CN113368883A - 一种0D/3D Fe2O3 QDs/g-C3N4杂化光芬顿催化剂的制备方法 - Google Patents

一种0D/3D Fe2O3 QDs/g-C3N4杂化光芬顿催化剂的制备方法 Download PDF

Info

Publication number
CN113368883A
CN113368883A CN202110639279.8A CN202110639279A CN113368883A CN 113368883 A CN113368883 A CN 113368883A CN 202110639279 A CN202110639279 A CN 202110639279A CN 113368883 A CN113368883 A CN 113368883A
Authority
CN
China
Prior art keywords
qds
fenton catalyst
photo
preparation
catalyst
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.)
Pending
Application number
CN202110639279.8A
Other languages
English (en)
Inventor
刘冬
倪天军
张丰泉
李春灵
赵茜
高霞
杨中智
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.)
Xinxiang Medical University
Original Assignee
Xinxiang Medical University
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 Xinxiang Medical University filed Critical Xinxiang Medical University
Priority to CN202110639279.8A priority Critical patent/CN113368883A/zh
Publication of CN113368883A publication Critical patent/CN113368883A/zh
Pending legal-status Critical Current

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
    • B01J27/00Catalysts comprising the elements or compounds of halogens, sulfur, selenium, tellurium, phosphorus or nitrogen; Catalysts comprising carbon compounds
    • B01J27/24Nitrogen compounds
    • 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
    • B01J35/20Catalysts, in general, characterised by their form or physical properties characterised by their non-solid state
    • B01J35/23Catalysts, in general, characterised by their form or physical properties characterised by their non-solid state in a colloidal state
    • 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
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J37/00Processes, in general, for preparing catalysts; Processes, in general, for activation of catalysts
    • B01J37/02Impregnation, coating or precipitation
    • B01J37/03Precipitation; Co-precipitation
    • B01J37/031Precipitation
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J37/00Processes, in general, for preparing catalysts; Processes, in general, for activation of catalysts
    • B01J37/08Heat treatment
    • B01J37/082Decomposition and pyrolysis
    • 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
    • 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
    • C02F1/72Treatment of water, waste water, or sewage by oxidation
    • C02F1/722Oxidation by peroxides
    • 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
    • C02F1/72Treatment of water, waste water, or sewage by oxidation
    • C02F1/725Treatment of water, waste water, or sewage by oxidation by catalytic oxidation
    • 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
    • C02F2305/02Specific form of oxidant
    • C02F2305/026Fenton's reagent
    • 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)
  • Engineering & Computer Science (AREA)
  • Organic Chemistry (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Materials Engineering (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Hydrology & Water Resources (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Thermal Sciences (AREA)
  • Physics & Mathematics (AREA)
  • Health & Medical Sciences (AREA)
  • Toxicology (AREA)
  • Catalysts (AREA)

Abstract

本发明公开了一种0D/3D Fe2O3 QDs/g‑C3N4杂化光芬顿催化剂的制备方法,该方法以三聚氰胺和三聚氰酸为原料,采用一步煅烧法制备三维多孔结构的g‑C3N4;通过合适比例的三维g‑C3N4、FeCl3·6H2O和NH4HCO3混合,经简单的自组装合成Fe2O3 QDs/g‑C3N4光芬顿催化剂。该催化剂具有良好的可见光响应、优异的有害污染物降解力和重复利用稳定性,较经典光芬顿催化剂具有更宽的工作范围;该制备方法工艺简单、原料成本低、易于大规模生产。

