CN106693990B - Pt-Cu2O包裹Cu纳米线及其制备方法与应用 - Google Patents

Pt-Cu2O包裹Cu纳米线及其制备方法与应用 Download PDF

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CN106693990B
CN106693990B CN201611267289.9A CN201611267289A CN106693990B CN 106693990 B CN106693990 B CN 106693990B CN 201611267289 A CN201611267289 A CN 201611267289A CN 106693990 B CN106693990 B CN 106693990B
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黄新文
凌姝琪
刘宗健
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Zhejiang University of Technology ZJUT
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Abstract

本发明提供了一种Pt‑Cu2O包裹Cu纳米线,其制备方法为:将铜纳米线、去离子水混合,于60~80℃反应5~7h,之后冷却至室温,过滤,洗涤,真空干燥,制得Cu2O为壳Cu为核的纳米线;室温下,将氯铂酸溶液滴加到所述Cu2O为壳Cu为核的纳米线中,滴完后静置25~30s,之后离心,沉淀物洗涤,干燥,得到最终产物;本发明制得的Pt‑Cu2O包裹Cu纳米线可应用于光催化降解染料废水中有机污染物的反应中,光催化效率高。

Description

Pt-Cu2O包裹Cu纳米线及其制备方法与应用
(一)技术领域
本发明涉及一种Pt-Cu2O包裹Cu纳米线及其制备方法与应用。
(二)背景技术
自20世纪70年代以来,光催化技术在染料废水治理方面引起广泛关注,但是传统的光催化剂TiO2能带过窄,对太阳光利用率过低。Cu2O作为一种拥有无毒、具有特殊光学性质等的P型半导体材料,其禁带宽度介于2~2.2eV,与常见催化剂相比,具有可吸收大部分可见光的优势,在光催化和电化学上都有着良好的应用前景。但Cu2O不稳定,且其形成的光生电子 -空穴也存在易复合的缺点,因此对其改性研究已成为研究热点,其中较热门的有异质结、金属掺杂和非金属掺杂。
(三)发明内容
针对目前Cu2O-Cu这种半导体-金属结构较难制备的缺点,本发明提出对Cu纳米线原位氧化制备Cu2O,再在Cu2O@Cu机体上掺杂稀有金属的方法,此方法既简易方便,又能利用半导体-金属结构的Schottky势垒和金属掺杂提高氧化亚铜光催化效率。
本发明采用如下技术方案:
一种Pt-Cu2O包裹Cu纳米线,按如下方法制备得到:
(1)将铜纳米线、去离子水按料液质量比1:1665~1670混合,于60~80℃反应5~7h,之后冷却至室温,过滤,滤饼用无水乙醇和蒸馏水洗涤,真空干燥,制得Cu2O为壳Cu为核的纳米线;
(2)室温下,将10wt%~20wt%氯铂酸溶液滴加到步骤(1)制得的Cu2O为壳Cu为核的纳米线中,滴完后静置25~30s(溶液由浅黄色变成浅蓝色),之后离心,沉淀物用无水乙醇和去离子水洗涤,干燥,得到所述的Pt-Cu2O包裹Cu纳米线;
所述氯铂酸溶液的体积用量以Cu2O为壳Cu为核的纳米线的质量计为6.6~16.7mL/g。
