CN115012052A - A method for preparing micro-nano cellulose fibers from corn stalks - Google Patents
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Abstract
Description
技术领域technical field
本发明属于绿色生物质精炼技术领域,特别是涉及到一种以玉米秸秆为原料制备微纳米纤维素纤维的方法。The invention belongs to the technical field of green biomass refining, and in particular relates to a method for preparing micro-nano cellulose fibers by using corn stover as a raw material.
背景技术Background technique
玉米秸秆占整株玉米生物学产量的50%以上,玉米秸秆中纤维素含量可达到35.0%~39.6%。仅次于大麦秸秆(36.0~43.0%),与小麦秸秆(32.0~40.0%)和高粱秸秆(35.0~39.0%)相当。The corn stalk accounts for more than 50% of the biological yield of the whole corn plant, and the cellulose content in the corn stalk can reach 35.0% to 39.6%. It is second only to barley straw (36.0-43.0%) and comparable to wheat straw (32.0-40.0%) and sorghum straw (35.0-39.0%).
由于具有较大的比表面积、较好的生物相容性和绿色可降解性,微纳米纤维素纤维在材料科学、纳米技术、生物医药和食品科学等领域都有着广阔的应用前景。Due to its large specific surface area, good biocompatibility and green degradability, micro- and nanocellulose fibers have broad application prospects in the fields of material science, nanotechnology, biomedicine and food science.
根据前期的研究结果,微纳米纤维素纤维的制备方法主要包括机械法、生物酶法和化学法。由于过高的能量消耗,机械法很难被推广工业化。虽然酶水解技术可以极大的降低微纳米纤维素纤维生产过程中的能耗,但是这种方法不能够有效的修饰纤维表面结构。相比之下,化学法可以有效的在纤维表面引入各种新的官能团,从而产生新奇性质的微纳米纤维素基新材料。因此,该方法具有更好的发展前景。According to the previous research results, the preparation methods of micro-nano cellulose fibers mainly include mechanical methods, biological enzymes and chemical methods. Due to the high energy consumption, the mechanical method is difficult to promote industrialization. Although the enzymatic hydrolysis technology can greatly reduce the energy consumption during the production of micro/nanocellulose fibers, this method cannot effectively modify the fiber surface structure. In contrast, chemical methods can effectively introduce various new functional groups on the fiber surface, resulting in novel micro- and nanocellulose-based materials with novel properties. Therefore, this method has better development prospects.
目前,大约有不下十种制备微纳米纤维素纤维的化学法被报道,例如2,2,6,6-四甲基哌啶自由基-1-氧基自由基(TEMPO)氧化法、阳离子化法、磷酸化法、羟甲基化法、磺酸基乙基化法等。其中,TEMPO氧化法得到了人们的广泛关注。At present, there are no less than ten chemical methods for preparing micro-nanocellulose fibers, such as 2,2,6,6-tetramethylpiperidine radical-1-oxyl radical (TEMPO) oxidation, cationization method, phosphorylation method, methylolation method, sulfoethylation method, etc. Among them, the TEMPO oxidation method has received extensive attention.
然而,这些报道的方法反应过程复杂,需要环境非友好型的共催化剂和溶剂,例如次氯酸盐和二氯甲烷等。这导致这些报道的方法完全不符合全绿色生物质精炼的原则。However, these reported methods have complex reaction processes and require environmentally unfriendly co-catalysts and solvents, such as hypochlorite and dichloromethane. This makes these reported methods totally inconsistent with the principles of all-green biomass refining.
由于具有低成本和没有额外环境污染物种的优势,Fenton反应体系在生物质精炼领域得到了人们的广泛关注。例如,利用Fenton反应体系模拟白腐菌的代谢过程生成羟基自由基氧化木质纤维中的木质素。在另外的一个例子中Fenton反应体系被采用去预处理木质素去生产酚油。Due to the advantages of low cost and no additional environmental pollutants, the Fenton reaction system has received extensive attention in the field of biomass refining. For example, the Fenton reaction system was used to simulate the metabolic process of white rot fungi to generate hydroxyl radicals to oxidize lignin in lignocellulose. In another example, the Fenton reaction system was used to de-pretreat lignin to produce phenolic oils.
