After measurement, the above-mentioned cotton fiber-based double-layer high amino density fiber-based adsorption material has an adsorption capacity of 6.11 mmol CO 2 /g for CO 2 and an adsorption capacity of 100 mg SO 2 /g for SO 2 .

循环再生10次后,二氧化碳、二氧化硫的解析率90%,再生效率在93%。After 10 cycles of regeneration, the resolution rate of carbon dioxide and sulfur dioxide is 90%, and the regeneration efficiency is 93%.

棉纤基双层高氨基密度纤维基吸附材料对金黄色葡萄球菌的抗菌率为99.0%,对大肠杆菌的抗菌率为96.9%,对白色念珠菌的抗菌率为95.9%。The cotton fiber-based double-layer high amino density fiber-based absorbent material has an antibacterial rate of 99.0% against Staphylococcus aureus, 96.9% against Escherichia coli, and 95.9% against Candida albicans.

实施例5Example 5

1、以笋粉为基体,制备吸附材料,步骤如下:1. Use bamboo shoot powder as the matrix to prepare the adsorption material, the steps are as follows:

(1)碱预处理:将将笋粉浸入20wt% NaOH水溶液中,,放入超声波震荡反应器中,在超声功率200W的条件下处理1.5h,超声处理结束后,取出于50℃的温度条件下浸泡20h,倾去溶液,所得笋粉用水洗涤,多次至中性,在60℃的烘箱真空干燥,至恒重。(1) Alkali pretreatment: immerse the bamboo shoot powder in 20wt% NaOH aqueous solution, put it into an ultrasonic shock reactor, and treat it under the condition of ultrasonic power 200W for 1.5h. After the ultrasonic treatment, take it out at a temperature of 50°C Soak it under water for 20 hours, pour off the solution, wash the obtained bamboo shoot powder with water for several times until it becomes neutral, and dry it under vacuum in an oven at 60°C until it reaches a constant weight.

(2)接枝反应:将步骤(1)中所得笋粉纤维与8wt%丙烯酸混合,控制笋粉纤维的重量与丙烯酸的体积的比例为1:50,混合均匀后,加入30% H2O2和1.5×10-2g/mL硫酸亚铁胺溶液;H2O2所需体积与丙烯酸的体积比例为0.6:100,硫酸亚铁胺溶液所需体积与丙烯酸的体积比例为1:5;在40℃下回流反应20h后,用乙醇浸洗抽滤3次,再用水浸洗抽滤5次,在60℃烘箱真空干燥,至恒重,得笋粉基接枝纤维。(2) Grafting reaction: mix the bamboo shoot powder fiber obtained in step (1) with 8wt% acrylic acid, control the ratio of the weight of the bamboo shoot powder fiber to the volume of acrylic acid to 1:50, after mixing evenly, add 30% H 2 O 2 and 1.5×10 -2 g/mL ferrous amine sulfate solution; the volume ratio of the required volume of H 2 O 2 to acrylic acid is 0.6:100, and the volume ratio of the required volume of ferrous amine sulfate solution to acrylic acid is 1:5 After reflux reaction at 40°C for 20h, wash with ethanol and filter for 3 times, then wash with water for 5 times, dry in a vacuum oven at 60°C until constant weight to obtain bamboo shoot powder-based grafted fiber.

(3)胺化反应:在步骤(2)中所得笋粉基接枝纤维中加入四乙烯五胺,接枝纤维的重量与四乙烯五胺的体积的比为1:50。混合物在130℃条件下反应8h。反应结束后用水浸洗若干次,最后用乙醇冲洗,抽滤,置于60℃烘箱内干燥。得笋粉基单层氨基纤维材料。(3) Amination reaction: Add tetraethylenepentamine to the bamboo shoot powder-based graft fiber obtained in step (2), and the ratio of the weight of the graft fiber to the volume of tetraethylenepentamine is 1:50. The mixture was reacted at 130°C for 8h. After the reaction, soak and wash with water several times, and finally rinse with ethanol, filter with suction, and dry in an oven at 60°C. A bamboo shoot powder-based single-layer amino fiber material is obtained.