本发明中,所述的室温为20~30℃。
所述的铜纳米线可按如下方法进行制备:
在14~16M的NaOH(99%分析纯)溶液中,依次加入0.1M的Cu(OH)2溶液、乙二胺、35wt%水合肼,混合均匀后于60~90℃反应0.8~1h,之后经离心、洗涤、微孔(孔径0.35~0.45um) 过滤、真空干燥,得到所述的铜纳米线(真空保存备用);
所述的NaOH溶液、Cu(OH)2溶液、乙二胺、水合肼的体积比为100:5~7.5:0.7~0.75: 0.125~0.175。
本发明制得的Pt-Cu2O包裹Cu纳米线粉体材料,利用扫描电镜(SEM)、电子能谱分析 (EDS)对样品进行分析表征。其中,内核铜纳米线为粗细较均匀的密集纳米线结构,直径约为90~110nm,外壳Cu2O颗粒粒径均匀,厚度约为24.5~30.6nm,且表面有Pt颗粒沉积。
本发明制得的Pt-Cu2O包裹Cu纳米线可作为光催化剂应用于光催化降解染料废水中的有机污染物(具体例如典型的偶氮染料甲基橙)的反应中。
本发明的有益效果主要体现在:Pt-Cu2O包裹Cu纳米线光催化材料的制备操作方法简单易行,且其表面的Cu2O颗粒,颗粒粒径均匀且大小仅约30~40nm,比表面积大,且Cu2O为壳Cu为核的纳米线产生的Schottky势垒和金属掺杂产生的Schottky势垒和等离子共振将提高其光催化效率,有良好的实际应用价值。
(四)附图说明
图1a:实施例1中制备的Pt-Cu2O包裹Cu纳米线的SEM图(放大30万倍);
图1b:实施例1中制备的Pt-Cu2O包裹Cu纳米线的SEM图(放大15万倍);
图2:实施例1中制备的Pt-Cu2O包裹Cu纳米线的EDS图谱;
图3:实施例4中Pt-Cu2O包裹Cu纳米线暗吸附甲基橙实验,并用相同质量的Cu2O为壳Cu为核的纳米线做对比,a:Cu2O为壳Cu为核的纳米线,b:Pt-Cu2O包裹Cu纳米线;
图4:实施例4中Pt-Cu2O包裹Cu纳米线光催化降解甲基橙实验,并用相同质量的Cu2O 为壳Cu为核的纳米线做对比,a:Cu2O为壳Cu为核的纳米线,b:Pt-Cu2O包裹Cu纳米线。
(五)具体实施方式
下面结合具体实施例对本发明进行进一步描述,但本发明的保护范围并不仅限于此。
以下实施例中所用到的铜纳米线按如下方法进行制备:
在200mL 15M的NaOH溶液中,依次加入10mL 0.1M的Cu(OH)2溶液、1.5mL乙二胺、0.25mL 35wt%水合肼,混合均匀后于75℃反应1h,之后经离心、无水乙醇和去离子水先后洗涤3次、微孔(孔径0.45um)过滤、真空干燥,得到铜纳米线0.75g。
实施例1
制备Pt-Cu2O包裹Cu纳米线
在圆底烧瓶中分别加入120mg的铜纳米线和200mL的去离子水,70℃水浴反应6h,之后冷却至室温,过滤,滤饼用无水乙醇和蒸馏水进行多次洗涤后,真空干燥制得Cu2O为壳Cu为核的纳米线。制备好的Cu2O为壳Cu为核的纳米线60mg放入小烧杯中,将0.4mL(质量分数为15%)氯铂酸溶液缓慢的滴加到烧杯中,1min滴完后将该混合液静置30s,溶液由之前的浅黄色变成浅蓝色,离心分离出沉淀物,分别用无水乙醇和去离子水清洗几次,干燥后得到Pt掺杂质量分数为2%的Pt-Cu2O包裹Cu纳米线。
利用扫描电镜(SEM)、电子能谱分析(EDS)对所得样品进行分析表征,见图1、图2。
实施例2
制备Pt-Cu2O包裹Cu纳米线