将传统的Fenton反应体系引入生物质精炼领域最大的缺点主要来自于羟基自由基活性物种不能有效作用在目标生物质的有机大分子上,多数在水体中失活,导致Fenton反应体系处理生物质体系过程中无效。发展原位诱导多相Fenton高级氧化技术是克服上述缺点的有效方法之一。The biggest disadvantage of introducing the traditional Fenton reaction system into the field of biomass refining mainly comes from the fact that the hydroxyl radical active species cannot effectively act on the organic macromolecules of the target biomass, and most of them are inactivated in the water body, resulting in the Fenton reaction system to treat the biomass system. invalid during the process. The development of in situ induced heterogeneous Fenton advanced oxidation technology is one of the effective methods to overcome the above shortcomings.
专利CN112227102B公开了将蔗髓、氢氧化钠、水进行混合,在氧气气氛下进行蒸煮,超声进行梯度离心,获得不同尺寸级别的微纳米纤维素纤维;专利CN106279444B公开了一种纳米纤维素原纤乳液的制备方法,是将天然纤维素纤维加入NaOH溶液中,在60~98℃下搅拌并同步超声波震荡0.2~2小时,然后浸没于含NaOH和NaClO的混合溶液中,在60~98℃下搅拌并同步超声波震荡1~20小时后,得到含纳米纤维素原纤的混合液;将所得的含纳米纤维素原纤的混合液进行离心分离,再透析0.5~3天,得到纳米纤维素原纤乳液。专利CN101851801A公布了将生物质纤维经苯醇溶液抽提、酸化亚氯酸钠处理、碱液梯度处理、超声波细胞粉碎机处理、高压匀质处理和干燥制备纳米纤维素纤维。还有一些工作是将软木漂白硫酸盐浆进行双氧水氧化后再用两室高压均质机制备纤维素微纳米纤维。综述所述,这些报道的方法制备的微纳米纤维素纤维尺寸不可控,溶剂和共催化剂环境不友好,高压均质能耗高等缺点。Patent CN112227102B discloses mixing cane pith, sodium hydroxide and water, cooking in an oxygen atmosphere, and ultrasonic gradient centrifugation to obtain micro- and nano-cellulose fibers of different sizes; Patent CN106279444B discloses a nano-cellulose fibril The preparation method of the emulsion is as follows: adding natural cellulose fibers to a NaOH solution, stirring at 60-98 °C and synchronous ultrasonic vibration for 0.2-2 hours, and then immersing in a mixed solution containing NaOH and NaClO, at a temperature of 60-98 °C. After stirring and synchronous ultrasonic vibration for 1 to 20 hours, a mixed solution containing nanocellulose fibrils is obtained; the obtained mixed solution containing nanocellulose fibrils is centrifuged, and then dialyzed for 0.5 to 3 days to obtain nanocellulose fibrils. fiber lotion. Patent CN101851801A discloses the preparation of nanocellulose fibers by extracting biomass fibers with benzene alcohol solution, treating with acidified sodium chlorite, lye gradient treatment, ultrasonic cell pulverizer treatment, high-pressure homogenization treatment and drying. There is also some work on the preparation of cellulose micro-nanofibers by using a two-chamber high-pressure homogenizer after the oxidation of softwood bleached kraft pulp with hydrogen peroxide. In summary, the micro-nanocellulose fibers prepared by these reported methods have the disadvantages of uncontrollable size, unfriendly solvent and co-catalyst environment, and high energy consumption for high-pressure homogenization.
发明内容SUMMARY OF THE INVENTION
本发明所要解决的技术问题是:提供一种以玉米秸秆为原料制备微纳米纤维素纤维的方法,克服微纳米纤维素纤维制造过程成本过高、所用溶剂环境不友好和过渡依赖木材或木材漂白硫酸盐纸浆为原料的缺点,采用原位诱导多相Fenton高级氧化技术,以来源丰富、价格低廉、利用率低的玉米秸秆为原料,将玉米秸秆预处理得到高纤维素含量的产物后,进一步经过原位诱导多相Fenton氧化与较短时间的超声得到具有纳米级尺度的纤维素纤维。The technical problem to be solved by the present invention is: to provide a method for preparing micro-nano cellulose fibers with corn stalks as raw materials, overcoming the high cost of the micro-nano cellulose fibers manufacturing process, the unfriendly environment of the solvent used and the excessive dependence on wood or wood bleaching The shortcomings of kraft pulp as raw material, using in-situ induced heterogeneous Fenton advanced oxidation technology, using corn stover with abundant sources, low price and low utilization rate as raw material, after pretreatment of corn stover to obtain a product with high cellulose content, further Cellulose fibers with nanoscale scale were obtained by in situ induced heterogeneous Fenton oxidation and short-time sonication.
