CN105536846A - 一种用于有机污水处理的光降解催化剂及其制备方法 - Google Patents
一种用于有机污水处理的光降解催化剂及其制备方法 Download PDFInfo
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Abstract
本发明公开了一种用于有机污水处理的光降解催化剂及其制备方法,该光降解催化剂是由纳米片状二氧化钛负载在氮化碳纳米片上,具有高效、多次重复使用、无二次污染等优点。本发明的用于有机污水处理的光降解催化剂为二氧化钛/氮化碳复合光降解催化剂,所述的二氧化钛为纳米片状,纳米片状二氧化钛负载在氮化碳纳米片上,所述的复合光降解催化剂粒径为1-10um,其中纳米片状二氧化钛与氮化碳纳米片的质量比为15:1-5:1。
Description
技术领域
本发明涉及一种催化剂及其制备方法,更具体地说涉及一种用于有机污水处理的光降解催化剂及其制备方法。
背景技术
目前全世界地面水体中检出的有机物达到二千多种,其中具有致癌,致畸的达到数百中之多,随着工农业生产的发展,越来越多的有机污染物通过三废排放,大气降雨,对水体环境造成不同程度的污染,引起了一系列社会问题。目前,有机废水的处理技术主要包括:生物处理技术,化学处理技术以及吸附过滤等物理处理技术。近年来发展出了光催化氧化法处理水体中有机污染物的新技术。光催化降解能有效去除有机污染物,并且避免对水体的二次污染。为了提高光催化降解效率,拓宽光谱吸收带,过渡金属及贵金属掺杂半导体氧化物被用于可见光光催化研究,但其成本较高。近年来出现了一种非金属石墨烯状氮化碳半导体光催化剂,由于该催化剂光生电子与正电荷复合能力强,极大的降低了光催化氧化效率,如果将TiO2负载在氮化碳上形成异相结,从而有效提高光生电子与正电荷分离能力。
发明内容
本发明的目的是解决现有技术中存在的问题与不足,提供一种用于有机污水处理的光降解催化剂及其制备方法,该光降解催化剂是由纳米片状二氧化钛负载在氮化碳纳米片上,具有高效、多次重复使用、无二次污染等优点。
本发明是通过以下技术方案实现的:
本发明的用于有机污水处理的光降解催化剂为二氧化钛/氮化碳复合光降解催化剂,所述的二氧化钛为纳米片状,纳米片状二氧化钛负载在氮化碳纳米片上,所述的复合光降解催化剂粒径为1~10um,其中纳米片状二氧化钛与氮化碳纳米片的质量比为15:1~5:1。
本发明上述的光降解催化剂,其进一步的技术方案是所述的二氧化钛为锐钛晶型,二氧化钛纳米片厚度约1~20nm,二氧化钛纳米片边长为5~50nm。
本发明上述的光降解催化剂,其进一步的技术方案还可以是所述的氮化碳纳米片为由1~50单层二维氮化碳堆积,氮化碳纳米片的二维粒径为1~10um。
本发明上述的光降解催化剂的制备方法,其包括以下步骤:
将烷氧基类钛酸酯、氮化碳、催化剂、溶剂混合后置于聚四氟乙烯内衬的水热反应器中,在150~200℃条件下,通过溶剂热反应12~24h,将所得悬浮液经分离后,用水多次清洗,经烘干得到浅黄色粉末即二氧化钛/氮化碳复合光降解催化剂。
本发明上述的光降解催化剂的制备方法,其进一步的技术方案是所述的烷氧基类钛酸酯为钛酸正丁酯或钛酸四异丙酯。
本发明上述的光降解催化剂的制备方法,其进一步的技术方案还可以是所述的催化剂为HF。
本发明上述的光降解催化剂的制备方法,其进一步的技术方案还可以是所述的溶剂为正丁醇或异丙醇。
本发明上述的光降解催化剂的制备方法,其进一步的技术方案还可以是所述的复合光降解催化剂中纳米片状二氧化钛与纳米片状氮化碳的质量比为15:1~5:1。
本发明与现有技术相比具有以下有益效果:
本发明的光降解催化剂是由纳米片状二氧化钛负载在氮化碳纳米片上,具有高效、多次重复使用、无二次污染等优点。本发明的光降解催化剂其二氧化钛/纳米片状氮化碳复合后的荧光效率降低90%以上,二氧化钛/氮化碳复合光降解催化剂分散在有机污水中,通过可见光照射,污水中的有机物可以降解为无机小分子或二氧化碳。二氧化钛/氮化碳复合光降解催化剂的使用浓度为0.1~1mg/L,在催化剂循环使用10次后的催化效率降低率不大于20%。
附图说明
图1为本发明实施例1的二氧化钛纳米片/氮化碳纳米片复合光催化剂的SEM形貌图
图2为本发明实施例1的二氧化钛纳米片/氮化碳纳米片复合光催化剂的TEM形貌图