在圆底烧瓶中分别加入120mg的铜纳米线和200mL的去离子水,70℃水浴反应6h,之后冷却至室温,过滤,滤饼用无水乙醇和蒸馏水进行多次洗涤后,真空干燥制得Cu2O为壳Cu为核的纳米线。制备好的Cu2O为壳Cu为核的纳米线60mg放入小烧杯中,将0.8mL(质量分数为15%)氯铂酸溶液缓慢的滴加到烧杯中,1min滴完后将该混合液静置30s,溶液由之前的浅黄色变成浅蓝色,离心分离出沉淀物,分别用无水乙醇和去离子水清洗几次,干燥后得到Pt掺杂质量分数为4%的Pt-Cu2O包裹Cu纳米线。
实施例3
制备Pt-Cu2O包裹Cu纳米线
在圆底烧瓶中分别加入120mg的铜纳米线和200mL的去离子水,70℃水浴反应6h,之后冷却至室温,过滤,滤饼用无水乙醇和蒸馏水进行多次洗涤后,真空干燥制得Cu2O为壳Cu为核的纳米线。制备好的Cu2O为壳Cu为核的纳米线60mg放入小烧杯中,将1mL(质量分数为15%)氯铂酸溶液缓慢的滴加到烧杯中,1min滴完后将该混合液静置30s,溶液由之前的浅黄色变成浅蓝色,离心分离出沉淀物,分别用无水乙醇和去离子水清洗几次,干燥后得到Pt掺杂质量分数为5%的Pt-Cu2O包裹Cu纳米线。
实施例4
性能测试
通过降解甲基橙来评价实施例1中制备的Cu2O为壳Cu为核的纳米线和Pt-Cu2O包裹Cu纳米线的吸附与光催化性能,测试方法如下:
一定浓度(50umol/L)的甲基橙溶液200ml置于玻璃烧杯中,放置于磁力搅拌器上,转速为300r/min,取实施例1制备的Cu2O为壳Cu为核的纳米线和Pt-Cu2O包裹Cu纳米线各60mg依次吸附甲基橙,每隔10min取出少量的混合液离心分离,取其上层清液用分光光度计测其全波长的吸光度,测试完成后混合液再次倒入反应体系中,直到最大吸收峰处的吸光度值不再变化达到吸附平衡。然后在吸附平衡的基础上进行光催化降解实验,该降解以100w的汞灯作为光源,降解反应在密闭的XPA-2(G8)型光催化反应仪里进行。在光催化反应仪中,光源距液面15cm,同时进行电磁搅拌和水冷,并保持反应温度在25℃。整个光催化反应时间为90min,每隔10min取出少量的混合液离心分离,取其上层清液用分光光度计测其全波长的吸光度。
实施例1制备的Cu2O为壳Cu为核的纳米线暗吸附与Pt-Cu2O包裹Cu纳米线暗吸附对比
从图3中可以看出,Pt-Cu2O包裹Cu纳米线暗吸附90分钟以后残留率达14.8%~16.8%,吸附效果良好。且与Cu2O为壳Cu为核的纳米线相比,吸附效率与甲基橙残留率都有明显的提高,最后吸附残留率降低了24.7%~25.7%。
实施例1制备的Cu2O为壳Cu为核的纳米线暗吸附与Pt-Cu2O包裹Cu纳米线暗吸附平衡后光催化对比
从图4中可以看出,Pt-Cu2O包裹Cu纳米线光催化降解90分钟以后残留率达31.2%~33.2%,降解效果良好。且与Cu2O为壳Cu为核的纳米线相比,光催化降解效率与甲基橙残留率都有明显的提高,最后残留率降低了24.9%~26.9%。
根据附图以及综上所述,一般的纳米Cu2O作为催化剂都是以球形、立方体、棒状出现,纳米线形式的很少,且用铜纳米线作为基底直接原位氧化生长的非常少见,且本发明一方面以纳米Cu2O为壳,纳米Cu为核产生金属-半导体界面肖基特垒式,另一方面贵金属Pt沉积在纳米Cu2O表面产生等离子体共振效应,联合这两种效应提升催化性能的也非常少见,由此增强整个催化剂的吸附与光催化效果,结果证明Pt-Cu2O包裹Cu纳米线对甲基橙光催化降解率最高达到67.8%,对甲基橙吸附率最高达到84.1%,证明其对甲基橙染料有良好的吸附与光催化效果。
本说明书实施例所述的内容仅仅是对发明构思的实现形式的列举,本发明的保护范围不应当被视为仅限于实施例所陈述的具体形式,本发明的保护范围也包括本领域技术人员根据本发明构思所能够想到的等同技术手段。