一种以玉米秸秆为原料制备微纳米纤维素纤维的方法,其特征是:包括以下步骤,且以下步骤顺次进行,A method for preparing micro-nano cellulose fibers using corn stalks as a raw material is characterized by comprising the following steps, and the following steps are performed in sequence,
步骤一、取PH为10.5~11.5的NaOH水溶液,按照质量比NaOH:H2O:玉米秸秆=1:8:1放入玉米秸秆;在90℃的条件下加热3h,经过滤后固液分离,获得固体纤维;Step 1. Take the NaOH aqueous solution with a pH of 10.5-11.5, put the corn stalks in the mass ratio NaOH:H 2 O:corn stalk=1:8:1; heat at 90°C for 3h, filter and separate solid-liquid , to obtain solid fibers;
步骤二、将所述步骤一获得的固体纤维浸泡在pH为2.5~4的Fe2+溶液中,完成Fe2+在纤维间的扩散与预吸附,经减压、过滤及洗涤去除多余的Fe2+;Step 2: Immerse the solid fibers obtained in the first step in Fe 2+ solution with a pH of 2.5 to 4 to complete the diffusion and pre-adsorption of Fe 2+ between fibers, and remove excess Fe through decompression, filtration and washing. 2+ ;
步骤三、将所述步骤二吸附Fe2+后的固体纤维置于0.4%的H2O2溶液中,室温搅拌24h进行氧化;氧化后的产物固液分离,分离后液体可补足Fe2+后重复多次使用,分离后固体洗涤至pH=5~7,分散在水中配置成2wt%的悬浮物,在频率为20KHz下的超声处理10min,得到含水率为99%微纳米纤维素纤维。Step 3: Place the solid fiber after adsorption of Fe 2+ in the second step in a 0.4% H 2 O 2 solution, and stir at room temperature for 24 hours for oxidation; the oxidized product is separated from solid and liquid, and the liquid after separation can supplement Fe 2+ After repeated use, the separated solid was washed to pH=5-7, dispersed in water to form a 2wt% suspension, and ultrasonically treated at a frequency of 20KHz for 10min to obtain micro-nano cellulose fibers with a moisture content of 99%.
所述步骤三获得的微纳米纤维素纤维的直径为50~70nm,羧基含量为0.59±0.04mmol/g,聚合度为649±6。The diameter of the micro-nano cellulose fibers obtained in the third step is 50-70 nm, the carboxyl group content is 0.59±0.04 mmol/g, and the degree of polymerization is 649±6.
所述步骤一采用的玉米秸秆为草球压机制作的草球状秸秆。The corn stalks used in the first step are grass-ball-shaped straws made by a grass-ball press.
所述步骤二采用的Fe2+为工业级FeSO4˙7H2O固体。The Fe 2+ used in the second step is an industrial-grade FeSO 4 ˙7H 2 O solid.
通过上述设计方案,本发明可以带来如下有益效果:一种以玉米秸秆为原料制备微纳米纤维素纤维的方法,在常温常压的温和环境下,利用原位诱导多相Fenton氧化法产生的强氧化性的羟基自由基对碱预处理的玉米秸秆进行氧化处理,只需要短时间的超声处理就可以完成最后微纳米纤维素纤维的生产,大大降低了设备耗能。Through the above-mentioned design scheme, the present invention can bring the following beneficial effects: a method for preparing micro-nano cellulose fibers using corn stalks as raw materials, in the mild environment of normal temperature and pressure, using the in-situ induced heterogeneous Fenton oxidation method to produce The strong oxidizing hydroxyl radicals oxidize the alkali-pretreated corn stalks, and only need a short-time ultrasonic treatment to complete the final production of micro-nano cellulose fibers, which greatly reduces the energy consumption of the equipment.
