CN108620128B - 一种可见光响应的FePc/BiOBr复合光催化剂的制备方法 - Google Patents

一种可见光响应的FePc/BiOBr复合光催化剂的制备方法 Download PDF

Info

Publication number
CN108620128B
CN108620128B CN201810399318.XA CN201810399318A CN108620128B CN 108620128 B CN108620128 B CN 108620128B CN 201810399318 A CN201810399318 A CN 201810399318A CN 108620128 B CN108620128 B CN 108620128B
Authority
CN
China
Prior art keywords
fepc
composite photocatalyst
bismuth acetate
reaction kettle
placing
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Active
Application number
CN201810399318.XA
Other languages
English (en)
Other versions
CN108620128A (zh
Inventor
尤玉静
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Ningbo University of Technology
Original Assignee
Ningbo University of Technology
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Ningbo University of Technology filed Critical Ningbo University of Technology
Priority to CN201810399318.XA priority Critical patent/CN108620128B/zh
Publication of CN108620128A publication Critical patent/CN108620128A/zh
Application granted granted Critical
Publication of CN108620128B publication Critical patent/CN108620128B/zh
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Images

Classifications

    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J31/00Catalysts comprising hydrides, coordination complexes or organic compounds
    • B01J31/16Catalysts comprising hydrides, coordination complexes or organic compounds containing coordination complexes
    • B01J31/18Catalysts comprising hydrides, coordination complexes or organic compounds containing coordination complexes containing nitrogen, phosphorus, arsenic or antimony as complexing atoms, e.g. in pyridine ligands, or in resonance therewith, e.g. in isocyanide ligands C=N-R or as complexed central atoms
    • B01J31/1805Catalysts comprising hydrides, coordination complexes or organic compounds containing coordination complexes containing nitrogen, phosphorus, arsenic or antimony as complexing atoms, e.g. in pyridine ligands, or in resonance therewith, e.g. in isocyanide ligands C=N-R or as complexed central atoms the ligands containing nitrogen
    • B01J31/181Cyclic ligands, including e.g. non-condensed polycyclic ligands, comprising at least one complexing nitrogen atom as ring member, e.g. pyridine
    • B01J31/1825Ligands comprising condensed ring systems, e.g. acridine, carbazole
    • B01J31/183Ligands comprising condensed ring systems, e.g. acridine, carbazole with more than one complexing nitrogen atom, e.g. phenanthroline
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J35/00Catalysts, in general, characterised by their form or physical properties
    • B01J35/30Catalysts, in general, characterised by their form or physical properties characterised by their physical properties
    • B01J35/39Photocatalytic properties
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/30Treatment of water, waste water, or sewage by irradiation
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J2531/00Additional information regarding catalytic systems classified in B01J31/00
    • B01J2531/02Compositional aspects of complexes used, e.g. polynuclearity
    • B01J2531/0213Complexes without C-metal linkages
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J2531/00Additional information regarding catalytic systems classified in B01J31/00
    • B01J2531/02Compositional aspects of complexes used, e.g. polynuclearity
    • B01J2531/0238Complexes comprising multidentate ligands, i.e. more than 2 ionic or coordinative bonds from the central metal to the ligand, the latter having at least two donor atoms, e.g. N, O, S, P
    • B01J2531/0241Rigid ligands, e.g. extended sp2-carbon frameworks or geminal di- or trisubstitution
    • B01J2531/025Ligands with a porphyrin ring system or analogues thereof, e.g. phthalocyanines, corroles
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J2531/00Additional information regarding catalytic systems classified in B01J31/00
    • B01J2531/80Complexes comprising metals of Group VIII as the central metal
    • B01J2531/84Metals of the iron group
    • B01J2531/842Iron
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/30Organic compounds
    • C02F2101/308Dyes; Colorants; Fluorescent agents
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2305/00Use of specific compounds during water treatment
    • C02F2305/10Photocatalysts

Landscapes

  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Engineering & Computer Science (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Materials Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Health & Medical Sciences (AREA)
  • Environmental & Geological Engineering (AREA)
  • Hydrology & Water Resources (AREA)
  • Inorganic Chemistry (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Toxicology (AREA)
  • Catalysts (AREA)

