CN108143543A - 多层组合生物降解芯体及其制备方法 - Google Patents

多层组合生物降解芯体及其制备方法 Download PDF

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CN108143543A
CN108143543A CN201711408182.6A CN201711408182A CN108143543A CN 108143543 A CN108143543 A CN 108143543A CN 201711408182 A CN201711408182 A CN 201711408182A CN 108143543 A CN108143543 A CN 108143543A
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CN108143543B (zh
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王伟
祝二斌
翁文伟
罗梅芳
吴晓彪
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Fujian Hengan Household Life Article Co Ltd
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Abstract

本发明公开一种多层组合生物降解芯体制备方法。包括如下步骤:(1)制备第一纤网层、第二纤网层、第三纤网层和底层;(2)将第一纤网层、第二纤网层、第三纤网层和底层由上到下进行粘合,并在第一纤网层和第二纤网层中间填充分子筛,在第二纤网层和第三纤网层之间填充可生物降解高吸水性树脂获得多层组合生物降解芯体。本发明多层组合生物降解芯体制备方法,通过制备的第一纤网层、第二纤网层和第三纤网层能够提高芯体的吸湿性能,通过在第一纤网层和第二纤网层中间填充分子筛,能够去除异味,通过在第二纤网层和第三纤网层中间填充可生物降解高吸水性树脂,进一步提高了芯体的吸水能力,使其更加舒适。