(4)加成反应:将步骤(3)中所得笋粉基单层氨基纤维材料与20%wt丙烯酰胺溶液混合,控制笋粉基单层氨基纤维材料的重量与丙烯酰胺溶液的体积的比例为1:50,放入超声波震荡反应器中,在超声功率400W的条件下处理1h,超声处理结束后取出,在水浴中继续反应,反应时间为8h,反应温度为70℃,使纤维发生Michael加成反应,反应结束后用水浸洗若干次,最后用乙醇冲洗,抽滤,置于60℃烘箱内干燥,得到加成后的笋粉基单层氨基纤维材料。(4) Addition reaction: mix the bamboo shoot powder-based single-layer amino fiber material obtained in step (3) with 20%wt acrylamide solution, and control the ratio of the weight of the bamboo shoot powder-based single-layer amino fiber material to the volume of the acrylamide solution 1:50, put it into an ultrasonic shock reactor, treat it under the condition of ultrasonic power 400W for 1h, take it out after the ultrasonic treatment, and continue the reaction in the water bath, the reaction time is 8h, and the reaction temperature is 70°C, so that the fiber will produce Michael Addition reaction, after the reaction is completed, soak and wash with water several times, finally rinse with ethanol, filter with suction, and dry in an oven at 60°C to obtain a bamboo shoot powder-based single-layer amino fiber material after addition.

(5)PEI酰胺取代反应:将步骤(4)中所得加成后的笋粉基单层氨基纤维材料与PEI混合,控制加成后笋粉基单层氨基纤维材料的重量与PEI体积比例为1:40,PEI的浓度为7wt %,反应时间为12h,反应温度为60℃,使纤维与PEI进行酰胺取代反应,反应结束后,乙醇洗涤除去多余的多胺试剂抽滤,置于60℃烘箱内干燥,得笋粉基双层高氨基密度纤维基吸附材料。(5) PEI amide substitution reaction: mix the bamboo shoot powder-based single-layer amino fiber material obtained in step (4) with PEI, and control the ratio of the weight of the bamboo shoot powder-based single-layer amino fiber material to the volume of PEI after the addition is 1:40, the concentration of PEI is 7wt%, the reaction time is 12h, and the reaction temperature is 60°C, so that the fiber and PEI undergo an amide substitution reaction. After the reaction, wash with ethanol to remove excess polyamine reagent and suction filter, and place at 60°C drying in an oven to obtain a bamboo shoot powder-based double-layer high amino density fiber-based adsorption material.

2、经过测定,上述笋粉基双层高氨基密度纤维基吸附材料对CO2的吸附容量为2.56 mmol CO2/g,对SO2的吸附容量为106mg SO2/g。2. After measurement, the adsorption capacity of the bamboo shoot powder-based double-layer high amino density fiber-based adsorption material for CO 2 is 2.56 mmol CO 2 /g, and the adsorption capacity for SO 2 is 106 mg SO 2 /g.

循环再生10次后,二氧化碳、二氧化硫的解析率92%,再生效率在95%。After 10 cycles of regeneration, the resolution rate of carbon dioxide and sulfur dioxide is 92%, and the regeneration efficiency is 95%.

笋粉基双层高氨基密度纤维基吸附材料对金黄色葡萄球菌的抗菌率为98.4%,对大肠杆菌的抗菌率为96.4%,对白色念珠菌的抗菌率为95.9%。The antibacterial rate of the bamboo shoot powder-based double-layer high amino density fiber-based absorbent material was 98.4% against Staphylococcus aureus, 96.4% against Escherichia coli, and 95.9% against Candida albicans.

实施例6Example 6

1、以玉米芯纤维为基体,制备吸附材料,步骤如下:1. Using corn cob fiber as the substrate to prepare the adsorption material, the steps are as follows:

(1)碱预处理:将将玉米芯纤维粉碎,浸入15wt% NaOH水溶液中,放入超声波震荡反应器中,在超声功率400W的条件下处理1h,超声处理结束后,取出于50℃的温度条件下浸泡10h,倾去溶液,所得玉米芯用水洗涤,多次至中性,在60℃的烘箱真空干燥,至恒重。(1) Alkali pretreatment: crush the corncob fibers, immerse them in 15wt% NaOH aqueous solution, put them into an ultrasonic shock reactor, and treat them for 1 hour under the condition of ultrasonic power 400W. After the ultrasonic treatment, take them out at a temperature of 50°C Soak for 10 hours under the same conditions, pour off the solution, wash the obtained corn cobs with water for several times until neutral, and vacuum-dry them in an oven at 60°C until they reach constant weight.

