CN108704615A - 一种活性炭吸附剂及其制备方法 - Google Patents
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Abstract
本发明提供一种活性炭吸附剂及其制备方法,包括改性活性炭600~800份;改性膨润土200~500份、氯化钙200~400份、硅藻土200~400份、环氧树脂粘结剂10~20份,将改性活性炭、改性膨润土、氯化钙、硅藻土和环氧树脂粘结剂混合制粒,烘干后即得。本发明通过活化步骤将活性炭和膨润土先进行活化,然后与氯化钙、硅藻土复合制备活性炭吸附剂,制备得到的吸附剂具有良好的强度和优异的吸附性。
Description
技术领域
本发明涉及一种活性炭吸附剂及其制备方法,属于吸附剂制备领域。
背景技术
空气中的污染物主要是工业燃料燃烧产生的气体、汽车尾气、生产中产生的有毒有害气体。水污染主要是工业生产排放的污水里含有大量有毒物质,还有人们生活中的污水产生很多有害物质。人们生活中也有很多时候需要脱除毒素,比如空调过滤网上有很多细菌、毒素,新装修的间有甲醛等有害物质,都需要脱除毒素。吸附剂能够有效脱除这些有害物质,目前常用到的有硅胶、活性氧化铝、活性炭、分子筛、矿物等,另外还有针对某种组分选择性吸附而研制的吸附材料。但是这些吸附剂大多吸附能力有限,需要针对不同的要求研究不同的吸附剂,以发挥最好的作用,成本较高。
发明内容
发明目的:本发明所要解决的技术问题是针对现有技术的不足,提供一种成本低廉,吸附效果佳的活性炭吸附剂,同时提供该吸附剂的制备方法。
为了解决上述技术问题,本发明公开了一种活性炭吸附剂,包括如下质量份的组份:
其中,所述改性活性炭包括如下重量份的组份:椰壳150~200份,木质活性炭150~200份、煤质活性炭150~200份、花生壳150~200份。
所述改性膨润土为酸化纳化改性膨润土。
本发明还提供上述活性炭吸附剂的制备方法,包括如下步骤:
改性活性炭制备:将活性炭原料与水混合,研磨成泥状,然后加入到氢氧化钾溶液中浸泡2~3h,过滤后水洗、干燥即得;
改性膨润土制备:将膨润土原料粉磨过300目筛,然后在硫酸溶液中浸泡1~2h,过滤后在氢氧化纳溶液中浸泡2~3h,过滤后水洗、干燥,最后在400~500℃下煅烧4~6h即得;
吸附剂制备:将改性活性炭、改性膨润土、氯化钙、硅藻土和环氧树脂粘结剂混合制粒,烘干后即得。
其中,所述氢氧化钾溶液的浓度为20~30wt%,所述活性炭原料与氢氧化钾溶液的质量体积比为0.24~0.5g/ml。
所述硫酸溶液的浓度为30~50wt%,所述膨润土原料与硫酸溶液的质量体积比为0.56~0.8g/ml。
所述氢氧化纳溶液的浓度为25~50wt%,所述膨润土原料与氢氧化纳溶液的质量体积比为0.46~0.58g/ml。
有益效果:
本发明先通过活化步骤将活性炭和膨润土先进行活化,然后与氯化钙、硅藻土复合制备活性炭吸附剂,制备得到的吸附剂具有良好的强度和优异的吸附性。
具体实施方式
实施例1
将椰壳180份,木质活性炭160份、煤质活性炭180份、花生壳150份与30份水混合,研磨成泥状,然后加入到25wt%氢氧化钾溶液中浸泡2.5h,活性炭原料与氢氧化钾溶液的质量体积比为0.42g/ml,过滤后水洗、干燥得改性活性炭;
将膨润土原料350份粉磨过300目筛,然后在40wt%硫酸溶液中浸泡1.5h,膨润土原料与硫酸溶液的质量体积比为0.68g/ml,过滤后在45wt%氢氧化纳溶液中浸泡2.5h,膨润土原料与氢氧化纳溶液的质量体积比为0.52g/ml,过滤后水洗、干燥,最后在450℃下煅烧5h得改性膨润土;
将制备得到的改性活性炭、改性膨润土和氯化钙300份、硅藻土300份以及环氧树脂粘结剂15份混合制成粒径小于0.2cm的颗粒,烘干即得。
实施例2
将椰壳150份,木质活性炭150份、煤质活性炭150份、花生壳150份与20份水混合,研磨成泥状,然后加入到20wt%氢氧化钾溶液中浸泡2h,活性炭原料与氢氧化钾溶液的质量体积比为0.24g/ml,过滤后水洗、干燥得改性活性炭;
将膨润土原料200份粉磨过300目筛,然后在30wt%硫酸溶液中浸泡1h,膨润土原料与硫酸溶液的质量体积比为0.56g/ml,过滤后在25wt%氢氧化纳溶液中浸泡2h,膨润土原料与氢氧化纳溶液的质量体积比为0.46g/ml,过滤后水洗、干燥,最后在400℃下煅烧6h得改性膨润土;
将制备得到的改性活性炭、改性膨润土和氯化钙200份、硅藻土200份以及环氧树脂粘结剂10份混合制成粒径小于0.2cm的颗粒,烘干即得。
实施例3