Description

多层组合生物降解芯体及其制备方法
技术领域
本发明涉及一种多层组合生物降解芯体及其制备方法。
背景技术
纸尿裤、纸尿片和卫生巾是一种用完即丢的一次性卫生用品,因其无需洗涤、舒适方便等性能而被广大消费所接受。为了增加纸尿裤、纸尿片或卫生巾吸湿性能,通常会在纸尿裤、纸尿片或卫生巾内添加芯体,然而传统的芯体只是单纯的提高了纸尿裤、纸尿片或卫生巾的吸湿性能,其抗菌、除异味功能效果较差且不能降解。
发明内容
针对上述问题,本发明提供一种多层组合生物降解芯体制备方法。
为达到上述目的,本发明一种多层组合生物降解芯体方法,包括如下步骤,
包括如下步骤,
(1)制备第一纤网层、第二纤网层、第三纤网层和底层;
(2)将第一纤网层、第二纤网层、第三纤网层和黏胶层由上到下进行粘合,并在第一纤网层和第二纤网层中间填充分子筛,在第二纤网层和第三纤网层之间填充可生物降解高吸水性树脂获得多层组合生物降解芯体。
进一步地,所述第一纤网层的制备方法为,将聚羟基戊酸酯、聚羟基丁酸酯和聚乳酸按照预定比例混合得到第一混合材料;
利用第一混合材料制成第一母粒,并对第一母粒进行纺丝制成第一纤维;
将第一纤维气流成网后,对网状结构进行热压粘合得到第一纤网层。
进一步地,所述第二纤网层的制备方法为:
获取麻纤维,并将麻纤维置于艾草提取物中,在5-10℃的温度下浸泡10-20min,再以5℃/min的速度升温至50-60℃,恒温保持30-40min,冷却至室温后并进出晾干处理得到处理后的麻纤维;
将处理后的麻纤维与竹纤维混纺得到第二纤维,将第二纤维编制成网状结构,并对网状结构进行粘合得到第二纤网层。
进一步地,所述第三纤网层的制备方法为:
将聚丁二酸丁二醇脂、聚己内酯和竹炭粉按照预定比例混合并搅拌得到第二混合材料;
利用第二混合材料制成第二母粒,并对第二母粒进行熔融纺丝处理得到第三纤维;
将第三纤维气流成网后对网状结构进行热压粘合得到第三纤网层。
进一步地,所述底层的制备方法为:将聚己二酸/对苯二甲酸丁二酯和聚羟基脂肪酸酯按照2:1的比例混合并搅拌得到第三混合材料;
利用第三混合材料制成第三母粒,并对第三母粒进行纺丝制成第三纤维;
将第三纤维气流成网后,对网状结构进行热压粘合得到底层。
进一步地,所述聚羟基戊酸酯的质量份为5-10份,聚羟基丁酸酯的质量份为5-10份,聚乳酸的质量份为20-30份。
进一步地,所述麻纤维与竹纤维的质量比为1:3。
进一步地,聚丁二酸丁二醇脂的质量份为5-10份,聚己内酯的质量份为15-20份,竹炭粉的质量份为1-5份。
进一步地,所述分子筛的制备方法为将金银花、绿茶叶和沸石磨成粉,按照1:1:4的比例进行混合,混合后挤出造粒得到分子筛颗粒;将分子筛颗粒置于薄荷提取物中在20-30℃的温度下浸泡1-2小时后,以5℃/min的速率升温至50-60℃,恒温保持1小时后取出冷却至室温,对冷却至室温的分子筛颗进行晾干处理得到分子筛。
本发明多层组合生物降解芯体制备方法,通过制备的第一纤网层、第二纤网层和第三纤网层能够提高芯体的吸湿性能,通过在第一纤网层和第二纤网层中间填充分子筛,能够去除异味,通过在第二纤网层和第三纤网层中间填充可生物降解高吸水性树脂,进一步提高了芯体的吸水能力,使其更加舒适,与此同时,本发明中的第一纤网层、第二纤网层和第三纤网层均由可降级材料制得,使用之后能够在一定的时间内降解,减少了对的环境污染,较为环保。
为达到上述目的,本发明一种多层组合生物降解芯体,按照上述的多层组合生物降解芯体制备方法制得。
本发明多层组合生物降解芯体,通过设置的第一纤网层、第二纤网层和第三纤网层能够提高芯体的吸湿性能,通过在第一纤网层和第二纤网层中间填充分子筛,能够去除异味,通过在第二纤网层和第三纤网层中间填充可生物降解高吸水性树脂,进一步提高了芯体的吸水能力,使其更加舒适。
具体实施方式
实施例1
本实施例提供一种多层组合生物降解芯体制备方法,包括如下步骤:
(1)制备第一纤网层、第二纤网层、第三纤网层和底层;
(2)将第一纤网层、第二纤网层、第三纤网层和黏胶层由上到下进行粘合,并在第一纤网层和第二纤网层中间填充分子筛,在第二纤网层和第三纤网层之间填充可生物降解高吸水性树脂获得多层组合生物降解芯体。
本实施例中第一纤网层的制备方法为,将聚羟基戊酸酯、聚羟基丁酸酯和聚乳酸按照预定比例混合得到第一混合材料;其中,聚羟基戊酸酯的质量份为5-10份,聚羟基丁酸酯的质量份为5-10份,聚乳酸的质量份为20-30份;利用第一混合材料制成第一母粒,并对第一母粒进行纺丝制成第一纤维;将第一纤维气流成网后,对网状结构进行热压粘合得到第一纤网层。
第二纤网层的制备方法为:
获取麻纤维,并将麻纤维置于艾草提取物中,在5-10℃的温度下浸泡10-20min,再以5℃/min的速度升温至50-60℃,恒温保持30-40min,冷却至室温后并进出晾干处理得到处理后的麻纤维;将处理后的麻纤维与竹纤维按照质量比1:3的比例混纺得到第二纤维,将第二纤维编制成网状结构,并对网状结构进行粘合得到第二纤网层。
第三纤网层的制备方法为:
将聚丁二酸丁二醇脂、聚己内酯和竹炭粉按照预定比例混合搅拌得到第二混合材料,其中,聚丁二酸丁二醇脂的质量份为5-10份,聚己内酯的质量份为15-20份,竹炭粉的质量份为1-5份;利用第二混合材料制成第二母粒,并对第二母粒进行熔融纺丝处理得到第三纤维;将第三纤维气流成网后对网状结构进行热压粘合得到第三纤网层。
具体的,底层的制备方法为:将聚己二酸/对苯二甲酸丁二酯和聚羟基脂肪酸酯按照质量比2:1的比例混合并搅拌得到第三混合材料;利用第三混合材料制成第三母粒,并对第三母粒进行纺丝制成第四纤维;
将第四纤维气流成网后,对网状结构进行热压粘合得到底层。
本实施例中的第一纤网层、第二纤网层和第三纤网层均由可降级材料制得,降解性能好,使用之后能够在一定的时间内降解,因此不会对环境造成污染,较为环保。
本实施例中可生物降解高吸水性树脂为采用丙烯酸与改性纤维素类或海藻酸系类进行交联制备而得。
实施例2
作为实施例1的具体方案,本实施例中分子筛的制备方法为将金银花、绿茶叶和沸石磨成粉,并按照质量比1:1:4的比例进行混合,混合后挤出造粒得到分子筛颗粒;将分子筛颗粒置于薄荷提取物中在20-30℃的温度下浸泡1-2小时后,以5℃/min的速率升温至50-60℃,恒温保持1小时后取出冷却至室温,对冷却至室温的分子筛颗进行晾干处理得到分子筛。
本发明多层组合生物降解芯体制备方法,通过制备的第一纤网层、第二纤网层和第三纤网层能够提高芯体的吸湿性能,通过在第一纤网层和第二纤网层中间填充分子筛,能够去除异味,通过在第二纤网层和第三纤网层中间填充可生物降解高吸水性树脂,进一步提高了芯体的吸水能力,使其更加舒适。
实施例3
本实施例提供一种多层组合生物降解芯体,按照如上所述的多层组合生物降解芯体制备方法制得。
本发明多层组合生物降解芯体能够应用在卫生用品领域,不但具有较好的吸湿性能,还具有抗菌除异味功能,除此之外,本发明还具有较好的降解性能,能够降解,非常环保。
实施例4
作为实施例1的具体方案,本实施中还包括制备水刺布,并将制得的水刺布包覆在生物降解芯体外;其中,水刺布包括基础层、吸水层和功能层,所述基础层、吸水层和功能层由上至下依次设置并通过水刺加固连接;
所述基础层包括第一植物纤维61-71质量份和细旦合成纤维29-39质量份;所述吸水层为第二植物纤维层;所述功能层包括第三植物纤维65-75质量份和细旦合成纤维25-35质量份;
所述基础层平方克重占总平方克重的35%;所述吸水层平方克重占总平方克重的40%;功能层平方克重占总平方克重的25%;
所述第一植物纤维包括质量份数分别为80-100份的竹浆和10-20份茶树木浆;
所述第二植物纤维包括质量份数分别为30-40份的竹浆和40-60份茶树木浆;
所述第三植物纤维包括质量份数分别为50-70份的竹浆、20-30份茶树木浆、8-15份蛇床子草浆和8-15份黄柏浆;
所述竹浆中的竹纤维长度大于10mm。
具体的,所述第一植物纤维包括质量份数分别为90份的竹浆和16份茶树木浆;
所述第二植物纤维包括质量份数分别为35份的竹浆和50份茶树木浆;
所述第三植物纤维包括质量份数分别为62份的竹浆、27份茶树木浆、12份蛇床子草浆和11份黄柏浆。
具体的,水刺非织造布的制造方法如下:
由上至下依次铺设基础层、吸水层和功能层,通过水刺进行相互缠结,得到水刺非织造布;
将水刺非织造布用真空吸水箱去除水分至湿度为50%-70%;
脱水处理后的水刺非织造布进行喷涂一种改性羧甲基纤维素钠,改性羧甲基纤维素钠的浓度为1-5%;
将喷涂处理后的水刺非织造布烘干,得到复合水刺非织造布。
其中,基础层的制造方法如下:
(1)取10-20份茶树木浆50-70圈/分钟的速度低速的搅拌状态下,以20份/分钟的速度添加80-100份的竹浆,保持搅拌5-9分钟制成混合浆料;
(2)将混合浆料和42-66份的细旦合成纤维加入气流成网机,采用气流成网方法铺网制成纤维网。
其中,功能层的制造方法如下:
(1)取20-30份茶树木浆70-100圈/分钟的速度低速的搅拌状态下,以30份/分钟的速度添加8-15份蛇床子草浆和8-15份黄柏浆,保持搅拌10-20分钟;
(2)再在70-100圈/分钟的速度低速的搅拌状态下,以30份/分钟的速度添加50-70份的竹浆,保持搅拌40-60分钟;
(3)将混合浆料和33-60份的细旦合成纤维加入气流成网机,采用气流成网方法铺网制成纤维网。
其中,吸水层的制造方法如下:
(1)取20-30份茶树木浆70-100圈/分钟的速度低速的搅拌状态下,以30份/分钟的速度添加8-15份蛇床子草浆和8-15份黄柏浆,保持搅拌10-20分钟;
(2)再在70-100圈/分钟的速度低速的搅拌状态下,以30份/分钟的速度添加50-70份的竹浆,保持搅拌40-60分钟;
(3)将混合浆料以10-15℃/分钟的速度升温至90-105℃,以3份/分钟的速度添加质量份数为3-5份的湿强剂,搅拌混合;
(4)将混合后的浆料采用湿法成网方法铺网制成纤维网。
以上,仅为本发明的较佳实施例,但本发明的保护范围并不局限于此,任何熟悉本技术领域的技术人员在本发明揭露的技术范围内,可轻易想到的变化或替换,都应涵盖在本发明的保护范围之内。因此,本发明的保护范围应该以权利要求所界定的保护范围为准。