Description

一种0D/3D Fe2O3 QDs/g-C3N4杂化光芬顿催化剂的制备方法
技术领域
本发明属于降解环境污染物的光芬顿催化剂的制备技术领域,具体涉及一种0D/3D Fe2O3 QDs/g-C3N4杂化光芬顿催化剂的制备方法。
背景技术
铁基催化剂因其毒性小、成本低、富集度高而被广泛应用于非均相芬顿中,但其催化活性通常较低,Fe3+-Fe2+之间的转化较慢,高酸条件下铁浸出,造成催化剂流失,因此,研究人员在增强Fe2+基催化剂的芬顿反应方面做了诸多努力,其中将半导体材料引入Fe2+基催化剂来增强其催化活性。
半导体材料的引入促进了Fe3+-Fe2+转化,提高了降解效率,其中Fe2O3被认为是最有前途的候选材料。但因半导体电荷迁移缓慢、中心缺乏高活性位点等特性,结果并不令人满意。常规Fe2O3纳米粒子因团聚作用,其表面活性位点数量减少,因此,开发具有丰富活性中心位点的高效Fe2O3催化剂具有重要意义。
0D量子点(quantum dots,QDs)的短程有序、大表面积和大量结构缺陷,可以提供大量的活性位点。近来,研究人员采用在2D纳米材料g-C3N4表面负载0D量子点的方法,有效的减少了量子点的自聚现象。但2D材料较薄和较细尺寸,都增加了将其从催化剂悬浮液中分离的难度。理论上,采用在三维纳米材料表面负载量子点的方式,不仅抑制了2D结构层的积累,也促进有机物的吸附和固液分离。
发明内容
本发明解决的技术问题是提供了一种具有良好的可见光响应的0D/3D Fe2O3 QDs/g-C3N4杂化光芬顿催化剂的制备方法,该方法采用一步煅烧法制备具有三维多孔结构的g-C3N4,通过合适比例的三维g-C3N4、FeCl3·6H2O和NH4HCO3混合,经简单的自组装合成Fe2O3QDs/g-C3N4光芬顿催化剂;在可见光下,通过添加H2O2降解有机污染物来评价催化剂的催化性能。该光芬顿催化剂具有良好的可见光响应、优异的有害污染物降解力和重复利用稳定性,较经典光芬顿催化剂具有更宽的光谱工作范围。
本发明为解决上述技术问题采用如下技术方案,一种0D/3D Fe2O3 QDs/g-C3N4杂化光芬顿催化剂的制备方法,其特征在于具体步骤为:
步骤S1:3D多孔g-C3N4的制备
配制三聚氰胺和三聚氰酸混合水溶液,搅拌使其分散均匀后,再转移至培养皿中于60℃进行干燥得到前体物;将干燥后的前驱物研磨,于550℃退火处理2-4h即得到微黄色的3D多孔g-C3N4样品;
步骤S2:0D/3D Fe2O3 QDs/g-C3N4杂化光芬顿催化剂的制备
将步骤S1得到的3D多孔g-C3N4样品分散于乙醇中,磁力搅拌以实现均匀分散得到g-C3N4乙醇分散液,再向上述分散液中添加FeCl3·6H2O和NH4HCO3并搅拌混合均匀,将产物离心、洗涤,并于60℃干燥过夜;然后于350℃退火处理2-4h即得到0D/3D Fe2O3 QDs/ g-C3N4光芬顿催化剂。
进一步限定,步骤S1中所述三聚氰胺与三聚氰酸的投料质量比为1:1,三聚氰胺和三聚氰酸混合水溶液中三聚氰胺和三聚氰酸质量分数均为2%。
进一步限定,步骤S2中所述g-C3N4乙醇分散液中g-C3N4的质量分数为0.9%-2%,FeCl3·6H2O和NH4HCO3与中g-C3N4对应的质量比分别为13.5%-30%和12%-26.5%。
本发明与现有技术相比具有以下有益效果:
1、本发明制得的0D/3D Fe2O3 QDs/g-C3N4杂化光芬顿催化剂具有良好的可见光响应、优异的有害污染物降解力和重复利用稳定性,较经典光芬顿催化剂具有更宽的光谱工作范围,可广泛应用于常见有机污染物的降解;
2、本发明制备0D/3D Fe2O3 QDs/g-C3N4杂化光芬顿催化剂的方法原料成本低廉、制备工艺简单且易于大规模生产;
3、本发明制备的0D/3D Fe2O3 QDs/g-C3N4杂化光芬顿催化剂为一种0D/3D杂化纳米材料,在三维多孔g-C3N4上负载Fe2O3量子点,Fe2O3 QDs为光芬顿反应提供活性位点,三维多孔g-C3N4具有较大的比表面积,具有良好的可见光响应和污染物降解能力。
附图说明
图1是本发明的制备工艺流程图;
图2是本发明制备的0D/3D Fe2O3 QDs/g-C3N4杂化光芬顿催化剂的紫外-可见漫反射吸收光谱图;
图3是本发明制备的0D/3D Fe2O3 QDs/g-C3N4杂化光芬顿催化剂的场发射电子扫描显微镜图;
图4是本发明制备的0D/3D Fe2O3 QDs/g-C3N4杂化光芬顿催化剂的透射电子显微镜图;
图5是本发明制备的0D/3D杂化的Fe2O3 QDs/g-C3N4光芬顿催化剂的罗丹明B(RhB)的去除效果图。
具体实施方式
以下通过实施例对本发明的上述内容做进一步详细说明,但不应该将此理解为本发明上述主题的范围仅限于以下的实施例,凡基于本发明上述内容实现的技术均属于本发明的范围。
实施例1
首先,取2.0g三聚氰胺和2.0g三聚氰酸溶于100mL超纯水中,搅拌12h;然后将上述溶液转移至玻璃皿中,于60℃干燥12h;将所得前体物研磨,于550℃退火处理4h,即得到微黄色的3D多孔g-C3N4样品。取0.9g上述3D多孔g-C3N4样品分散于100mL乙醇中,磁力搅拌2h以实现均匀分散得到g-C3N4乙醇分散液,向上述分散液中添加0.27g FeCl3·6H2O和0.24gNH4HCO3并搅拌12h,将产物离心、洗涤,并于60℃干燥过夜;于350℃退火处理2h,即得到Fe2O3 QDs/g-C3N4光芬顿催化剂。
实施例2
首先,取2.0g三聚氰胺和2.0g三聚氰酸溶于100mL超纯水中,搅拌12h;然后将上述溶液转移至玻璃皿中,于60℃干燥12h;将所得前体物研磨,于550℃退火处理4h,即得到微黄色的3D多孔g-C3N4样品。取1.5g上述3D多孔g-C3N4样品分散于100mL乙醇中,磁力搅拌2h以实现均匀分散得到g-C3N4乙醇分散液,向上述分散液中添加0.27g FeCl3·6H2O和0.24gNH4HCO3并搅拌12h,将产物离心、洗涤,并于60℃干燥过夜;于350℃退火处理2h,即得到Fe2O3 QDs/g-C3N4光芬顿催化剂。
实施例3
取80mL浓度为20mg/L RhB溶液,再加入实施例2中制备的Fe2O3 QDs/g-C3N4光芬顿催化剂,经暗光搅拌10min,取样过滤分析,然后加入1.5mL的双氧水(H2O2,30wt%),开启光源、开始计时,分别在20min,40min,60min,80min时间点取样过滤分析,在可见光下反应60min后,溶液中RhB的去除率大于99%,效果详见图5。
以上实施例描述了本发明的基本原理、主要特征及优点,本行业的技术人员应该了解,本发明不受上述实施例的限制,上述实施例和说明书中描述的只是说明本发明的原理,在不脱离本发明原理的范围下,本发明还会有各种变化和改进,这些变化和改进均落入本发明保护的范围内。