Claims (3)

1.一种Pt-Cu2O包裹Cu纳米线,其特征在于,所述的Pt-Cu2O包裹Cu纳米线按如下方法制备得到:
(1)将铜纳米线、去离子水按料液质量比1:1665~1670混合,于60~80℃反应5~7h,之后冷却至室温,过滤,滤饼用无水乙醇和蒸馏水洗涤,真空干燥,制得Cu2O为壳Cu为核的纳米线;
(2)室温下,将10wt%~20wt%氯铂酸溶液滴加到步骤(1)制得的Cu2O为壳Cu为核的纳米线中,滴完后静置25~30s,之后离心,沉淀物用无水乙醇和去离子水洗涤,干燥,得到所述的Pt-Cu2O包裹Cu纳米线;
所述氯铂酸溶液的体积用量以Cu2O为壳Cu为核的纳米线的质量计为6.6~16.7mL/g。
2.如权利要求1所述的Pt-Cu2O包裹Cu纳米线,其特征在于,所述的铜纳米线按如下方法制备得到:
在14~16M的NaOH溶液中,依次加入0.1M的Cu(OH)2溶液、乙二胺、35wt%水合肼,混合均匀后于60~90℃反应0.8~1h,之后经离心、洗涤、微孔过滤、真空干燥,得到所述的铜纳米线;
所述的NaOH溶液、Cu(OH)2溶液、乙二胺、水合肼的体积比为100:5~7.5:0.7~0.75:0.125~0.175。
3.如权利要求1所述的Pt-Cu2O包裹Cu纳米线在光催化降解染料废水中有机污染物的反应中的应用。
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Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101734614A (zh) * 2009-12-22 2010-06-16 上海大学 金属氧化物纳米线/贵金属纳米晶复合材料的制造方法
CN101797495A (zh) * 2010-03-25 2010-08-11 中国科学技术大学 一种有机染料吸附剂金掺氧化亚铜及其制备方法
CN104162680A (zh) * 2014-07-28 2014-11-26 江苏大学 一种连续合成铜纳米线的方法
CN105126868A (zh) * 2015-08-15 2015-12-09 淮北师范大学 高活性可见光催化剂Ag/Cu2O分级结构微球制备方法
CN106238747A (zh) * 2016-07-12 2016-12-21 中国石油化工股份有限公司 一种多级铜/氧化亚铜纳米线材料的制备方法和基于该材料的葡萄糖传感器电极

Family Cites Families (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
EP3010640A1 (en) * 2013-06-17 2016-04-27 Hindustan Petroleum Corporation Ltd. Nata03 : la203 catalyst with co-catalyst composition for photocatalytic reduction of carbon dioxide

Patent Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101734614A (zh) * 2009-12-22 2010-06-16 上海大学 金属氧化物纳米线/贵金属纳米晶复合材料的制造方法
CN101797495A (zh) * 2010-03-25 2010-08-11 中国科学技术大学 一种有机染料吸附剂金掺氧化亚铜及其制备方法
CN104162680A (zh) * 2014-07-28 2014-11-26 江苏大学 一种连续合成铜纳米线的方法
CN105126868A (zh) * 2015-08-15 2015-12-09 淮北师范大学 高活性可见光催化剂Ag/Cu2O分级结构微球制备方法
CN106238747A (zh) * 2016-07-12 2016-12-21 中国石油化工股份有限公司 一种多级铜/氧化亚铜纳米线材料的制备方法和基于该材料的葡萄糖传感器电极

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