Claims (10)

1.一种多层组合生物降解芯体制备方法,其特征在于,包括如下步骤,
(1)制备第一纤网层、第二纤网层、第三纤网层和底层;
(2)将第一纤网层、第二纤网层、第三纤网层和底层由上到下进行粘合,并在第一纤网层和第二纤网层中间填充分子筛,在第二纤网层和第三纤网层之间填充可生物降解高吸水性树脂获得多层组合生物降解芯体。
2.根据权利要求1所述的多层组合生物降解芯体制备方法,其特征在于,所述第一纤网层的制备方法为,将聚羟基戊酸酯、聚羟基丁酸酯和聚乳酸按照预定比例混合得到第一混合材料;
利用第一混合材料制成第一母粒,并对第一母粒进行纺丝制成第一纤维;
将第一纤维气流成网后,对网状结构进行热压粘合得到第一纤网层。
3.根据权利要求1所述的多层组合生物降解芯体制备方法,其特征在于,所述第二纤网层的制备方法为:
获取麻纤维,并将麻纤维置于艾草提取物中,在5-10℃的温度下浸泡10-20min,再以5℃/min的速度升温至50-60℃,恒温保持30-40min,冷却至室温后并进出晾干处理得到处理后的麻纤维;
将处理后的麻纤维与竹纤维混纺得到第二纤维,将第二纤维编制成网状结构,并对网状结构进行粘合得到第二纤网层。
4.根据权利要求1所述的多层组合生物降解芯体制备方法,其特征在于,所述第三纤网层的制备方法为:
将聚丁二酸丁二醇脂、聚己内酯和竹炭粉按照预定比例混合搅拌得到第二混合材料;
利用第二混合材料制成第二母粒,并对第二母粒进行熔融纺丝处理得到第三纤维;
将第三纤维气流成网后对网状结构进行热压粘合得到第三纤网层。
5.根据权利要求1所述的多层组合生物降解芯体制备方法,其特征在于,
所述底层的制备方法为:将聚己二酸/对苯二甲酸丁二酯和聚羟基脂肪酸酯按照质量比2:1的比例混合并搅拌得到第三混合材料;
利用第三混合材料制成第三母粒,并对第三母粒进行纺丝制成第四纤维;
将第四纤维气流成网后,对网状结构进行热压粘合得到底层。
6.根据权利要求2所述的多层组合生物降解芯体制备方法,其特征在于,所述聚羟基戊酸酯的质量份为5-10份,聚羟基丁酸酯的质量份为5-10份,聚乳酸的质量份为20-30份。
7.根据权利要求3所述的多层组合生物降解芯体制备方法,其特征在于,所述麻纤维与竹纤维的质量比为1:3。
8.根据权利要求4所述的多层组合生物降解芯体制备方法,其特征在于,聚丁二酸丁二醇脂的质量份为5-10份,聚己内酯的质量份为15-20份,竹炭粉的质量份为1-5份。
9.根据权利要求1所述的多层组合生物降解芯体制备方法,其特征在于,所述分子筛的制备方法为将金银花、绿茶叶和沸石磨成粉,按照质量比1:1:4的比例进行混合,混合后挤出造粒得到分子筛颗粒;将分子筛颗粒置于薄荷提取物中在20-30℃的温度下浸泡1-2小时后,以5℃/min的速率升温至50-60℃,恒温保持1小时后取出冷却至室温,对冷却至室温的分子筛颗进行晾干处理得到分子筛。
10.一种多层组合生物降解芯体,其特征在于,按照权利要求1-9所述的多层组合生物降解芯体制备方法制得。
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