Claims (3)

1.一种0D/3D Fe2O3 QDs/g-C3N4杂化光芬顿催化剂的制备方法,其特征在于具体步骤为:
步骤S1:3D多孔g-C3N4的制备
配制三聚氰胺和三聚氰酸混合水溶液,搅拌使其分散均匀后,再转移至培养皿中于60℃进行干燥得到前体物;将干燥后的前驱物研磨,于550℃退火处理2-4h即得到微黄色的3D多孔g-C3N4样品;
步骤S2:0D/3D Fe2O3 QDs/g-C3N4杂化光芬顿催化剂的制备
将步骤S1得到的3D多孔g-C3N4样品分散于乙醇中,磁力搅拌以实现均匀分散得到g-C3N4乙醇分散液,再向上述分散液中添加FeCl3·6H2O和NH4HCO3并搅拌混合均匀,将产物离心、洗涤,并于60℃干燥过夜;然后于350℃退火处理2-4h即得到0D/3D Fe2O3 QDs/ g-C3N4光芬顿催化剂。
2. 根据权利要求1所述的0D/3D Fe2O3 QDs/g-C3N4杂化光芬顿催化剂的制备方法,其特征在于:步骤S1中所述三聚氰胺与三聚氰酸的投料质量比为1:1,三聚氰胺和三聚氰酸混合水溶液中三聚氰胺和三聚氰酸质量分数均为2%。
3.根据权利要求1所述的0D/3D Fe2O3 QDs/g-C3N4杂化光芬顿催化剂的制备方法,其特征在于:步骤S2中所述g-C3N4乙醇分散液中g-C3N4的质量分数为0.9%-2%,FeCl3·6H2O和NH4HCO3与中g-C3N4对应的质量比分别为13.5%-30%和12%-26.5%。
CN202110639279.8A 2021-06-08 2021-06-08 一种0D/3D Fe2O3 QDs/g-C3N4杂化光芬顿催化剂的制备方法 Pending CN113368883A (zh)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN202110639279.8A CN113368883A (zh) 2021-06-08 2021-06-08 一种0D/3D Fe2O3 QDs/g-C3N4杂化光芬顿催化剂的制备方法

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN202110639279.8A CN113368883A (zh) 2021-06-08 2021-06-08 一种0D/3D Fe2O3 QDs/g-C3N4杂化光芬顿催化剂的制备方法

Publications (1)

Publication Number Publication Date
CN113368883A true CN113368883A (zh) 2021-09-10

Family

ID=77572894

Family Applications (1)

Application Number Title Priority Date Filing Date
CN202110639279.8A Pending CN113368883A (zh) 2021-06-08 2021-06-08 一种0D/3D Fe2O3 QDs/g-C3N4杂化光芬顿催化剂的制备方法

Country Status (1)

Country Link
CN (1) CN113368883A (zh)

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN113751046A (zh) * 2021-10-09 2021-12-07 东华大学 一种铁掺杂树脂修饰石墨相氮化碳光芬顿催化剂及制备方法
CN114100663A (zh) * 2021-12-01 2022-03-01 化学与精细化工广东省实验室 具有多通道电荷转移的半导体基芬顿催化剂及其制备方法和应用
CN114522709A (zh) * 2022-01-14 2022-05-24 广东工业大学 一种三维多孔石墨相氮化碳/碘氧化铋/银纳米粒子复合光催化剂及其制备方法和应用

Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN106345505A (zh) * 2016-07-29 2017-01-25 中国石油大学(华东) 一种多孔异质结构的复合光催化剂及其制备方法
CN108493461A (zh) * 2018-05-08 2018-09-04 大连理工大学 一种N掺杂多孔碳包覆Fe、Co双金属纳米粒子的催化剂及其制备方法
CN111659440A (zh) * 2020-06-11 2020-09-15 江南大学 一种光-芬顿催化剂及其制备方法和在水处理中的应用
US20200378018A1 (en) * 2020-04-16 2020-12-03 Chinese Research Academy Of Environmental Sciences Carbon dots-based photocatalytic electrode for simultaneous organic matter degradation and heavy metal reduction and use thereof
CN112619682A (zh) * 2020-12-30 2021-04-09 汕头大学 一种双金属氧化物量子点和氮化碳纳米片的复合材料和制备方法及其应用

Patent Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN106345505A (zh) * 2016-07-29 2017-01-25 中国石油大学(华东) 一种多孔异质结构的复合光催化剂及其制备方法
CN108493461A (zh) * 2018-05-08 2018-09-04 大连理工大学 一种N掺杂多孔碳包覆Fe、Co双金属纳米粒子的催化剂及其制备方法
US20200378018A1 (en) * 2020-04-16 2020-12-03 Chinese Research Academy Of Environmental Sciences Carbon dots-based photocatalytic electrode for simultaneous organic matter degradation and heavy metal reduction and use thereof
CN111659440A (zh) * 2020-06-11 2020-09-15 江南大学 一种光-芬顿催化剂及其制备方法和在水处理中的应用
CN112619682A (zh) * 2020-12-30 2021-04-09 汕头大学 一种双金属氧化物量子点和氮化碳纳米片的复合材料和制备方法及其应用