(2)接枝反应:将步骤(1)中所得玉米芯纤维与20wt%丙烯腈混合,控制玉米芯纤维的重量与丙烯腈的体积的比例为1:40,混合均匀后,加入30% H2O2和8×10-3g/mL硫酸亚铁胺溶液;H2O2所需体积与丙烯腈的体积比例为0.8:100,硫酸亚铁胺溶液所需体积与丙烯腈的体积比例为1:5;在70℃下回流反应24h后,用乙醇浸洗抽滤5次,再用水浸洗抽滤4次,在60℃烘箱真空干燥,至恒重,得玉米芯基接枝纤维。(2) Grafting reaction: Mix the corn cob fiber obtained in step (1) with 20wt% acrylonitrile, control the ratio of the weight of the corn cob fiber to the volume of acrylonitrile to 1:40, after mixing evenly, add 30% H 2 O 2 and 8×10 -3 g/mL ferrous amine sulfate solution; the volume ratio of the required volume of H 2 O 2 to acrylonitrile is 0.8:100, the volume ratio of the required volume of ferrous amine sulfate solution to acrylonitrile The ratio is 1:5; after reflux reaction at 70°C for 24 hours, immerse and filter with ethanol for 5 times, then soak and filter with water for 4 times, dry in a 60°C oven under vacuum until constant weight, and obtain corn cob-based grafted fiber .

(3)胺化反应:在步骤(2)中所得玉米芯基接枝纤维中加入二乙胺,接枝纤维的重量与二乙胺的体积的比为1:40。混合物在100℃条件下反应4h。反应结束后用水浸洗若干次,最后用乙醇冲洗,抽滤,置于60℃烘箱内干燥。得玉米芯基单层氨基纤维材料。(3) Amination reaction: Add diethylamine to the corncob-based graft fiber obtained in step (2), and the ratio of the weight of the graft fiber to the volume of diethylamine is 1:40. The mixture was reacted at 100°C for 4h. After the reaction, soak and wash with water several times, and finally rinse with ethanol, filter with suction, and dry in an oven at 60°C. Obtain corncob-based single-layer amino fiber material.

(4)加成反应:将步骤(3)中所得玉米芯基单层氨基纤维材料与20%wt丙烯酸甲酯溶液混合,控制玉米芯基单层氨基纤维材料的重量与丙烯酸甲酯溶液的体积的比例为1:30,放入超声波震荡反应器中,在超声功率400W的条件下处理1h,超声处理结束后取出,在水浴中继续反应,反应时间为20h,反应温度为70℃,使纤维发生Michael加成反应,反应结束后用水浸洗若干次,最后用乙醇冲洗,抽滤,置于60℃烘箱内干燥,得到加成后的玉米芯基单层氨基纤维材料。(4) Addition reaction: Mix the corncob-based single-layer amino fiber material obtained in step (3) with 20%wt methyl acrylate solution, and control the weight of the corncob-based single-layer amino fiber material and the volume of the methyl acrylate solution The ratio is 1:30, put it into an ultrasonic shock reactor, and treat it under the condition of ultrasonic power 400W for 1h, take it out after the ultrasonic treatment, and continue the reaction in a water bath, the reaction time is 20h, and the reaction temperature is 70°C. A Michael addition reaction occurs, after the reaction is completed, it is soaked with water for several times, finally rinsed with ethanol, filtered with suction, and dried in an oven at 60°C to obtain a corncob-based single-layer amino fiber material after addition.

(5)PEI酰胺取代反应:将步骤(4)中所得加成后玉米芯基单层氨基纤维材料与PEI混合,控制加成后玉米芯基单层氨基纤维材料的重量与PEI体积比例为1:50,PEI的浓度为15 wt %,反应时间为48h,反应温度为60℃,使纤维与PEI进行酰胺取代反应,反应结束后,乙醇洗涤除去多余的多胺试剂抽滤,置于60℃烘箱内干燥,得玉米芯基双层高氨基密度纤维基吸附材料。(5) PEI amide substitution reaction: Mix the added corncob-based single-layer amino fiber material obtained in step (4) with PEI, and control the weight ratio of the added corncob-based single-layer amino fiber material to PEI volume ratio to 1 :50, the concentration of PEI is 15 wt %, the reaction time is 48h, and the reaction temperature is 60°C, so that the fiber and PEI are subjected to amide substitution reaction. After the reaction, wash with ethanol to remove excess polyamine reagent and suction filter, and place at 60°C drying in an oven to obtain a corncob-based double-layer high amino density fiber-based adsorption material.

2、经过测定,上述玉米芯基双层高氨基密度纤维基吸附材料对CO2的吸附容量为4.25 mmol CO2/g,对SO2的吸附容量为105mg SO2/g。2. It has been determined that the above-mentioned corncob-based double-layer high amino density fiber-based adsorption material has an adsorption capacity of 4.25 mmol CO 2 /g for CO 2 and an adsorption capacity of 105 mg SO 2 /g for SO 2 .

循环再生10次后,二氧化碳、二氧化硫的解析率93%,再生效率在96%。After 10 cycles of regeneration, the resolution rate of carbon dioxide and sulfur dioxide is 93%, and the regeneration efficiency is 96%.

