CN113171800B - 改性分子筛复合柔性陶瓷纳米纤维材料及其制法和应用 - Google Patents

改性分子筛复合柔性陶瓷纳米纤维材料及其制法和应用 Download PDF

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CN113171800B
CN113171800B CN202110443629.3A CN202110443629A CN113171800B CN 113171800 B CN113171800 B CN 113171800B CN 202110443629 A CN202110443629 A CN 202110443629A CN 113171800 B CN113171800 B CN 113171800B
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molecular sieve
flexible ceramic
ceramic nanofiber
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nanofiber material
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CN113171800A (zh
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刘一涛
王慧
戴劲
俞建勇
丁彬
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Abstract

本发明涉及一种改性分子筛复合柔性陶瓷纳米纤维材料及其制法和应用,该方法是在同一接收基材上先后交替进行杂化纳米纤维膜的沉积和分子筛分散液的喷涂,并控制沉积次数比喷涂次数多一次后,进行煅烧处理制得复合柔性陶瓷纳米纤维材料;其中,杂化纳米纤维膜由包含陶瓷前驱体、高分子聚合物和溶剂的前驱体溶液经静电纺丝制得;制得的复合柔性陶瓷纳米纤维材料包含两层以上柔性陶瓷纳米纤维膜以及封装于相邻两层柔性陶瓷纳米纤维膜之间的分子筛。该材料可以用于氮氧分离;当分子筛上负载有活性组分时,该材料用于催化氧化降解工业废水。本发明的复合柔性陶瓷纳米纤维材料化学稳定性优异、比表面积大且制备简单,易于在工业中应用。

Description

改性分子筛复合柔性陶瓷纳米纤维材料及其制法和应用
技术领域
本发明属于工业催化用材料技术领域,具体涉及一种改性分子筛复合柔性陶瓷纳米纤维材料及其制法和应用。
背景技术
多相固体催化剂是目前工业中使用比例最高的催化剂,主要包括活性组分及载体两大部分,活性组分负载于载体之上,其中,载体材料应具有较高的比表面积和优良的物理化学稳定性。
近年来,分子筛因其比表面积大、内部孔道密集、稳定性好,在催化剂载体领域受到了广泛关注。然而,粉末或颗粒状分子筛间缺乏牢固的相互作用力,导致其在液相介质中使用时极易分散成悬浮液,使其面临与反应介质的分离成本高,操作复杂且易造成二次污染的问题,同时,其在空气介质中使用时存在易脱落、脆性大、不耐振动等问题。专利CN104874418B和CN103316708B经挤压成型后得到整体式分子筛催化剂,方便于反应介质分离,但其制备过程需要加入粘结剂,粘结剂会堵塞部分分子筛孔道使其无法被充分利用,催化活性降低;专利CN111841625A制备了一种不锈钢纤维复合分子筛膜处理VOCs催化剂,活性组分均匀分散在催化剂中,但其以不锈钢纤维为载体,采用水热二次生长法制备该材料,材料尺寸受反应釜内径限制,难以大规模、连续化生产;CN105603579B制备了一种高长径比中空分子筛纤维,但其将静电纺丝制备的纤维浸渍于分子筛晶种液中而后经水热合成制备了该材料,高温高压环境对纤维有很大损害,使其变脆变硬,且反应釜内径有限,限制了其规模化、连续化生产;美国专利US7390452B2公开了一种静电纺丝的介孔分子筛/纤维复合材料,聚醚酰亚胺(PEI)甲醇溶液和介孔分子筛溶液共混静电纺丝形成复合物,从扫描电子显微镜在纤维表面没有明显观察到分子筛,即分子筛大部分存在纤维中,内部的分子筛无法发挥其性能。