Non-Patent Citations (1)

* Cited by examiner, † Cited by third party
Title
席清华等: "Fe2O3/g-C3N4 光催化降解罗丹明B 性能研究" *

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN113751046A (zh) * 2021-10-09 2021-12-07 东华大学 一种铁掺杂树脂修饰石墨相氮化碳光芬顿催化剂及制备方法
CN114100663A (zh) * 2021-12-01 2022-03-01 化学与精细化工广东省实验室 具有多通道电荷转移的半导体基芬顿催化剂及其制备方法和应用
CN114522709A (zh) * 2022-01-14 2022-05-24 广东工业大学 一种三维多孔石墨相氮化碳/碘氧化铋/银纳米粒子复合光催化剂及其制备方法和应用
CN114522709B (zh) * 2022-01-14 2023-10-31 广东工业大学 一种三维多孔石墨相氮化碳/碘氧化铋/银纳米粒子复合光催化剂及其制备方法和应用

Similar Documents

Publication Publication Date Title
CN113368883A (zh) 一种0D/3D Fe2O3 QDs/g-C3N4杂化光芬顿催化剂的制备方法
CN110152711B (zh) 一种CeO2@MoS2/g-C3N4三元复合光催化剂及其制备方法
CN108097261B (zh) 一种高效稳定的铁锰复合氧化物催化剂及其制备方法与应用
CN111905766B (zh) 一种0D/1D W18O49/CdS Z-型可见光催化剂的制备方法及应用
CN108355669B (zh) 一种磁性纳米洋葱碳负载Bi2WO6的光催化剂及其制备方法和应用
CN105709793A (zh) 硫化镉纳米粒子修饰的五氧化二铌纳米棒/氮掺杂石墨烯复合光催化剂、制备方法与应用
CN110624595A (zh) 一种钙铟硫/碳化钛光催化复合材料及其制备方法
CN114768841B (zh) 过渡金属磷化物修饰的氧掺杂ZnIn2S4极化光催化材料及其制备方法和用途
CN113976148B (zh) 一种Z型C60/Bi/BiOBr复合光催化剂及其制备方法和应用
CN107497455A (zh) 一种微量硫表面修饰的超薄钨酸铋纳米片光催化剂的制备方法及其应用
CN111715211B (zh) 一种活性炭负载TiO2/Bi2WO6异质结复合材料的制备方法
CN117582977A (zh) 一种用于降解四环素的LCQDs/Bi2MoO6球花状复合光催化剂的制备方法与应用
CN109876783B (zh) 利用铁尾矿制备纳米气泡状硅酸锰复合材料的方法
CN114870899B (zh) 一种光催化co2分解制合成气的复合光催化剂及其制备方法
CN115155592B (zh) 一种高效活化过硫酸盐的钴酸铁/煤矸石催化剂的制备方法及应用
CN114950530B (zh) 具有类过氧化物酶活性的氮掺杂蛋壳纳米酶的制备方法
CN114849789B (zh) Mil-125负载1t相硫化钼复合光催化剂的制备方法及其应用
CN114192143B (zh) 一种钨酸银/偏钒酸银复合光催化剂的制备及其应用
CN112569955B (zh) 一种降解有机染料废水的CeO2/BiFeO3纳米纤维光催化剂及制备方法
CN108295903A (zh) 一种用于制氢的硫化镉量子点-酞箐铜光催化剂及制备方法
CN111298844B (zh) 一种BiOBr/Fe3O4@UiO-66三元复合光催化材料
CN113926470A (zh) 一种富含氧空位WO3/BiOBr纳米花光催化剂及其制备方法和应用
CN112337473A (zh) 一种可见光响应降解有机物的CuO/Bi2MoO6异质结光催化材料的制备方法及应用
CN112844415A (zh) 一种生态环境修复剂
CN111974421B (zh) 一种高效界面电荷转移的金属/半导体异质结复合材料的制备方法

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
WD01 Invention patent application deemed withdrawn after publication
WD01 Invention patent application deemed withdrawn after publication

Application publication date: 20210910