将椰壳200份,木质活性炭200份、煤质活性炭200份、花生壳200份与40份水混合,研磨成泥状,然后加入到30wt%氢氧化钾溶液中浸泡3h,活性炭原料与氢氧化钾溶液的质量体积比为0.5g/ml,过滤后水洗、干燥得改性活性炭;
将膨润土原料500份粉磨过300目筛,然后在50wt%硫酸溶液中浸泡2h,膨润土原料与硫酸溶液的质量体积比为0.8g/ml,过滤后在50wt%氢氧化纳溶液中浸泡3h,膨润土原料与氢氧化纳溶液的质量体积比为0.58g/ml,过滤后水洗、干燥,最后在500℃下煅烧4h得改性膨润土;
将制备得到的改性活性炭、改性膨润土和氯化钙400份、硅藻土400份以及环氧树脂粘结剂20份混合制成粒径小于0.2cm的颗粒,烘干即得。
实施例4
将椰壳200份,木质活性炭180份、煤质活性炭150份、花生壳150份与30份水混合,研磨成泥状,然后加入到25wt%氢氧化钾溶液中浸泡3h,活性炭原料与氢氧化钾溶液的质量体积比为0.48g/ml,过滤后水洗、干燥得改性活性炭;
将膨润土原料400份粉磨过300目筛,然后在40wt%硫酸溶液中浸泡2h,膨润土原料与硫酸溶液的质量体积比为0.72g/ml,过滤后在40wt%氢氧化纳溶液中浸泡3h,膨润土原料与氢氧化纳溶液的质量体积比为0.56g/ml,过滤后水洗、干燥,最后在450℃下煅烧6h得改性膨润土;
将制备得到的改性活性炭、改性膨润土和氯化钙300份、硅藻土300份以及环氧树脂粘结剂20份混合制成粒径小于0.2cm的颗粒,烘干即得。
实施例5
对实施例1~4制备的活性炭吸附剂的强度和吸附性进行检测,检测结果见表1,其中强度检测参照GB/T12496.6-1999《木质活性炭试验方法强度的测定》,碘吸附值检测参照GB/T12496.8-1999《木质活性炭试验方法碘吸附值的测定》,亚甲基蓝吸附值检测参照GB/T12496.10-1999《木质活性炭试验方法亚甲基蓝吸附值的测定》。
由表1数据可知,实施例1制备的活性炭吸附剂各项参数最高,实施例1~4制备的活性炭吸附剂强度不低于96.7%,碘吸附值1773mg/g,亚甲基蓝吸附值不低于42.56ml/0.1g,远高于一级活性炭的标准值。
表1
实施例 | 强度(%) | 碘吸附值(mg/g) | 亚甲基蓝吸附值(ml/0.1g) |
实施例1 | 98.5 | 1863 | 48.31 |
实施例2 | 96.7 | 1773 | 42.56 |
实施例3 | 97.1 | 1784 | 43.78 |
实施例4 | 97.4 | 1812 | 47.54 |
本发明提供了一种活性炭吸附剂及其制备方法的思路及方法,具体实现该技术方案的方法和途径很多,以上所述仅是本发明的优选实施方式,应当指出,对于本技术领域的普通技术人员来说,在不脱离本发明原理的前提下,还可以做出若干改进和润饰,这些改进和润饰也应视为本发明的保护范围。本实施例中未明确的各组成部分均可用现有技术加以实现。
Claims (7)
1.一种活性炭吸附剂,其特征在于,包括如下质量份的组份:
2.根据权利要求1所述的一种活性炭吸附剂,其特征在于,所述改性活性炭包括如下重量份的组份:椰壳150~200份,木质活性炭150~200份、煤质活性炭150~200份、花生壳150~200份。
3.根据权利要求1所述的一种活性炭吸附剂,其特征在于,所述改性膨润土为酸化纳化改性膨润土。
4.权利要求1~3中任意一项所述活性炭吸附剂的制备方法,其特征在于,包括如下步骤:
改性活性炭制备:将活性炭原料与水混合,研磨成泥状,然后加入到氢氧化钾溶液中浸泡2~3h,过滤后水洗、干燥即得;
改性膨润土制备:将膨润土原料粉磨过300目筛,然后在硫酸溶液中浸泡1~2h,过滤后在氢氧化纳溶液中浸泡2~3h,过滤后水洗、干燥,最后在400~500℃下煅烧4~6h即得;
吸附剂制备:将改性活性炭、改性膨润土、氯化钙、硅藻土和环氧树脂粘结剂混合制粒,烘干后即得。
5.根据权利要求4所述的活性炭吸附剂的制备方法,其特征在于,所述氢氧化钾溶液的浓度为20~30wt%,所述活性炭原料与氢氧化钾溶液的质量体积比为0.24~0.5g/ml。
6.根据权利要求4所述的活性炭吸附剂的制备方法,其特征在于,所述硫酸溶液的浓度为30~50wt%,所述膨润土原料与硫酸溶液的质量体积比为0.56~0.8g/ml。
7.根据权利要求4所述的活性炭吸附剂的制备方法,其特征在于,所述氢氧化纳溶液的浓度为25~50wt%,所述膨润土原料与氢氧化纳溶液的质量体积比为0.46~0.58g/ml。
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