因此,研究一种可充分利用单分子筛的性能、催化性能优异、具备一定柔性、化学稳定性优异、比表面积大且制备简单、易于与反应介质相分离、易于在工业中实际应用的催化材料具有十分重要的意义。
发明内容
本发明的目的在于克服现有材料的不足之处,提供一种改性分子筛复合柔性陶瓷纳米纤维材料及其制法和应用。
为达到上述目的,本发明采用的技术方案如下:
一种改性分子筛复合柔性陶瓷纳米纤维材料,包含两层以上柔性陶瓷纳米纤维膜以及封装于相邻两层柔性陶瓷纳米纤维膜之间的分子筛。
作为优选的技术方案:
如上所述的一种改性分子筛复合柔性陶瓷纳米纤维材料,柔性陶瓷纳米纤维膜的比表面积为40~200m2/g,厚度为10~100μm,纤维直径为100~600nm;改性分子筛复合柔性陶瓷纳米纤维材料中分子筛的含量为20~90wt%。
如上所述的一种改性分子筛复合柔性陶瓷纳米纤维材料,柔性陶瓷纳米纤维膜为柔性二氧化硅纳米纤维膜或柔性二氧化钛纳米纤维膜;优选的二氧化硅和二氧化钛陶瓷纳米纤维膜均具有优异的亲水性,可与液相中有机污染物充分接触反应,且该材料耐腐蚀,化学稳定性好,可在复杂条件废水中长期使用而保持结构稳定。
如上所述的一种改性分子筛复合柔性陶瓷纳米纤维材料,分子筛上还负载有活性组分;活性组分在分子筛上的负载量为3~65wt%。
如上所述的一种改性分子筛复合柔性陶瓷纳米纤维材料,活性组分为金属氧化物;负载有活性组分的分子筛是通过将分子筛浸渍于金属盐溶液中后进行干燥和焙烧获得的;金属盐溶液中金属元素的含量为分子筛重量的5~80wt%;分子筛与金属盐溶液的质量比为1:10~100;浸渍时间为10~360min,温度为20~80℃;优选参数范围内,金属盐可充分溶解于溶剂中,而后通过浸渍、干燥并焙烧稳定负载于分子筛上,金属氧化物在分子筛上的负载量直接影响最终制备的负载催化剂的活性,该范围内制得的产品可保证其优异的催化活性。
如上所述的一种改性分子筛复合柔性陶瓷纳米纤维材料,金属盐为硝酸铁、硫酸亚铁、硝酸锰、氯化锰、硝酸铜和硝酸钴中的一种以上;金属盐溶液中的溶剂为水和/或乙醇;
以上金属盐均具备水溶性或者醇溶性优良的特点,且原料易得,成本低廉,选择不同的金属盐直接影响最终制备的负载催化剂的活性,优选金属盐制得的产品可保证其优异的催化活性。
制备如上所述的一种改性分子筛复合柔性陶瓷纳米纤维材料的方法,在同一接收基材上先后交替进行杂化纳米纤维膜的沉积和分子筛分散液的喷涂,并控制沉积次数比喷涂次数多一次后,进行煅烧处理制得改性分子筛复合柔性陶瓷纳米纤维材料;
杂化纳米纤维膜由前驱体溶液经静电纺丝制得,前驱体溶液包含陶瓷前驱体、高分子聚合物和溶剂。
作为优选的技术方案:
如上所述的方法,陶瓷前驱体为正硅酸乙酯、硅酸钠、六甲基二氧硅烷、钛酸四丁酯、钛酸异丙酯和钛酸四乙酯中的一种以上;所选用的硅源和钛源在不同溶剂中,水解形成溶胶的过程有显著区别,直接影响纺丝成纤过程;
高分子聚合物为聚已烯醇、聚乙烯吡咯烷酮、聚氧化乙烯和聚乙烯醇缩丁醛中的一种以上;以上选择的聚合物均为水溶性和醇溶性较优异的聚合物,且原料易得,成本低廉,不同的聚合物会使最后成型陶瓷纤维具有多种独特的表面结构,得到不同形貌和比表面积的陶瓷纳米纤维;
前驱体溶液中的溶剂为水、冰乙酸、甲醇、乙醇、正丙醇、正丁醇、乙二醇、丙二醇、仲丁醇和N,N-二甲基甲酰胺中的一种以上;
前驱体溶液中,陶瓷前驱体的含量为10~50wt%,高分子聚合物的含量为1~10wt%;陶瓷前驱体含量以及高分子聚合物的浓度设定可以确保通过静电纺丝得到粗细均匀的纤维,同时,缓解煅烧过程中由于聚合物模板的去除,纤维膜的体积收缩对生产效率的影响;
静电纺丝的参数为:相对湿度25~55%,温度18~35℃,电压5~30kV,灌注速度0.1~10mL/h,纺丝距离10~40cm,滚筒速度5~100r/min,滑台运行速度5~100cm/min;
分子筛分散液中的溶剂为水、冰乙酸、乙醇和N,N-二甲基甲酰胺中的一种以上;负载有活性组分的分子筛分散液的浓度为10~50wt%;在该参数范围内,可制备静电喷涂所需的分子筛分散液,使负载有活性组分的分子筛喷涂于基材上,而后被稳定封装于相邻的纤维膜中,最终得到具有催化活性的且方便于反应介质相分离的固体催化材料;
喷涂采用静电纺丝装置;喷涂的参数为:相对湿度25~55%,温度18~35℃,电压10~30kV,灌注速度0.1~10mL/h,喷涂距离10~40cm,滚筒速度5~80r/min,滑台运行速度5~100cm/min;