Abstract

本发明涉及到一种可见光响应的FePc/BiOBr复合光催化剂的制备方法,包括下述步骤:(1)称取15~20mmol四甲基溴化铵、0.1~1.0mmol的酞菁铁加入到25~35ml三乙二醇中,在超声波清洗器中300~800W下超声0.5~1.5h得到酞菁铁、四甲基溴化铵混合溶液;(2)称取6~12mmol醋酸铋加入到装有25~35ml三乙二醇的烧杯中,在200~500rpm下搅拌1~3h后得到醋酸铋醇溶液;(3)将两种溶液混合搅拌后用聚四氟乙烯内胆盛放,并放置于不锈钢高压反应釜中于150~190℃下反应2~8h;产物抽滤、洗涤后,置于40~60℃真空干燥箱内真空干燥12~48h,得到FePc/BiOBr复合光催化剂。

Description

一种可见光响应的FePc/BiOBr复合光催化剂的制备方法
技术领域
本发明涉及到光催化剂技术领域,尤其涉及一种对可见光响应的催化剂的制备方法。
背景技术
传统的光催化剂TiO2具有很好的化学稳定性,优良的光催化活性并能氧化空气和水中的污染物,但TiO2的宽能带带隙(3.2e V)只允许它吸收紫外线(<387nm),这意味着太阳光谱中,只有3%-5%的能量是可以利用的。因此限制了它在很多领域中的应用。相较于传统的光催化剂,可见光光催化剂可以对可见光响应,并可以利用太阳光对污染物进行催化降解,节约成本。可见光响应的光催化报道较少
发明内容
本发明所要解决的技术问题是针对现有技术的现状提供一种成本低、稳定性好能够在可见光光源的照射下光催化降解有机染料废水的催化剂的制备方法。
本发明解决上述技术问题所采用的技术方案为:该可见光响应的FePc/BiOBr复合光催化剂的制备方法,其特征在于包括下述步骤:
(1)分别称取15~20mmol四甲基溴化铵、0.1~1.0mmol的酞菁铁加入到25~35ml三乙二醇中,在超声波清洗器中300~800W下超声0.5~1.5h得到酞菁铁、四甲基溴化铵混合溶液;
(2)称取6~12mmol醋酸铋加入到装有25~35ml三乙二醇的烧杯中,在200~500rpm下搅拌1~3h后得到醋酸铋醇溶液;
(3)将步骤(1)所得的混合溶液加入到步骤(2)所得的醋酸铋醇溶液中,200~500rpm下搅拌0.5~1.5h后加入到聚四氟乙烯内胆中,填充体积为60%~80%,将装好反应溶液的内胆放置于不锈钢高压反应釜中,再将密封好的反应釜置于烘箱内150~190℃下反应2~8h;反应后将反应釜取出,室温下静置自然冷却至室温,打开反应釜,用滤纸将内胆中沉淀下来的固体通过抽滤分离出来,所收集的沉淀物用超纯水清洗三次,乙醇清洗一次。最后把洗净的材料置于40~60℃真空干燥箱内真空干燥12~48h,得到FePc/BiOBr复合光催化剂。
上述方案所制备的催化剂使用后的回收方法,其特征在于包括下述步骤:
将使用后的催化剂在600~1000rpm下离心,然后用清水洗涤三次,在20~60℃下真空干燥箱内真空干燥10~15小时后,即得到回收的催化剂。
与现有技术相比,本发明所提供了一种新型FePc/BiOBr复合光催化剂,该催化剂制备方法简单可行,该复合光催化剂在可见光照射下能在短时间内快速降解酸性红B废水,且效率高、稳定性好可重复利用。
附图说明
图1为本发明实施例中FePc/BiOBr复合光催化剂的扫描电镜照片;
图2为本发明实施例FePc/BiOBr催化剂在可见光下降解酸性红B;
图3为本发明实施例中回收的FePc/BiOBr催化剂多次循环利用的光催化性能。
具体实施方式
以下结合附图实施例对本发明作进一步详细描述。
1、制备FePc/BiOBr复合光催化剂:
分别称取16mmol四甲基溴化铵、0.15mmol的酞菁铁加入到盛有30ml三乙二醇的烧杯中,在超声波清洗器中400W下超声1h得到酞菁铁、四甲基溴化铵混合溶液。
称取6.5mmol醋酸铋加入到装有30ml三乙二醇的烧杯中,在400rpm下搅拌1.5h后得到醋酸铋醇溶液。
将酞菁铁、四甲基溴化铵混合溶液加入到醋酸铋醇溶液中400rpm下搅拌1h后,加入到聚四氟乙烯内胆中,填充体积为70%。将装好反应溶液的内胆放置于不锈钢高压反应釜中,再将密封好的反应釜置于烘箱内150℃下反应2h,反应后将反应釜取出,室温下静置自然冷却至室温。
聚四氟乙烯内胆是指用聚四氟乙烯材质制备的容器。
打开反应釜,用滤纸将内胆中沉淀下来的固体通过抽滤分离出来,所收集的沉淀物用超纯水清洗三次。最后把洗净的材料置于40℃真空干燥箱内真空干燥12h,得到0.13g的FePc/BiOBr复合光催化剂。
电镜扫描
将实施例1的FePc/BiOBr复合光催化剂在日立高新扫描电子显微镜SEM SU3500中进行分析测试,其中各参数设置如下:加速电压:20kV,放大倍率:25~200.000,分辨率:3.5nm,真空度:6×l0-6Pa。
图1为FePc/BiOBr复合光催化剂的SEM图。
从图1可以看出:BiOBr以片层结构堆积在一起;FePc为颗粒状,嵌在BiOBr的片层结构之间。
催化活性测试
以酸性红B作为目标降解物,采用120W的LED光源(波长大于400nm)为可见光源,研究合成的FePc/BiOBr复合光催化剂在可见光下的光催化活性。具体实验过程为:
将0.05g的FePc/BiOB粉体加入到盛有150ml浓度为15mg/L的酸性红B溶液的石英反应器中,将反应器在暗室避光搅拌30min以达到吸附-脱附平衡,打开光源,用120W、波长大于400nm的LED光源照射;每隔15min取一次样,离心,取上清液。
采用可见光分光光度计测定酸性红B溶液的吸光度,以酸性红B的脱色率(降解过程中t时刻浓度/初始浓度)表征降解的程度。如图2所示。
由图2可以看出,本实施例制备的催化剂在60min内可以使酸性红B降解率达到97%。
回收催化剂催化活性测试
将催化活性测试实验使用过的催化剂在800rpm离心,用清水洗涤三次,在40℃真空干燥箱内真空干燥12h,重复上述光催化活性实验。
然后对再次使用过的催化剂进行回收,测试其光催化活性。
重复上述实验六次,测试结果如图3所示。
从图3中可以看出回收的催化剂稳定性好,第5次循环使用可以在60min内使酸性红B降解率达到90%。