进一步的,本发明步骤一中固液分离的滤液可在补充水以后重复使用最少三次,且黑液中富含木质素,可进行二次利用;Further, the filtrate of the solid-liquid separation in step 1 of the present invention can be reused at least three times after replenishing water, and the black liquor is rich in lignin, which can be used for secondary use;
本发明步骤二和步骤三氧化用水均可以在补充Fe2+后进行循环利用,不会产生水资源的排放与浪费;Both step 2 and step trioxidation water of the present invention can be recycled after supplementing Fe 2+ , and will not produce discharge and waste of water resources;
本发明在Fe2+吸附至最后得到微纳米纤维素纤维产物的所有过程都不会产生废水排放与水资源浪费;In the present invention, all processes from Fe 2+ adsorption to finally obtaining micro-nano cellulose fiber products will not produce waste water discharge and water resources waste;
本发明得到的微纳米纤维素纤维平均长度≤2μm,直径为50~70nm,具有鲜明的纳米尺度结构,羧基含量为0.59±0.04mmol/g,DP为649±6,含水率可达到99%,在进一步真空过滤热压后可得到半透明薄膜。The micro-nano cellulose fibers obtained by the invention have an average length of ≤2 μm, a diameter of 50-70 nm, a distinct nano-scale structure, a carboxyl group content of 0.59±0.04 mmol/g, a DP of 649±6, and a moisture content of 99%. A translucent film can be obtained after further vacuum filtration and hot pressing.
以下结合具体实施方式对本发明作进一步的说明:The present invention will be further described below in conjunction with specific embodiments:
具体实施方式Detailed ways
实例1:取20gNaOH固体放入2L不锈钢反应釜中,取水1.6L倒入并搅拌使NaOH固体完全溶解,200g玉米秸秆(40目粉末)倒入反应釜边搅拌便在90℃条件下处理3h。预先将20gFeSO4˙7H2O与800ml水混合,并完全溶解,用稀硫酸调节pH在2.5~4范围内,称取干重为100g的碱液预处理秸秆放入溶液,在室温下搅拌1h完成纤维对Fe2+的吸附过程,真空过滤除去悬浮在液体中多余的Fe2+,洗涤除去粘附在纤维表面多余的Fe2+。预吸附完成后,先将20ml浓度为30%的H2O2分散在780ml水中,在2L不锈钢反应器内,将溶液与预吸附纤维混合,室温搅拌3h使其充分氧化。将氧化完成的固体产物,与水混合至2wt%,取800ml悬浮液于1L塑料容器中,在20KHz频率下超声处理10min,最终得到微纳米纤维素纤维产品。Example 1: Take 20g of NaOH solid and put it into a 2L stainless steel reaction kettle, pour 1.6L of water into it and stir to completely dissolve the NaOH solid, 200g of corn stalks (40 mesh powder) are poured into the reaction kettle and stirred at 90°C for 3 hours. Mix 20g FeSO 4 ˙ 7H 2 O with 800ml of water in advance and dissolve it completely, adjust the pH with dilute sulfuric acid in the range of 2.5 to 4, weigh 100g dry weight of lye pretreated straw, put it into the solution, and stir at room temperature for 1 hour After completing the adsorption process of Fe 2+ on the fiber, vacuum filtration to remove the excess Fe 2+ suspended in the liquid, and washing to remove the excess Fe 2+ adhering to the surface of the fiber. After the pre-adsorption was completed, 20ml of H 2 O 2 with a concentration of 30% was dispersed in 780ml of water, the solution was mixed with the pre-adsorbed fibers in a 2L stainless steel reactor, and stirred at room temperature for 3h to make it fully oxidized. The oxidized solid product was mixed with water to 2wt%, 800ml of the suspension was taken in a 1L plastic container, and ultrasonically treated at a frequency of 20KHz for 10min to finally obtain a micro-nano cellulose fiber product.
实例2:取200gNaOH固体放入50L玻璃夹套反应釜中,取水16L倒入并搅拌使NaOH固体完全溶解,2kg玉米秸秆(草球状固体)倒入反应釜边搅拌便在90℃条件下处理3h,使用磨浆机磨浆后固液分离。预先将200gFeSO4˙7H2O与10水混合,并完全溶解,用稀硫酸调节pH在2.5~4范围内,将碱液预处理后的秸秆放入溶液,在室温下搅拌1h完成纤维对Fe2+的吸附过程,真空过滤除去悬浮在液体中多余的Fe2+,洗涤除去粘附在纤维表面多余的Fe2+。预吸附完成后,先将200ml浓度为30%的H2O2分散在10ml水中,在50L玻璃夹套反应器内,将溶液与预吸附纤维混合,室温搅拌3h使其充分氧化。将氧化完成的固体产物,与水混合至2wt%,在20KHz频率下超声处理得到微纳米纤维素纤维产品。Example 2: Take 200g of NaOH solid and put it into a 50L glass-jacketed reactor, take 16L of water and pour it in and stir to dissolve the NaOH solid completely, and pour 2kg of corn stalk (grass ball-shaped solid) into the reactor and stir it for 3 hours at 90°C , solid-liquid separation after refining with a refiner. Mix 200g FeSO 4 ˙ 7H 2 O with 10 water in advance, and dissolve it completely, adjust the pH with dilute sulfuric acid in the range of 2.5 to 4, put the straw pretreated with lye into the solution, and stir at room temperature for 1 hour to complete the effect of fiber on Fe In the adsorption process of 2+ , the excess Fe 2+ suspended in the liquid is removed by vacuum filtration, and the excess Fe 2+ adhering to the surface of the fiber is removed by washing. After the pre-adsorption is completed, 200 ml of H 2 O 2 with a concentration of 30% is dispersed in 10 ml of water, and the solution is mixed with the pre-adsorbed fibers in a 50 L glass-jacketed reactor, and stirred at room temperature for 3 h to make it fully oxidized. The oxidized solid product is mixed with water to 2wt%, and ultrasonically treated at a frequency of 20KHz to obtain a micro-nano cellulose fiber product.