煅烧的参数为:煅烧温度400~1000℃,升温速率2~10℃/min,保温时间0~6h;煅烧温度在400℃至1000℃之间且保温时间设置在0~6小时内可以确保金属盐完全分解,并且形成的金属氧化物结构较为完善;将升温速率控制在2~10℃/min内,金属氧化物颗粒生长较均匀,有效抑制升温速率不当引起的颗粒团聚,分布不均匀等情况。
本发明还提供如上所述的改性分子筛复合柔性陶瓷纳米纤维材料的应用,改性分子筛复合柔性陶瓷纳米纤维材料用于氮氧分离。
本发明还提供如上所述的改性分子筛复合柔性陶瓷纳米纤维材料的应用,改性分子筛复合柔性陶瓷纳米纤维材料用于催化氧化降解工业废水。
本发明的原理是:
在高压静电场作用下,陶瓷前驱体溶胶/聚合物液滴带电并且产生形变,在喷头末端处形成锥状液滴,当液滴表面静电斥力大于表面张力时,会使液滴表面喷射出溶液射流,在其飞行过程中经过溶液挥发、固化等过程最终形成杂化纳米纤维沉积在接收装置上;通过调控分子筛溶液体系,使其均匀分散,在高压作用下,以静电喷雾的形式将分子筛颗粒均匀负载到纤维表面,随后可以根据需求,将纤维和分子筛多次沉积,得到厚度可调的纤维-分子筛-纤维的三明治夹芯结构,最后通过高温煅烧得到复合材料。
本发明产品成型过程中仅使用静电纺丝设备(不需要静电雾化装置),仅使用柔性陶瓷纳米纤维膜作为外层基材使本发明制得的产品便于与反应介质相分离,负载有活性组分的分子筛通过静电喷涂的方式被纳米纤维膜封装于纤维层间而非纤维中,且外层材料为纳米纤维材料,孔隙率高且具备亲水性能,可与液相反应介质充分接触,液相反应介质可透过纤维膜间的孔隙与封装与其中的单分子筛充分接触、反应,可充分利用单分子筛的催化性能,有效比表面积大,催化活性位点多,催化效率高;因此,使得将本发明中的改性分子筛复合柔性陶瓷纳米纤维材料在应用至氮氧分离和催化氧化降解工业废水中时,取得了优异的效果。
有益效果
(1)本发明的一种改性分子筛复合柔性陶瓷纳米纤维材料的方法,在材料成型过程中仅需要使用静电纺丝设备,无需额外静电喷涂设备,节约成本,减少设备占地面积;
(2)本发明一种改性分子筛复合柔性陶瓷纳米纤维材料的方法制备的材料结构为柔性陶瓷纳米纤维膜-分子筛-柔性陶瓷纳米纤维膜的类三明治结构,无需粘结剂即可将负载有活性组分的分子筛稳定封装于两层纳米纤维膜之中,不易脱落且不会对分子筛孔道结构产生破坏;
(3)本发明一种改性分子筛复合柔性陶瓷纳米纤维材料的方法制备的材料金属改性分子筛存在于纤维层间而非纤维中,且外层材料为纳米纤维材料,孔隙率高且具备亲水性能,可充分利用单分子筛的催化性能,有效比表面积大,催化活性位点多,催化效率高;
(4)本发明一种改性分子筛复合柔性陶瓷纳米纤维材料的方法制备的材料为整体式柔性催化材料,应用方便,便于与反应介质分离,无需进行二次处理。
具体实施方式
下面结合具体实施例,进一步阐述本发明。应理解,这些实施例仅用于说明本发明而不限制本发明的范围。此外应理解,在阅读了本发明讲授的内容之后,本领域技术人员可以对本发明做各种改动或修改,这些等价形式同样落于本申请所附权利要求书所限定的范围。
实施例1
一种改性分子筛复合柔性陶瓷纳米纤维材料的方法,具体步骤如下:
(1)负载有活性组分的分子筛的制备;
通过将分子筛(MCM41分子筛)浸渍于温度为20℃的金属盐溶液中360min后,进行干燥(干燥时间3h,干燥温度110℃)和焙烧(焙烧温度550℃,焙烧时间2h)获得负载有活性组分的分子筛;金属盐溶液中,金属盐为硝酸铁,溶剂为水;金属盐溶液中铁的含量为分子筛重量的10wt%;分子筛与金属盐溶液的质量比为1:10;
制得的负载有活性组分的分子筛中的活性组分为氧化铁;
(2)由前驱体溶液经静电纺丝制得杂化纳米纤维膜;
前驱体溶液由含量为25wt%的正硅酸乙酯、含量为5wt%的聚已烯醇和水组成;
静电纺丝的参数为:相对湿度40%,温度20℃,电压18kV,灌注速度1mL/h,纺丝距离20cm,滚筒速度50r/min,滑台运行速度50cm/min;
(3)将步骤(1)制得的负载有活性组分的分子筛分散在水中,制得浓度为30wt%的负载有活性组分的分子筛分散液,利用静电纺丝装置将其喷涂于步骤(2)所得杂化纳米纤维膜上;
