CN113952961A - 一种新型镍钼合金纳米颗粒的制备方法及其处理废水的方法 - Google Patents

一种新型镍钼合金纳米颗粒的制备方法及其处理废水的方法 Download PDF

Info

Publication number
CN113952961A
CN113952961A CN202111433183.2A CN202111433183A CN113952961A CN 113952961 A CN113952961 A CN 113952961A CN 202111433183 A CN202111433183 A CN 202111433183A CN 113952961 A CN113952961 A CN 113952961A
Authority
CN
China
Prior art keywords
molybdenum alloy
nickel
alloy nanoparticles
preparation
cnt
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
CN202111433183.2A
Other languages
English (en)
Inventor
刘利
诸力维
彭喜林
张楷彬
彭真容
刘晓
孙浩荻
李晓林
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.)
Chongqing Water Group Longxing Drainage Co ltd
Original Assignee
Chongqing Three Gorges Yufu Drainage Co ltd
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 Chongqing Three Gorges Yufu Drainage Co ltd filed Critical Chongqing Three Gorges Yufu Drainage Co ltd
Priority to CN202111433183.2A priority Critical patent/CN113952961A/zh
Publication of CN113952961A publication Critical patent/CN113952961A/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
    • B01J23/00Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00
    • B01J23/70Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of the iron group metals or copper
    • B01J23/76Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of the iron group metals or copper combined with metals, oxides or hydroxides provided for in groups B01J23/02 - B01J23/36
    • B01J23/84Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of the iron group metals or copper combined with metals, oxides or hydroxides provided for in groups B01J23/02 - B01J23/36 with arsenic, antimony, bismuth, vanadium, niobium, tantalum, polonium, chromium, molybdenum, tungsten, manganese, technetium or rhenium
    • B01J23/85Chromium, molybdenum or tungsten
    • B01J23/88Molybdenum
    • B01J23/883Molybdenum and nickel
    • 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
    • B01J35/33Electric or magnetic 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
    • B01J35/00Catalysts, in general, characterised by their form or physical properties
    • B01J35/40Catalysts, in general, characterised by their form or physical properties characterised by dimensions, e.g. grain size
    • 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
    • B01J35/60Catalysts, in general, characterised by their form or physical properties characterised by their surface properties or porosity
    • 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
    • C02F1/46Treatment of water, waste water, or sewage by electrochemical methods
    • C02F1/461Treatment of water, waste water, or sewage by electrochemical methods by electrolysis
    • C02F1/46104Devices therefor; Their operating or servicing
    • C02F1/46109Electrodes
    • 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
    • C02F1/46Treatment of water, waste water, or sewage by electrochemical methods
    • C02F1/461Treatment of water, waste water, or sewage by electrochemical methods by electrolysis
    • C02F1/467Treatment of water, waste water, or sewage by electrochemical methods by electrolysis by electrochemical disinfection; by electrooxydation or by electroreduction
    • C02F1/4672Treatment of water, waste water, or sewage by electrochemical methods by electrolysis by electrochemical disinfection; by electrooxydation or by electroreduction by electrooxydation
    • 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
    • C02F1/46Treatment of water, waste water, or sewage by electrochemical methods
    • C02F1/461Treatment of water, waste water, or sewage by electrochemical methods by electrolysis
    • C02F1/46104Devices therefor; Their operating or servicing
    • C02F1/46109Electrodes
    • C02F2001/46133Electrodes characterised by the material
    • C02F2001/46138Electrodes comprising a substrate and a coating
    • C02F2001/46142Catalytic coating
    • 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
    • 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
    • C02F2101/36Organic compounds containing halogen
    • 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
    • C02F2101/38Organic compounds containing nitrogen
    • 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
    • C02F2101/40Organic compounds containing sulfur
    • 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
    • C02F2305/023Reactive oxygen species, singlet oxygen, OH radical

Landscapes

  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Engineering & Computer Science (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Materials Engineering (AREA)
  • Electrochemistry (AREA)
  • General Chemical & Material Sciences (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Hydrology & Water Resources (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Water Treatment By Electricity Or Magnetism (AREA)
  • Electrolytic Production Of Non-Metals, Compounds, Apparatuses Therefor (AREA)