实例3:取200gNaOH固体放入50L玻璃夹套反应釜中,取实例2中过滤出的碱液预处理的黑液,加水补充至16L,此时的pH为10.5~11略有下降,2kg玉米秸秆(草球状固体)倒入反应釜边搅拌便在90℃条件下处理3h,使用磨浆机简单磨浆后固液分离。向实例2中预吸附用水中加入适量FeSO4˙7H2O补足Fe2+浓度,并完全溶解,用稀硫酸调节pH在2.5~4范围内,将碱液预处理后的秸秆放入溶液,在室温下搅拌1h完成纤维对Fe2+的吸附过程,真空过滤除去悬浮在液体中多余的Fe2+,洗涤除去粘附在纤维表面多余的Fe2+。预吸附完成后,补足H2O2浓度后氧化用水重复使用,在50L玻璃夹套反应器内,将溶液与预吸附纤维混合,室温搅拌3h使其充分氧化。将氧化完成的固体产物,与水混合至2wt%,在20KHz频率下超声处理得到微纳米纤维素纤维产品。Example 3: get 200g of NaOH solid and put it into a 50L glass jacketed reactor, get the black liquor of the lye pretreatment filtered out in example 2, add water and make up to 16L, the pH at this time is 10.5~11 and drops slightly, 2kg corn The straw (grass ball-like solid) was poured into the reaction kettle and stirred at 90°C for 3 hours, and the solid-liquid separation was performed after simple refining with a refiner. In Example 2, an appropriate amount of FeSO 4 ˙7H 2 O was added to the pre-adsorption water to make up the Fe 2+ concentration, and it was completely dissolved. The pH was adjusted with dilute sulfuric acid in the range of 2.5 to 4, and the lye pretreated straw was put into the solution. The adsorption process of Fe 2+ on the fiber was completed by stirring at room temperature for 1 h, the excess Fe 2+ suspended in the liquid was removed by vacuum filtration, and the excess Fe 2+ adhering to the surface of the fiber was removed by washing. After the pre-adsorption is completed, the oxidation water is reused after supplementing the H 2 O 2 concentration. In a 50L glass-jacketed reactor, the solution is mixed with the pre-adsorbed fibers, and stirred at room temperature for 3 hours to fully oxidize. The oxidized solid product is mixed with water to 2wt%, and ultrasonically treated at a frequency of 20KHz to obtain a micro-nano cellulose fiber product.
表1.原料与不同处理下产物的成分与聚合度Table 1. Composition and degree of polymerization of raw materials and products under different treatments
表1说明:Table 1 explains:
(1)纤维素与木质素含量的测定,采用GB/T 2677.10-1995、GB/T 35818-2018现行国家标准进行测定;(1) Determination of cellulose and lignin content, using the current national standards of GB/T 2677.10-1995 and GB/T 35818-2018;
(2)羧基含量采用的是GB/T 10338-2008现行国家标准,聚合度DP采用特性粘度法与GB 5888-1986现行国家标准相结合进行测定,测量前样品均经过干燥处理;(2) The carboxyl group content adopts the current national standard of GB/T 10338-2008, the degree of polymerization DP is determined by the intrinsic viscosity method combined with the current national standard of GB 5888-1986, and the samples are all dried before measurement;
(3)所有数据均经过三次以上测量取得平均值,以避免一次测量引起测量错误并减小数据误差。(3) All data are averaged after three or more measurements to avoid measurement errors caused by one measurement and reduce data errors.
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