喷涂的参数为:相对湿度40%,温度20℃,电压20kV,灌注速度1.5mL/h,喷涂距离20cm,滚筒速度40r/min,滑台运行速度50cm/min;
(4)在步骤(3)所得材料上,在喷涂分子筛分散液的那一面,重复步骤(2)后,进行煅烧处理制得改性分子筛复合柔性陶瓷纳米纤维材料;
煅烧的参数为:煅烧温度800℃,升温速率5℃/min,保温时间0h。
制得的改性分子筛复合柔性陶瓷纳米纤维材料,包含2层柔性二氧化硅纳米纤维膜(由杂化纳米纤维膜经过煅烧处理制得)以及封装于相邻两层柔性陶瓷纳米纤维膜之间的负载有活性组分的分子筛;柔性陶瓷纳米纤维膜的比表面积为167m2/g,厚度为60μm,纤维直径为200~300nm;活性组分在分子筛上的负载量为9wt%;改性分子筛复合柔性陶瓷纳米纤维材料中负载有活性组分的分子筛的含量为50wt%。
应用:将改性分子筛复合柔性陶瓷纳米纤维材料用于催化氧化降解工业废水,改性分子筛复合柔性陶瓷纳米纤维材料通过臭氧催化氧化法1h内对苯甲酸钠的降解率达到90%,通过过硫酸盐氧化法1h内对苯酚的降解率达到89%。
测试方法如下:
臭氧催化氧化法降解苯甲酸钠:将50毫克的改性分子筛复合柔性陶瓷纳米纤维材料置于250mL圆底烧瓶中,向圆底烧瓶中加入100mL的100mg/L的苯甲酸钠模拟废水溶液,使用曝气头从圆底烧瓶底部曝气,将臭氧的进气流量控制在0.4L/min,进气浓度为4mg/L。连续曝气1小时后,取样,测定COD值,计算去除效果。
过硫酸盐氧化法:以50mg/L的苯酚溶液作为模拟废水,在100mL的苯酚模拟废水中加入20mM的过硫酸钾,取50mg的改性分子筛复合柔性陶瓷纳米纤维材料加至上述溶液中进行降解测试,以改性分子筛复合柔性陶瓷纳米纤维材料加入时作为计时零点,分别在60min取样,通过4-氨基安替比林法测试苯酚浓度,计算苯酚去除效果。
实施例2
一种改性分子筛复合柔性陶瓷纳米纤维材料的方法,具体步骤如下:
(1)负载有活性组分的分子筛的制备;
通过将分子筛(钛硅分子筛TS-1)浸渍于温度为30℃的金属盐溶液中300min后,进行干燥(干燥时间3h,干燥温度110℃)和焙烧(焙烧温度550℃,焙烧时间2h)获得负载有活性组分的分子筛;金属盐溶液中,金属盐为硫酸亚铁,溶剂为水;金属盐溶液中铁的含量为分子筛重量的10wt%;分子筛与金属盐溶液的质量比为1:10;
制得的负载有活性组分的分子筛中的活性组分为氧化铁;
(2)由前驱体溶液经静电纺丝制得杂化纳米纤维膜;
前驱体溶液由含量为20wt%的钛酸四丁酯、含量为2wt%的聚乙烯吡咯烷酮和质量比为7:5的乙醇与冰乙酸的混合物组成;
静电纺丝的参数为:相对湿度40%,温度30℃,电压15kV,灌注速度1.5mL/h,纺丝距离15cm,滚筒速度50r/min,滑台运行速度50cm/min;
(3)将步骤(1)制得的负载有活性组分的分子筛分散在乙醇中,制得浓度为30wt%的负载有活性组分的分子筛分散液,利用静电纺丝装置将其喷涂于步骤(2)所得杂化纳米纤维膜上;
喷涂的参数为:相对湿度40%,温度30℃,电压25kV,灌注速度1.8mL/h,喷涂距离18cm,滚筒速度30r/min,滑台运行速度100cm/min;
(4)在步骤(3)所得材料上,在喷涂分子筛分散液的那一面,重复步骤(2)后,进行煅烧处理制得改性分子筛复合柔性陶瓷纳米纤维材料;
煅烧的参数为:煅烧温度600℃,升温速率5℃/min,保温时间2h。
制得的改性分子筛复合柔性陶瓷纳米纤维材料,包含2层柔性二氧化钛纳米纤维膜(由杂化纳米纤维膜经过煅烧处理制得)以及封装于相邻两层柔性陶瓷纳米纤维膜之间的负载有活性组分的分子筛;柔性陶瓷纳米纤维膜的比表面积为156m2/g,厚度为30μm,纤维直径为200nm~300nm;活性组分在分子筛上的负载量为9.3wt%;改性分子筛复合柔性陶瓷纳米纤维材料中负载有活性组分的分子筛的含量为50wt%。
应用:将改性分子筛复合柔性陶瓷纳米纤维材料用于催化氧化降解工业废水,改性分子筛复合柔性陶瓷纳米纤维材料通过臭氧催化氧化法1h内对苯甲酸钠的降解率达到87%,通过过硫酸盐氧化法1h内对苯酚的降解率达到86%;测试方法如实施例1。
实施例3
一种改性分子筛复合柔性陶瓷纳米纤维材料的方法,具体步骤如下:
(1)负载有活性组分的分子筛的制备;