Abstract

本发明公开了一种新型镍钼合金纳米颗粒的制备方法及其处理废水的方法,包括如下步骤(1)MoNiOx/CNT的制备:(2)MoNi/CNT纳米结构的制备。通过本发明所述方法制备得到的镍钼合金纳米颗粒具有较高的电催化性能,Mo‑Ni合金形成后,Ni与Mo两种元素产生协同作用,有利于降低析氧电位,利于羟基自由基的产生,同时,在高电流密度电解下,Mo存在溶出效应,可以形成多孔结构,使电极的真实表面积增大,进一步提升镍钼合金纳米颗粒的电催化效果。

Description

一种新型镍钼合金纳米颗粒的制备方法及其处理废水的方法
技术领域
本发明涉及污水处理技术领域,具体涉及一种新型镍钼合金纳米颗粒的制备方法及其处理废水的方法。
背景技术
随着现代工业的日益发展,工业用水量及废水的排放量日益增加,世界各国的水体都出现了不同程度的污染,导致世界性的水资源匮乏危机日益严重。为极大地缓解水资源的短缺状况,工业废水处理技术的研究也日益受到人们的密切关注。
目前,已经开发了许多方法来处理废水,包括物理、化学或生物过程。尽管生物处理是一种低成本的技术,但由于废水特性的变化、高化学需氧量 (COD) 浓度和低生物降解性,生物处理系统可能无法持续达到处理要求。而物理和化学方法,例如离子交换、吸附和凝聚,只是将污染物转移到另一相而不是破坏它们。近年来,电化学氧化方法因其高效、易于操作和环境兼容性等优点而备受关注并开始替代传统工艺。
在污染物降解方面,电化学氧化是直接或间接通过在电极表面形成高氧化活性氧(•OH) 来氧化污染物的过程。通常,电化学氧化过程取决于阳极材料。铂、碳 、掺硼金刚石(BDD) 和金属氧化物都可用作阳极材料。其中,二氧化铅(PbO2 )被广泛研究用于污水电化学氧化处理的阳极,但是PbO2 电极不稳定,Pb2+的析出会造成二次污染。因此,电催化处理废水技术推广受到电催化氧化催化剂的限制。
发明内容
针对现有技术存在的上述不足,本发明的目的在于提供一种用于废水电催化氧化裂解的镍钼合金纳米颗粒的制备方法,以解决现有技术通过水电解析氢催化剂成本高、稳定性差和二次污染等问题。
为了解决上述技术问题,本发明采用如下技术方案:
一种用于废水电催化氧化裂解的镍钼合金纳米颗粒的制备方法,包括如下步骤:
(1)MoNiOX/CNT的制备:
将碳管与乙二醇混合后,再加入Mo(CO)6和Ni(OAc)2,在150℃~200℃的条件下搅拌反应2~4h,反应结束后冷却至室温,洗涤多次后得到产物MoNiOX/CNT;其中,碳管、Mo(CO)6和Ni(OAc)2的质量比为1:(5~10):(5~10);
(2)MoNi/CNT纳米结构的制备:
将MoNiOX/CNT平铺在磁舟中,将所述磁舟放入管式炉中加热,待管式炉中空气排出后,在H2/Ar氛围中加热至450℃~550℃并保持反应20min~1h,得到产品MoNi/CNT。
本发明还提供一种利用镍钼合金纳米颗粒电催化氧化裂解处理废水的方法,采用如本发明所述制备方法制备得到所述镍钼合金纳米颗粒,将所述镍钼合金纳米颗粒与乙醇、水和Nafion配置成混合溶液,将所述混合溶液涂在碳电极表面后干燥,重复操作至少四次,以所述碳电极为阳极,碳棒为阴极,在污水中添加硫酸钠作为支持电解质,将阳极和阴极放在电解槽中进行裂解处理。
与现有技术相比,本发明具有如下有益效果:
1、通过本发明所述方法制备得到的镍钼合金纳米颗粒具有较高的电催化性能,Mo-Ni合金形成后,Ni与Mo两种元素产生协同作用,有利于降低析氧电位,从而提高氧化裂解效率,同时,在高电流密度电解下,Mo存在溶出效应,可以形成多孔结构,使电极的真实表面积增大,进一步提升镍钼合金纳米颗粒的催化效果。