Claims (1)

1.一种可见光响应的FePc/BiOBr复合光催化剂的制备方法,其特征在于包括下述步骤:
(1)分别称取16mmol四甲基溴化铵、0.15mmol的酞菁铁加入到盛有30ml三乙二醇的烧杯中,在超声波清洗器中400W下超声1h得到酞菁铁、四甲基溴化铵混合溶液;
(2)称取6.5mmol醋酸铋加入到装有30ml三乙二醇的烧杯中,在400rpm下搅拌1.5h后得到醋酸铋醇溶液;
(3)将酞菁铁、四甲基溴化铵混合溶液加入到醋酸铋醇溶液中400rpm下搅拌1h后,加入到聚四氟乙烯内胆中,填充体积为70%;将装好反应溶液的内胆放置于不锈钢高压反应釜中,再将密封好的反应釜置于烘箱内150℃下反应2h,反应后将反应釜取出,室温下静置自然冷却至室温;
(4)打开反应釜,用滤纸将内胆中沉淀下来的固体通过抽滤分离出来,所收集的沉淀物用超纯水清洗三次;最后把洗净的材料置于40℃真空干燥箱内真空干燥12h,得到0.13g的FePc/BiOBr复合光催化剂。
CN201810399318.XA 2018-04-28 2018-04-28 一种可见光响应的FePc/BiOBr复合光催化剂的制备方法 Active CN108620128B (zh)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201810399318.XA CN108620128B (zh) 2018-04-28 2018-04-28 一种可见光响应的FePc/BiOBr复合光催化剂的制备方法

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201810399318.XA CN108620128B (zh) 2018-04-28 2018-04-28 一种可见光响应的FePc/BiOBr复合光催化剂的制备方法

Publications (2)

Publication Number Publication Date
CN108620128A CN108620128A (zh) 2018-10-09
CN108620128B true CN108620128B (zh) 2021-01-29

Family

ID=63695042

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201810399318.XA Active CN108620128B (zh) 2018-04-28 2018-04-28 一种可见光响应的FePc/BiOBr复合光催化剂的制备方法

Country Status (1)

Country Link
CN (1) CN108620128B (zh)

Families Citing this family (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN113198539A (zh) * 2021-03-30 2021-08-03 长安大学 一种双核金属酞菁/碘氧化铋光催化剂的制备方法

Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101664687A (zh) * 2009-09-29 2010-03-10 福州大学 一种染料敏化的卤氧化铋可见光催化剂的制备及其应用
CN101786023A (zh) * 2010-02-12 2010-07-28 湖州师范学院 酞菁敏化钒酸铋纳米粉体的超声化学原位制备方法
CN106925304A (zh) * 2017-04-19 2017-07-07 宁德师范学院 Bi24O31Br10/ZnO复合可见光催化剂及其制备方法
CN106975498A (zh) * 2017-05-08 2017-07-25 昆明理工大学 一种近红外光催化剂BiOCl或BiOBr的制备方法及其应用

Patent Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101664687A (zh) * 2009-09-29 2010-03-10 福州大学 一种染料敏化的卤氧化铋可见光催化剂的制备及其应用
CN101786023A (zh) * 2010-02-12 2010-07-28 湖州师范学院 酞菁敏化钒酸铋纳米粉体的超声化学原位制备方法
CN106925304A (zh) * 2017-04-19 2017-07-07 宁德师范学院 Bi24O31Br10/ZnO复合可见光催化剂及其制备方法
CN106975498A (zh) * 2017-05-08 2017-07-25 昆明理工大学 一种近红外光催化剂BiOCl或BiOBr的制备方法及其应用

Non-Patent Citations (2)

* Cited by examiner, † Cited by third party
Title
"Visible/near-IR-light-driven TNFePc/BiOCl organic–inorganic heterostructures with enhanced photocatalytic activity";Lu Li 等;《Dalton Trans.》;20160504;第45卷;第9497页右栏最后一段,第9498页第2.1节 *
"Water splitting from dye wastewater:A case study of BiOCl/copper(II) phthalocyanine composite photocatalyst";LingZhang等;《Applied Catalysis B:Environmental》;20121210;第132-133卷;第316页第2.1、3.1节 *

Also Published As

Publication number Publication date
CN108620128A (zh) 2018-10-09

Similar Documents

Publication Publication Date Title
CN103657619B (zh) 一种尺寸可控的二氧化钛纳米片光催化材料的制备方法
CN110773213B (zh) 一维硫化镉/二维碳化钛复合光催化剂及其制备方法与应用
CN103480353A (zh) 一种用水热法合成碳量子点溶液制备复合纳米光催化剂的方法
CN105148964B (zh) 一种三维还原氧化石墨烯‑Mn3O4/MnCO3纳米复合材料及其制备方法
CN102274739B (zh) 铜-氮双掺杂二氧化钛光催化材料
CN111111727B (zh) 一种三元磁性复合可见光催化纳米材料及其制备方法与应用
CN111871465B (zh) 一种双配体金属有机骨架光催化剂及其制备方法
CN109967074A (zh) 一种银负载的二氧化钛光催化剂的制备方法与应用
CN103028386A (zh) 具有可见光活性的Ti3+与碳共掺杂TiO2光催化剂及其制备方法
CN108160042A (zh) 利用钴离子掺杂金属有机骨架材料处理抗生素废水的方法
CN106944074A (zh) 一种可见光响应型复合光催化剂及其制备方法和应用
CN106512977A (zh) 活性炭掺杂二氧化钛纳米光催化剂的制备方法及应用
CN106423216B (zh) 一种碳量子点CQDs杂化CdIn2S4复合材料的制备方法及其应用
CN111874988A (zh) 基于多元素共掺杂TiO2纳米光催化材料的有机废水处理方法
CN105170192A (zh) 一种磺化钴酞菁敏化二氧化钛复合光催化剂的制备方法
CN114849785B (zh) 一种三嗪环共价有机框架材料掺杂卟啉钴光催化剂的制备
CN113181974A (zh) 一种氧化铋-氮化碳-卟啉复合光催化剂及其制备方法
CN113401876A (zh) 一种无牺牲剂的光催化产双氧水方法
CN108620128B (zh) 一种可见光响应的FePc/BiOBr复合光催化剂的制备方法
CN106040280B (zh) 全光谱响应型铵钨青铜‑二氧化钛复合光催化剂
CN102658104A (zh) 可见光下具有光催化活性的TiO2催化剂的制备方法
CN108607580B (zh) 硫化铟/钒酸铟复合光催化剂及其制备方法和应用
CN111151278B (zh) 一种碳点复合碳酸氧铋可见光催化剂的制备方法
CN108554427B (zh) 一种In2O3/BiOI半导体复合光催化剂及其制备方法和用途
CN108298632B (zh) 一种纳米TiO2光催化剂降解染料废水的工艺

Legal Events

Date Code Title Description
PB01 Publication
PB01 Publication
SE01 Entry into force of request for substantive examination
SE01 Entry into force of request for substantive examination
GR01 Patent grant
GR01 Patent grant