通过将分子筛(13x分子筛)浸渍于温度为40℃的金属盐溶液中240min后,进行干燥(干燥时间3h,干燥温度110℃)和焙烧(焙烧温度550℃,焙烧时间2h)获得负载有活性组分的分子筛;金属盐溶液中,金属盐为硝酸铜,溶剂为水;金属盐溶液中铜的含量为分子筛重量的5wt%;分子筛与金属盐溶液的质量比为1:10;
制得的负载有活性组分的分子筛中的活性组分为氧化铜;
(2)由前驱体溶液经静电纺丝制得杂化纳米纤维膜;
前驱体溶液由含量为20wt%的六甲基二氧硅烷、含量为1wt%的聚乙烯吡咯烷酮和甲醇组成;
静电纺丝的参数为:相对湿度55%,温度18℃,电压5kV,灌注速度0.1mL/h,纺丝距离10cm,滚筒速度5r/min,滑台运行速度5cm/min;
(3)将步骤(1)制得的负载有活性组分的分子筛分散在冰乙酸中,制得浓度为10wt%的负载有活性组分的分子筛分散液,利用静电纺丝装置将其喷涂于步骤(2)所得杂化纳米纤维膜上;
喷涂的参数为:相对湿度55%,温度18℃,电压10kV,灌注速度0.1mL/h,喷涂距离10cm,滚筒速度5r/min,滑台运行速度5cm/min;
(4)在步骤(3)所得材料上,在喷涂分子筛分散液的那一面,重复步骤(2)后,进行煅烧处理制得改性分子筛复合柔性陶瓷纳米纤维材料;
煅烧的参数为:煅烧温度400℃,升温速率2℃/min,保温时间2h。
制得的改性分子筛复合柔性陶瓷纳米纤维材料,包含2层柔性二氧化硅纳米纤维膜(由杂化纳米纤维膜经过煅烧处理制得)以及封装于相邻两层柔性陶瓷纳米纤维膜之间的负载有活性组分的分子筛;柔性陶瓷纳米纤维膜的比表面积为40m2/g,厚度为10μm,纤维直径为500~600nm;活性组分在分子筛上的负载量为3wt%;改性分子筛复合柔性陶瓷纳米纤维材料中负载有活性组分的分子筛的含量为20wt%。
应用:将改性分子筛复合柔性陶瓷纳米纤维材料用于催化氧化降解工业废水,改性分子筛复合柔性陶瓷纳米纤维材料通过臭氧催化氧化法1h内对苯甲酸钠的降解率达到85%,通过过硫酸盐氧化法1h内对苯酚的降解率达到85%;测试方法如实施例1。
实施例4
一种改性分子筛复合柔性陶瓷纳米纤维材料的方法,具体步骤如下:
(1)负载有活性组分的分子筛的制备;
通过将分子筛(SAPO-34分子筛)浸渍于温度为50℃的金属盐溶液中180min后,进行干燥(干燥时间6h,干燥温度110℃)和焙烧(焙烧温度550℃,焙烧时间2h)获得负载有活性组分的分子筛;金属盐溶液中,金属盐为硝酸锰,溶剂为水;金属盐溶液中锰的含量为分子筛重量的20wt%;分子筛与金属盐溶液的质量比为1:40;
制得的负载有活性组分的分子筛中的活性组分为氧化锰;
(2)由前驱体溶液经静电纺丝制得杂化纳米纤维膜;
前驱体溶液由含量为10wt%的硅酸钠、含量为5wt%的质量比为1:1的聚氧化乙烯与聚乙烯醇缩丁醛的混合物和N,N-二甲基甲酰胺组成;
静电纺丝的参数为:相对湿度40%,温度25℃,电压20kV,灌注速度10mL/h,纺丝距离40cm,滚筒速度100r/min,滑台运行速度100cm/min;
(3)将步骤(1)制得的负载有活性组分的分子筛分散在水中,制得浓度为26wt%的负载有活性组分的分子筛分散液,利用静电纺丝装置将其喷涂于步骤(2)所得杂化纳米纤维膜上;
喷涂的参数为:相对湿度40%,温度25℃,电压30kV,灌注速度10mL/h,喷涂距离40cm,滚筒速度80r/min,滑台运行速度100cm/min;
(4)在步骤(3)所得材料上,在喷涂分子筛分散液的那一面,重复步骤(2)后,进行煅烧处理制得改性分子筛复合柔性陶瓷纳米纤维材料;
煅烧的参数为:煅烧温度1000℃,升温速率3℃/min,保温时间2h。
制得的改性分子筛复合柔性陶瓷纳米纤维材料,包含2层柔性二氧化硅纳米纤维膜(由杂化纳米纤维膜经过煅烧处理制得)以及封装于相邻两层柔性陶瓷纳米纤维膜之间的负载有活性组分的分子筛;柔性陶瓷纳米纤维膜的比表面积为169m2/g,厚度为40μm,纤维直径为200nm~300nm;活性组分在分子筛上的负载量为18wt%;改性分子筛复合柔性陶瓷纳米纤维材料中负载有活性组分的分子筛的含量为48wt%。
应用:将改性分子筛复合柔性陶瓷纳米纤维材料用于催化氧化降解工业废水,改性分子筛复合柔性陶瓷纳米纤维材料通过臭氧催化氧化法1h内对苯甲酸钠的降解率达到92%,通过过硫酸盐氧化法1h内对苯酚的降解率达到93%;测试方法如实施例1。