2、本发明利用在电极表面形成的高度氧化自由基(·OH)对污水中的有机物进行氧化,高度氧化的自由基能够与有机物发生碰撞,导致共价键断裂并与·OOH 反应,而且,随着降解时间的延长,产生的化合物进一步与·OH碰撞并产生新的中间体,新的中间体最终可以被裂解成水和二氧化碳,从而达到处理和降解水中有机污染物的目的。
附图说明
图1为实施例1的MoNi/CNT纳米材料的XRD图。
图2为生长在CNT上的实施例1的MoNi合金纳米颗粒的TEM图。
图3为电催化裂解的H型电解槽示意图。
具体实施方式
下面将结合附图和实施例对本发明作进一步说明。
一、新型镍钼合金纳米颗粒的制备
(1)MoNiOX/CNT的制备:
将20mg碳管与60ml乙二醇混合,并超声处理1h后使其分散均匀。将其加入100ml圆底烧瓶中,再加入150mg的Mo(CO)6和100mg的Ni(OAc)2,在190℃的条件下,以1500r/min的搅拌速度反应3h,反应结束后冷却至室温,用超纯水洗涤多次后得到产物MoNiOX/CNT。
(2)MoNi/CNT纳米结构的制备:
将30mg的MoNiOX/CNT平铺在磁舟中,将所述磁舟放入管式炉中加热,待管式炉中空气排出后,在H2/Ar氛围中加热至500℃并保持反应30min,得到产品MoNi/CNT。
根据表1的原料配比,采用上述方法制备实施例1~5。
表1
实施例 碳管、Mo(CO)<sub>6</sub>和Ni(OAc)<sub>2</sub>的质量比 反应温度(℃) 产品形貌
1 1:2.5:5 500 纳米颗粒
2 1:5:5 500 纳米颗粒
3 1:5:5 600 纳米颗粒
4 1:5:7.5 500 纳米颗粒
5 1:5:10 500 纳米颗粒
二、一种利用镍钼合金纳米颗粒电催化氧化裂解处理废水的方法
采用实施例1~5和对比例1~2,将1mg镍钼合金纳米颗粒与50μL乙醇、190μL水和10μL的Nafion配置成混合溶液,超声处理至少40min形成均匀的分散体系。然后取25ul催化剂滴到在表面积为0.5cm2的碳纸电极上,所制备的催化剂膜在红外灯下干燥,重复滴四次。以亚甲基蓝有机污水为样本,添加少量Na2SO4作为支持电解质,以制备的电极为阳极,碳棒为阴极,在H型电解槽进行裂解反应。
以0.5 mol/L的亚甲基蓝为例,降解效果如表2所示。
表2
实施例 样品制备配比 样品制备反应温度(℃) 电流密度(mA/cm<sup>-2</sup>) 电解时间(min) 亚甲基蓝去除率(%) 法拉第效率(%)
1 1:2.5:5 500 5 10 35.1 81.0
2 1:5:5 500 10 20 62.9 82.3
3 1:5:5 600 25 30 89.7 85.2
4 1:5:7.5 500 50 60 92.6 75.3
5 1:5:10 500 100 90 98.5 63.9
碳管、Mo(CO)6和Ni(OAc)2的质量比1:5:5,600℃条件下制备的样品,在电流密度为25mA/cm-2时,电解时间为30min,亚甲基蓝的去除率可达到89.7%,法拉第效率可达到85.2%。
三、稳定性测试
对实施例1~5进行稳定性测试,设置电流密度为25mA/cm-2,在20h的长时间裂解下,电流密度基本没有衰减,表明实施例1~5具有很好的稳定性。
最后需要说明的是,以上实施例仅用以说明本发明的技术方案而非限制技术方案,本领域的普通技术人员应当理解,那些对本发明的技术方案进行修改或者等同替换,而不脱离本技术方案的宗旨和范围,均应涵盖在本发明的权利要求范围当中。