玉米芯基双层高氨基密度纤维基吸附材料对金黄色葡萄球菌的抗菌率为99.1%,对大肠杆菌的抗菌率为97.1%,对白色念珠菌的抗菌率为95.6%。The antibacterial rate of the corncob-based double-layer high amino density fiber-based absorbent material was 99.1% against Staphylococcus aureus, 97.1% against Escherichia coli, and 95.6% against Candida albicans.

Claims (4)

1. a kind of double-deck high amino density Plant fiber's adsorbing material is it is characterised in that prepared by following preparation method:
S1. oxygenation pretreatment:
S11. Plant fiber is placed in 10~20wt% NaOH aqueous solution, 100~400W ultrasonic vibration processes 1~2h;
S12., after supersound process, soak 10~24h in 50 DEG C;
S13. incline solution, and gained fiber is washed with water to neutrality, 60 DEG C of drying;
Described Plant fiber is bagasse, Radix Crotalariae szemoensis powder, maize cob meal, Folium Agaves Sisalanae, straw or cotton fiber;
S2. graft reaction:
S21. it is 1 according to the weight of Plant fiber after oxygenation pretreatment with the ratio of the volume of unsaturated grafted monomers solution:10~ 1:50, both are mixed;The concentration of described unsaturation grafted monomers solution is 2~20wt%;
S22. according to H2O2Volume ratio with unsaturated grafted monomers solution is 0.2:100~2:100, the solution after mixing to S21 Middle addition initiator H2O2
S23. the volume ratio according to ferrous sulfate amine aqueous solution and unsaturated grafted monomers solution is 1:5, the solution after processing to S22 Middle addition ferrous sulfate amine aqueous solution;The concentration of described ferrous sulfate amine aqueous solution is 1 × 10-3~1 × 10-1g/mL;
S24., after reaction 1~24h under the conditions of 30~80 DEG C, embathe sucking filtration 2~5 times with ethanol, then wash sucking filtration 2~5 with water logging Secondary, 60 DEG C of vacuum dryings, obtain graft fibres;
Described unsaturation grafted monomers solution be:Acrylamide solution, methyl acrylate solution, acrylonitrile solution, acrylic acid are molten Liquid or glycidyl methacrylate solution;S3. aminating reaction:
S31. according to polyamines and graft fibres weight than for 2:1~100:1, graft fibres add polyamines;
S32. under the conditions of 100~150 DEG C react 6~10h, washed 2~5 times with water logging, then use alcohol flushing, sucking filtration, 60 DEG C dry Dry, obtain monolayer amino plant fiber-based material;
Described polyamines is ethylenediamine, diethylamine, diethylenetriamine, triethylene tetramine, TEPA or pentaethylene hexamine;
S4. additive reaction:
S41. it is 1 according to the weight of monolayer amino plant fiber-based material with the ratio of the volume of unsaturated grafted monomers solution: 10~1:60, both are mixed, the concentration of described unsaturation grafted monomers solution is 5~50wt%;
S42., after 100~400W ultrasonic lower process 1~2h, 10~60 DEG C of water-baths are reacted 1~24h;
S43. washed 2~5 times with water logging, finally use alcohol flushing, sucking filtration, 60 DEG C of drying, obtain the monolayer amino plant after addition Fiber-based material;
S5.PEI amide substitution reaction:
S51. the ratio according to the weight of the monolayer amino plant fiber-based material after addition and the volume of polyethyleneimine is 1:5 ~1:60, both are mixed, the concentration of described polyethyleneimine is 5~15wt%;
S52. react 10~48h at 20~60 DEG C, make fiber and polyethyleneimine carry out amide substitution reaction;
S53. washing with alcohol removes unnecessary polyethyleneimine, sucking filtration, 60 DEG C of drying, obtains double-deck high amino density Plant fiber Adsorbing material;
Wherein, described Plant fiber is bagasse, Radix Crotalariae szemoensis powder, maize cob meal, Folium Agaves Sisalanae, straw or cotton fiber;
The heat decomposition temperature of this adsorbing material, more than 300 DEG C, has anti-microbial property and the adsorbing and trapping performance to sour gas; This adsorbing material, after adsorbed gas, can regenerate through thermal desorption.
2. application in terms of absorbing acid gases for the double-deck high amino density Plant fiber's adsorbing material described in claim 1.
3. described in claim 1, double-deck high amino density Plant fiber's adsorbing material in Wood-plastic material antibacterial or prevents the wood fiber The application of aspect of going mouldy.
4. apply according to claim 3 it is characterised in that being to be applied to anti-Staphylococcus aureus, escherichia coli or white Color candidiasises.
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