实施例5
一种改性分子筛复合柔性陶瓷纳米纤维材料的方法,具体步骤如下:
(1)负载有活性组分的分子筛的制备;
通过将分子筛(ZSM-5分子筛)浸渍于温度为60℃的金属盐溶液中120min后,进行干燥(干燥时间6h,干燥温度110℃)和焙烧(焙烧温度550℃,焙烧时间2h)获得负载有活性组分的分子筛;金属盐溶液中,金属盐为氯化锰,溶剂为乙醇;金属盐溶液中锰的含量为分子筛重量的80wt%;分子筛与金属盐溶液的质量比为1:60;
制得的负载有活性组分的分子筛中的活性组分为氧化锰;
(2)由前驱体溶液经静电纺丝制得杂化纳米纤维膜;
前驱体溶液由含量为30wt%的质量比为1:1的正硅酸乙酯和硅酸钠的混合物、含量为10wt%的聚氧化乙烯和质量比为1:1的丙二醇和仲丁醇混合物组成;
静电纺丝的参数为:相对湿度35%,温度26℃,电压25kV,灌注速度1mL/h,纺丝距离16cm,滚筒速度20r/min,滑台运行速度30cm/min;
(3)将步骤(1)制得的负载有活性组分的分子筛分散在N,N-二甲基甲酰胺中,制得浓度为32wt%的负载有活性组分的分子筛分散液,利用静电纺丝装置将其喷涂于步骤(2)所得杂化纳米纤维膜上;
喷涂的参数为:相对湿度35%,温度26℃,电压20kV,灌注速度5mL/h,喷涂距离16cm,滚筒速度20r/min,滑台运行速度20cm/min;
(4)在步骤(3)所得材料上,在喷涂分子筛分散液的那一面,重复步骤(2)后,进行煅烧处理制得改性分子筛复合柔性陶瓷纳米纤维材料;
煅烧的参数为:煅烧温度700℃,升温速率6℃/min,保温时间3h。
制得的改性分子筛复合柔性陶瓷纳米纤维材料,包含2层柔性二氧化硅纳米纤维膜(由杂化纳米纤维膜经过煅烧处理制得)以及封装于相邻两层柔性陶瓷纳米纤维膜之间的负载有活性组分的分子筛;柔性陶瓷纳米纤维膜的比表面积为183m2/g,厚度为35μm,纤维直径为100~200nm;活性组分在分子筛上的负载量为62wt%;改性分子筛复合柔性陶瓷纳米纤维材料中负载有活性组分的分子筛的含量为57wt%。
应用:将改性分子筛复合柔性陶瓷纳米纤维材料用于催化氧化降解工业废水,改性分子筛复合柔性陶瓷纳米纤维材料通过臭氧催化氧化法1h内对苯甲酸钠的降解率达到99%,通过过硫酸盐氧化法1h内对苯酚的降解率达到98%;测试方法如实施例1。
实施例6
一种改性分子筛复合柔性陶瓷纳米纤维材料的方法,具体步骤如下:
(1)负载有活性组分的分子筛的制备;
通过将分子筛(钛硅分子筛TS-1)浸渍于温度为80℃的金属盐溶液中10min后,进行干燥(干燥时间6h,干燥温度110℃)和焙烧(焙烧温度550℃,焙烧时间2h)获得负载有活性组分的分子筛;金属盐溶液中,金属盐为硝酸钴,溶剂为乙醇;金属盐溶液中钴的含量为分子筛重量的60wt%;分子筛与金属盐溶液的质量比为1:80;
制得的负载有活性组分的分子筛中的活性组分为氧化钴;
(2)由前驱体溶液经静电纺丝制得杂化纳米纤维膜;
前驱体溶液由含量为50wt%的钛酸异丙酯、含量为7wt%的聚乙烯醇缩丁醛和正丙醇组成;
静电纺丝的参数为:相对湿度35%,温度35℃,电压30kV,灌注速度6mL/h,纺丝距离26cm,滚筒速度60r/min,滑台运行速度50cm/min;
(3)将步骤(1)制得的负载有活性组分的分子筛分散在水中,制得浓度为38wt%的负载有活性组分的分子筛分散液,利用静电纺丝装置将其喷涂于步骤(2)所得杂化纳米纤维膜上;
喷涂的参数为:相对湿度35%,温度35℃,电压22kV,灌注速度7mL/h,喷涂距离26cm,滚筒速度55r/min,滑台运行速度40cm/min;
(4)在步骤(3)所得材料上,在喷涂分子筛分散液的那一面,重复步骤(2)后,进行煅烧处理制得改性分子筛复合柔性陶瓷纳米纤维材料;
煅烧的参数为:煅烧温度800℃,升温速率7℃/min,保温时间4h。
制得的改性分子筛复合柔性陶瓷纳米纤维材料,包含2层柔性二氧化钛纳米纤维膜(由杂化纳米纤维膜经过煅烧处理制得)以及封装于相邻两层柔性陶瓷纳米纤维膜之间的负载有活性组分的分子筛;柔性陶瓷纳米纤维膜的比表面积为176m2/g,厚度为80μm,纤维直径为400~500nm;活性组分在分子筛上的负载量为37wt%;改性分子筛复合柔性陶瓷纳米纤维材料中负载有活性组分的分子筛的含量为65wt%。