Claims (7)

1.一种新型镍钼合金纳米颗粒的制备方法,其特征在于,包括如下步骤:
(1)MoNiOX/CNT的制备:
将碳管与乙二醇混合后,再加入Mo(CO)6和Ni(OAc)2,在150℃~200℃的条件下搅拌反应2~4h,反应结束后冷却至室温,洗涤多次后得到产物MoNiOX/CNT;其中,碳管、Mo(CO)6和Ni(OAc)2的质量比为1:(5~10):(5~10);
(2)MoNi/CNT纳米结构的制备:
将MoNiOX/CNT平铺在磁舟中,将所述磁舟放入管式炉中加热,待管式炉中空气排出后,在H2/Ar氛围中加热至450℃~550℃并保持反应20min~1h,得到产品MoNi/CNT。
2.根据权利要求1所述新型镍钼合金纳米颗粒的制备方法,其特征在于,在(1)中,碳管与乙二醇的质量比为1:(3~5)。
3.根据权利要求1所述新型镍钼合金纳米颗粒的制备方法,其特征在于,在(1)中,对混合后的碳管和乙二醇进行超声处理,使其分散均匀。
4.根据权利要求1所述新型镍钼合金纳米颗粒的制备方法,其特征在于,在(2)中,H2和Ar之间的体积比为1:10。
5.一种利用镍钼合金纳米颗粒电催化氧化裂解处理废水的方法,其特征在于,采用如权利要求1~4任一所述制备方法制备得到所述镍钼合金纳米颗粒,将所述镍钼合金纳米颗粒与乙醇、水和Nafion配置成混合溶液,将所述混合溶液涂在碳电极表面后干燥,重复操作至少四次,以所述碳电极为阳极,碳棒为阴极,在污水中添加硫酸钠作为支持电解质,将阳极和阴极放在电解槽中进行裂解处理。
6.根据权利要求5所述利用镍钼合金纳米颗粒电催化氧化裂解处理废水的方法,其特征在于,所述混合溶液中,镍钼合金纳米颗粒的用量为2~5mg/mL。
7.根据权利要求5所述利用镍钼合金纳米颗粒电催化氧化裂解处理废水的方法,其特征在于,所述混合溶液中,水、乙醇和Nafion的体积比为5:19:1。
CN202111433183.2A 2021-11-29 2021-11-29 一种新型镍钼合金纳米颗粒的制备方法及其处理废水的方法 Pending CN113952961A (zh)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN202111433183.2A CN113952961A (zh) 2021-11-29 2021-11-29 一种新型镍钼合金纳米颗粒的制备方法及其处理废水的方法

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN202111433183.2A CN113952961A (zh) 2021-11-29 2021-11-29 一种新型镍钼合金纳米颗粒的制备方法及其处理废水的方法

Publications (1)

Publication Number Publication Date
CN113952961A true CN113952961A (zh) 2022-01-21

Family

ID=79472427

Family Applications (1)

Application Number Title Priority Date Filing Date
CN202111433183.2A Pending CN113952961A (zh) 2021-11-29 2021-11-29 一种新型镍钼合金纳米颗粒的制备方法及其处理废水的方法

Country Status (1)

Country Link
CN (1) CN113952961A (zh)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN114318393A (zh) * 2022-01-30 2022-04-12 中国华能集团清洁能源技术研究院有限公司 一种多孔镍钼钴析氢电极及其制备方法和应用

Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1850641A (zh) * 2006-05-26 2006-10-25 上海大学 碳纳米管/二氧化锡复合电催化电极的制备方法
CN101752569A (zh) * 2010-01-11 2010-06-23 华南师范大学 碳化镍钼在制备微生物燃料电池阳极中的应用
CN109351359A (zh) * 2018-10-18 2019-02-19 吉林师范大学 一种以碳纳米管为原料合成多金属碳化物的制备方法

Patent Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1850641A (zh) * 2006-05-26 2006-10-25 上海大学 碳纳米管/二氧化锡复合电催化电极的制备方法
CN101752569A (zh) * 2010-01-11 2010-06-23 华南师范大学 碳化镍钼在制备微生物燃料电池阳极中的应用
CN109351359A (zh) * 2018-10-18 2019-02-19 吉林师范大学 一种以碳纳米管为原料合成多金属碳化物的制备方法