具体实施方式:
实施例1
100g三聚氰胺在520℃条件下煅烧3h,取出后碾磨成粉末,得到氮化碳粉末。
将8ml钛酸正丁酯,1ml的HF溶液(40wt%)0.2g的氮化碳粉末,150ml异丙醇混合后倒入水热反应器中,在180℃条件下,反应24h,将所得悬浮液经分离后,用水多次清洗,在90℃下烘干得到浅黄色粉末。
将0.2g以上催化剂粉末球磨分散在10mL的水中制备成分散浆料,然后将该浆料按加入1L的溶度为10mg/mL有机污染的水体中(污染物为甲基兰),置于关照强度为0.51W/m2340nm的Q-SUN老化箱体中2h,有机污染物残留量为初始溶度的3.5%。
实施例2
100g三聚氰胺在520℃条件下煅烧3h,取出后碾磨成粉末,得到氮化碳粉末,然后将该粉末在550℃条件下煅烧0.5h。
将8ml钛酸正丁酯,1ml的HF溶液(40wt%)0.1g的氮化碳粉末,150ml异丙醇混合后倒入水热反应器中,在180℃条件下,反应24h,将所得悬浮液经分离后,用水多次清洗,在90℃下烘干得到浅黄色粉末。
将0.2g以上催化剂粉末球磨分散在10mL的水中制备成分散浆料,然后将该浆料按加入1L的溶度为10mg/mL有机污染的水体中(污染物为甲基兰),置于关照强度为0.51W/m2340nm的Q-SUN老化箱体中2h,有机污染物残留量为初始溶度的3.0%。
实施例3
100g三聚氰胺在520℃条件下煅烧3h,取出后碾磨成粉末,得到氮化碳粉末。
将8ml钛酸四异丙酯,1ml的HF溶液(40wt%),0.1g的氮化碳粉末,150ml异丁醇混合后倒入水热反应器中,在180℃条件下,反应24h,将所得悬浮液经分离后,用水多次清洗,在90℃下烘干得到浅黄色粉末。
将0.3g以上催化剂粉末球磨分散在10ml的水中制备成分散浆料,然后将该浆料按加入1L的溶度为20mg/mL有机污染的水体中(污染物为苯酚),置于关照强度为0.51W/m2340nm的Q-SUN老化箱体中2h,有机污染物残留量为初始溶度的3.6%。
实施例4
100g三聚氰胺在520℃条件下煅烧3h,取出后碾磨成粉末,得到氮化碳粉末。
将8ml钛酸正丁酯,2ml的HF溶液(40wt%),0.3g的氮化碳粉末,150ml正丁醇混合后倒入水热反应器中,在200℃条件下,反应24h,将所得悬浮液经分离后,用水多次清洗,在90℃下烘干得到浅黄色粉末。
将0.5g以上催化剂粉末球磨分散在10L的水中制备成分散浆料,然后将该浆料按加入1L的溶度为2mg/mL有机污染的水体中(污染物为硝基苯),置于关照强度为0.51W/m2340nm的Q-SUN老化箱体中2h,有机污染物残留量为初始溶度的5.0%。
Claims (8)
1.一种用于有机污水处理的光降解催化剂,其特征在于该光降解催化剂为二氧化钛/氮化碳复合光降解催化剂,所述的二氧化钛为纳米片状,纳米片状二氧化钛负载在氮化碳纳米片上,所述的复合光降解催化剂粒径为1~10um,其中纳米片状二氧化钛与氮化碳纳米片的质量比为15:1~5:1。
2.根据权利要求1所述的光降解催化剂,其特征在于所述的二氧化钛为锐钛晶型,二氧化钛纳米片厚度约1~20nm,二氧化钛纳米片边长为5~50nm。
3.根据权利要求1所述的光降解催化剂,其特征在于所述的氮化碳纳米片为由1~50单层二维氮化碳堆积,氮化碳纳米片的二维粒径为1~10um。
4.一种如权利要求1-3任一所述的光降解催化剂的制备方法,其特征在于包括以下步骤:
将烷氧基类钛酸酯、氮化碳、催化剂、溶剂混合后置于聚四氟乙烯内衬的水热反应器中,在150~200℃条件下,通过溶剂热反应12~24h,将所得悬浮液经分离后,用水多次清洗,经烘干得到浅黄色粉末即二氧化钛/氮化碳复合光降解催化剂。
5.根据权利要求4所述的光降解催化剂的制备方法,其特征在于所述的烷氧基类钛酸酯为钛酸正丁酯或钛酸四异丙酯。
6.根据权利要求4所述的光降解催化剂的制备方法,其特征在于所述的催化剂为HF。
7.根据权利要求4所述的光降解催化剂的制备方法,其特征在于所述的溶剂为正丁醇或异丙醇。
8.根据权利要求4所述的光降解催化剂的制备方法,其特征在于所述的复合光降解催化剂中纳米片状二氧化钛与纳米片状氮化碳的质量比为15:1~5:1。
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