应用:将改性分子筛复合柔性陶瓷纳米纤维材料用于催化氧化降解工业废水,改性分子筛复合柔性陶瓷纳米纤维材料通过臭氧催化氧化法1h内对苯甲酸钠的降解率达到96%,通过过硫酸盐氧化法1h内对苯酚的降解率达到95%;测试方法如实施例1。
实施例7
一种改性分子筛复合柔性陶瓷纳米纤维材料的方法,具体步骤如下:
(1)负载有活性组分的分子筛的制备;
通过将分子筛(ZSM-5分子筛)浸渍于温度为70℃的金属盐溶液中200min后,进行干燥(干燥时间36h,干燥温度110℃)和焙烧(焙烧温度550℃,焙烧时间2h)获得负载有活性组分的分子筛;金属盐溶液中,金属盐为质量比为1:1硝酸铁和硝酸锰的混合物,溶剂为质量比1:1的水和乙醇的混合物;金属盐溶液中铁和锰的含量为分子筛重量的40wt%;分子筛与金属盐溶液的质量比为1:100;
制得的负载有活性组分的分子筛中的活性组分为氧化铁和氧化锰;
(2)由前驱体溶液经静电纺丝制得杂化纳米纤维膜;
前驱体溶液由含量为25wt%的钛酸四乙酯、含量为3wt%的聚已烯醇和正丁醇组成;
静电纺丝的参数为:相对湿度30%,温度20℃,电压10V,灌注速度2mL/h,纺丝距离14cm,滚筒速度10r/min,滑台运行速度10cm/min;
(3)将步骤(1)制得的负载有活性组分的分子筛分散在质量比为1:1的水和冰乙酸的混合溶液中,制得浓度为50wt%的负载有活性组分的分子筛分散液,利用静电纺丝装置将其喷涂于步骤(2)所得杂化纳米纤维膜上;
喷涂的参数为:相对湿度30%,温度20℃,电压15kV,灌注速度3mL/h,喷涂距离13cm,滚筒速度10r/min,滑台运行速度10cm/min;
(4)在步骤(3)所得材料上,在喷涂分子筛分散液的那一面,依次重复步骤(2)、步骤(3)、步骤(2)后,进行煅烧处理制得改性分子筛复合柔性陶瓷纳米纤维材料;
煅烧的参数为:煅烧温度500℃,升温速率10℃/min,保温时间6h。
制得的改性分子筛复合柔性陶瓷纳米纤维材料,包含3层柔性二氧化钛纳米纤维膜(由杂化纳米纤维膜经过煅烧处理制得)以及封装于相邻两层柔性陶瓷纳米纤维膜之间的负载有活性组分的分子筛;柔性陶瓷纳米纤维膜的比表面积为200m2/g,厚度为100μm,纤维直径为300nm~400nm;活性组分在分子筛上的负载量为65wt%;改性分子筛复合柔性陶瓷纳米纤维材料中负载有活性组分的分子筛的含量为90wt%;
应用:将改性分子筛复合柔性陶瓷纳米纤维材料用于催化氧化降解工业废水,改性分子筛复合柔性陶瓷纳米纤维材料通过臭氧催化氧化法1h内对苯甲酸钠的降解率达到100%,通过过硫酸盐氧化法1h内对苯酚的降解率达到100%;测试方法如实施例1。
实施例8
一种改性分子筛复合柔性陶瓷纳米纤维材料的方法,具体步骤如下:
(1)由前驱体溶液经静电纺丝制得杂化纳米纤维膜;
前驱体溶液由含量为50wt%的钛酸异丙酯、含量为7wt%的聚乙烯醇缩丁醛和正丙醇组成;
静电纺丝的参数为:相对湿度35%,温度35℃,电压30kV,灌注速度6mL/h,纺丝距离26cm,滚筒速度60r/min,滑台运行速度50cm/min;
(2)将分子筛(钛硅分子筛TS-1)分散在水中,制得浓度为38wt%的分子筛分散液,利用静电纺丝装置将其喷涂于步骤(1)所得杂化纳米纤维膜上;
喷涂的参数为:相对湿度35%,温度35℃,电压22kV,灌注速度7mL/h,喷涂距离26cm,滚筒速度55r/min,滑台运行速度40cm/min;
(3)在步骤(2)所得材料上,在喷涂分子筛分散液的那一面,重复步骤(1)后,进行煅烧处理制得改性分子筛复合柔性陶瓷纳米纤维材料;
煅烧的参数为:煅烧温度800℃,升温速率7℃/min,保温时间4h。
制得的改性分子筛复合柔性陶瓷纳米纤维材料,包含2层柔性二氧化钛纳米纤维膜(由杂化纳米纤维膜经过煅烧处理制得)以及封装于相邻两层柔性陶瓷纳米纤维膜之间的分子筛;柔性陶瓷纳米纤维膜的比表面积为176m2/g,厚度为80μm,纤维直径为400~500nm。
应用:改性分子筛复合柔性陶瓷纳米纤维材料用于氮氧分离。
实施例9
一种改性分子筛复合柔性陶瓷纳米纤维材料的方法,具体步骤如下:
(1)由前驱体溶液经静电纺丝制得杂化纳米纤维膜;
前驱体溶液由含量为30wt%的质量比为1:1的正硅酸乙酯和硅酸钠的混合物、含量为10wt%的聚氧化乙烯和质量比为1:1的丙二醇和仲丁醇混合物组成;