Non-Patent Citations (1)

* Cited by examiner, † Cited by third party
Title
I. ESWARAMOORTHI等: "Application of multi-walled carbon nanotubes as efficient support to NiMo hydrotreating catalyst", 《APPLIED CATALYSIS A: GENERAL》, vol. 339, 31 January 2008 (2008-01-31), pages 187 - 195, XP022560379 *

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN114318393A (zh) * 2022-01-30 2022-04-12 中国华能集团清洁能源技术研究院有限公司 一种多孔镍钼钴析氢电极及其制备方法和应用
CN114318393B (zh) * 2022-01-30 2023-03-24 中国华能集团清洁能源技术研究院有限公司 一种多孔镍钼钴析氢电极及其制备方法和应用

Similar Documents

Publication Publication Date Title
CN111285446B (zh) 一种Pd/NiCo2O4/Ni foam复合电极及其制备方法和应用
CN110272100B (zh) Ti4O7涂层的陶瓷微滤膜电极的制备方法
CN112408554B (zh) 一种漂浮式双氧源气体扩散电极装置及应用
CN113023835B (zh) 一种基于污泥基生物质炭的电芬顿阴极材料的制备方法及其产品和应用
CN113511763B (zh) 利用TiO2-NTs/Sb-SnO2/PbO2电催化氧化去除水中氨氮的方法及应用
CN113353932A (zh) 火龙果皮制备的分级孔生物炭电催化剂及制备方法和应用
CN113952961A (zh) 一种新型镍钼合金纳米颗粒的制备方法及其处理废水的方法
Zhang et al. Preparation of a ruthenium-modified composite electrode and evaluation of the degradation process and degradation mechanism of doxycycline at this electrode
CN113060803A (zh) 一种电催化处理再生水中痕量雌激素的系统及方法
CN112225382A (zh) 一种废水中药品和个人护理品的去除方法
CN114540873B (zh) 一种钯/γ-二氧化锰/泡沫镍复合电极及其制备方法和应用
CN108529720B (zh) 一种颗粒电极及其制备方法和应用
WO2023098252A1 (zh) 一种光电微生物耦合脱氮除碳系统
CN114671495B (zh) 一种高活性稳定阳极材料的制备方法及应用
CN113998760B (zh) 用于非均相电芬顿体系的铜钴氧化物/碳纳米管/泡沫镍复合电极及应用
CN113233549A (zh) 一种纳米二氧化铅电极及其制备方法和应用
Chen et al. Critical role of Photo-electrode with Ce-g-C3N4 in multi-stage microbial fuel cells cascade reactor treating diluted hyper-saline industrial wastewater rich in amines
CN111939895B (zh) 一种不同形貌氧化铋负载二氧化铅催化剂及其制备方法和应用
Chen et al. Electro-peroxone degradation of metamitron using a gas diffusion cathode with ZIF-derived heteroatom-doped porous carbon as the catalytic layer
CN113461110B (zh) 一种基于非自由基氧化的反应性电催化膜及其制备方法和应用
CN114804454B (zh) 一种电芬顿式的污水处理工艺
WO2024119637A1 (zh) 一种用于废水处理的阴阳两极协同电催化系统与应用
CN110357224B (zh) 一种高浓度自由基电极的制备方法及应用
CN114715982B (zh) 一种电化学活化过氧单硫酸盐处理抗生素废水的方法
CN113422074B (zh) 一种电化学系统碳基电极材料的预处理方法

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
TA01 Transfer of patent application right

Effective date of registration: 20240524

Address after: 401133 No. 69 Shenghua Road, Fusheng Town, Jiangbei District, Chongqing (self committed)

Applicant after: Chongqing Water Group Longxing Drainage Co.,Ltd.

Country or region after: China

Address before: 400000 Chongqing Liangjiang New Area Yuzui Wujiashan orchard sewage treatment plant

Applicant before: Chongqing Three Gorges Yufu drainage Co.,Ltd.

Country or region before: China