静电纺丝的参数为:相对湿度35%,温度26℃,电压25kV,灌注速度1mL/h,纺丝距离16cm,滚筒速度20r/min,滑台运行速度30cm/min;
(2)将分子筛(ZSM-5分子筛)分散在N,N-二甲基甲酰胺中,制得浓度为32wt%的分子筛分散液,利用静电纺丝装置将其喷涂于步骤(1)所得杂化纳米纤维膜上;
喷涂的参数为:相对湿度35%,温度26℃,电压20kV,灌注速度5mL/h,喷涂距离16cm,滚筒速度20r/min,滑台运行速度20cm/min;
(3)在步骤(2)所得材料上,在喷涂分子筛分散液的那一面,重复步骤(1)后,进行煅烧处理制得改性分子筛复合柔性陶瓷纳米纤维材料;
煅烧的参数为:煅烧温度700℃,升温速率6℃/min,保温时间3h。
制得的改性分子筛复合柔性陶瓷纳米纤维材料,包含2层柔性二氧化硅纳米纤维膜(由杂化纳米纤维膜经过煅烧处理制得)以及封装于相邻两层柔性陶瓷纳米纤维膜之间的分子筛;柔性陶瓷纳米纤维膜的比表面积为183m2/g,厚度为35μm,纤维直径为100~200nm。
应用:改性分子筛复合柔性陶瓷纳米纤维材料用于氮氧分离。

Claims (6)

1.一种改性分子筛复合柔性陶瓷纳米纤维材料,其特征在于,包含两层以上柔性陶瓷纳米纤维膜以及封装于相邻两层柔性陶瓷纳米纤维膜之间的分子筛;
柔性陶瓷纳米纤维膜的比表面积为40~200m²/g,厚度为10~100μm,纤维直径为100~600nm;改性分子筛复合柔性陶瓷纳米纤维材料中分子筛的含量为20~90wt%;
分子筛上还负载有活性组分;活性组分在分子筛上的负载量为3~65wt%;
改性分子筛复合柔性陶瓷纳米纤维材料用于催化氧化降解工业废水。
2.根据权利要求1所述的一种改性分子筛复合柔性陶瓷纳米纤维材料,其特征在于,柔性陶瓷纳米纤维膜为柔性二氧化硅纳米纤维膜或柔性二氧化钛纳米纤维膜。
3.根据权利要求1所述的一种改性分子筛复合柔性陶瓷纳米纤维材料,其特征在于,活性组分为金属氧化物;负载有活性组分的分子筛是通过将分子筛浸渍于金属盐溶液中后进行干燥和焙烧获得的;金属盐溶液中金属元素的含量为分子筛重量的5~80wt%;分子筛与金属盐溶液的质量比为1:10~100;浸渍时间为10~360min,温度为20~80℃。
4.根据权利要求3所述的一种改性分子筛复合柔性陶瓷纳米纤维材料,其特征在于,金属盐为硝酸铁、硫酸亚铁、硝酸锰、氯化锰、硝酸铜和硝酸钴中的一种以上;金属盐溶液中的溶剂为水和/或乙醇。
5.制备如权利要求1~4任一项所述的一种改性分子筛复合柔性陶瓷纳米纤维材料的方法,其特征在于,在同一接收基材上先后交替进行杂化纳米纤维膜的沉积和分子筛分散液的喷涂,并控制沉积次数比喷涂次数多一次后,进行煅烧处理制得改性分子筛复合柔性陶瓷纳米纤维材料;
杂化纳米纤维膜由前驱体溶液经静电纺丝制得,前驱体溶液包含陶瓷前驱体、高分子聚合物和溶剂。
6.根据权利要求5所述的方法,其特征在于,陶瓷前驱体为正硅酸乙酯、硅酸钠、六甲基二氧硅烷、钛酸四丁酯、钛酸异丙酯和钛酸四乙酯中的一种以上;
高分子聚合物为聚已烯醇、聚乙烯吡咯烷酮、聚氧化乙烯和聚乙烯醇缩丁醛中的一种以上;
前驱体溶液中的溶剂为水、冰乙酸、甲醇、乙醇、正丙醇、正丁醇、乙二醇、丙二醇、仲丁醇和N,N-二甲基甲酰胺中的一种以上;
前驱体溶液中,陶瓷前驱体的含量为10~50wt%,高分子聚合物的含量为1~10wt%;
静电纺丝的参数为:相对湿度25~55%,温度18~35℃,电压5~30kV,灌注速度0.1~10mL/h,纺丝距离10~40cm,滚筒速度5~100r/min,滑台运行速度5~100cm/min;
分子筛分散液中的溶剂为水、冰乙酸、乙醇和N,N-二甲基甲酰胺中的一种以上;分子筛分散液的浓度为10~50wt%;
喷涂采用静电纺丝装置;喷涂的参数为:相对湿度25~55%,温度18~35℃,电压10~30kV,灌注速度0.1~10mL/h,喷涂距离10~40cm,滚筒速度5~80r/min,滑台运行速度5~100cm/min;
煅烧的参数为:煅烧温度400~1000℃,升温速率2~10℃/min,保温时间0~6h。
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