CN110124688A - 一种电触媒材料的合成方法 - Google Patents

一种电触媒材料的合成方法 Download PDF

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CN110124688A
CN110124688A CN201910412171.8A CN201910412171A CN110124688A CN 110124688 A CN110124688 A CN 110124688A CN 201910412171 A CN201910412171 A CN 201910412171A CN 110124688 A CN110124688 A CN 110124688A
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陈希敏
简良荣
陆海涛
杨跃滨
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Xiamen EASO Co Ltd
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    • 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
    • B01J23/89Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of the iron group metals or copper combined with noble metals
    • B01J23/8933Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of the iron group metals or copper combined with noble metals also combined with metals, or metal oxides or hydroxides provided for in groups B01J23/02 - B01J23/36
    • B01J23/8953Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of the iron group metals or copper combined with noble metals also combined with metals, or metal oxides or hydroxides provided for in groups B01J23/02 - B01J23/36 with zinc, cadmium or mercury
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    • C02F1/46109Electrodes
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    • C02F1/46Treatment of water, waste water, or sewage by electrochemical methods
    • C02F1/461Treatment of water, waste water, or sewage by electrochemical methods by electrolysis
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    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
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    • 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
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    • 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
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    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
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Abstract

本发明公开了一种电触媒材料的合成方法,包括以下步骤:步骤1、将锌和铜熔融混合,制得熔融颗粒;步骤2、将二氧化钛、二氧化钌、熔融颗粒和铂粉混合,得到混合材料;将聚偏氟乙烯放入N‑甲基吡咯烷酮溶剂溶解,得到混合溶液;步骤3、将混合材料和混合溶液进行搅浆混合后倒入模具,置于氮气中,在高温炉烧制得到电触媒材料。采用上述方法后,本发明所合成的电触媒材料作为电极时进行电解水时,可以提高超氧离子的释放速率,从而提高杀菌除余氯的效果,并且能保持杀菌除余氯效果的稳定性。

Description

一种电触媒材料的合成方法
技术领域
本发明涉及水处理领域,特别是指一种电触媒材料的合成方法。
背景技术
生活的提高使得人们对健康用水越来越关注,水中的余氯对人们沐浴有很大的会害。自来水中的氯,对任何有毛细孔如皮肤、鼻孔、口腔、肺部、毛发、眼睛等氧化表层有更直接性的危害,因为氯很容易快速被吸收,儿童幼嫩的皮肤、毛发和敏感肌肤对此更为敏感,且由于洗澡时全身的毛孔处于张开状态,则更加加剧氯的吸收数量和吸收量,吸收较多的氯后,容易伤害儿童娇嫩的皮肤,儿童容易因此引起皮炎湿疹等症状。
如何有效地将水中的余氯去除,以及防止水中滋生细菌,避免危害人体健康,一直是人们关注的问题。
发明内容
本发明的目的在于提供一种电触媒材料的合成方法,所生产的电触媒材料作为电极进行电解水时,可以提高超氧离子的释放速率,从而提高杀菌除余氯的效果。
为了达成上述目的,本发明的解决方案是:
一种电触媒材料的合成方法,包括以下步骤:
步骤1、将锌和铜熔融混合,制得熔融颗粒;
步骤2、将二氧化钛、二氧化钌、熔融颗粒和铂粉混合,得到混合材料;将聚偏氟乙烯放入N-甲基吡咯烷酮溶剂溶解,得到混合溶液;
步骤3、将混合材料和混合溶液进行搅浆混合后倒入模具,置于氮气中,在高温炉烧制得到电触媒材料。
所述步骤1中,锌与铜的质量份比值为为60:40。
所述步骤1中,将锌和铜通过焙烧、煅烧或者烧结熔融混合。
所述步骤2的混合材料的体积中,二氧化钛的占比为40-60%,二氧化钌的占比为5-20%,熔融颗粒的占比为20-40%,铂粉的占比为5-15%。
所述步骤3中,混合材料和混合溶液的重量比为1:10。
所述步骤3中,高温炉的烧制温度为500-600℃。
所述步骤2中,铂粉的尺寸为微米或者纳米级。
所述步骤2中,混合溶液中聚偏氟乙烯的浓度为7%。
采用上述方法后,本发明所合成的电触媒材料作为电极时进行电解水时,可以提高超氧离子的释放速率,从而提高杀菌除余氯的效果,并且能保持杀菌除余氯效果的稳定性。
具体实施方式
为了进一步解释本发明的技术方案,下面通过具体实施例来对本发明进行详细阐述。
电触媒处理技术是分别将电触媒材料(如TiO2、IrO2等)与电化学相结合的高级氧化处理程序,现阶段运用于有机污染物降解,具有良好成效,由于其高效率、设备简单、操作方便(可于常温常压下进行)等优点,现已逐步应用于有机污染物废水上。
本发明为一种电触媒材料的合成方法,包括以下步骤:
步骤1、将锌(Zn)和铜(Cu)通过焙烧、煅烧或者烧结熔融混合,制得熔融颗粒,其中锌与铜的质量份比值为为60:40;
步骤2、将二氧化钛(TiO2)、二氧化钌(RuO2)、熔融颗粒和铂粉(Pt)混合,得到混合材料,所述铂粉的尺寸为微米或者纳米级;将聚偏氟乙烯(PVDF)放入N-甲基吡咯烷酮(NMP)溶剂溶解,得到聚偏氟乙烯浓度为7%的混合溶液;上述混合材料的体积中,二氧化钛的占比为40-60%,二氧化钌的占比为5-20%,熔融颗粒的占比为20-40%,铂粉的占比为5-15%;
步骤3、将混合材料和混合溶液按照1:10的重量比进行搅浆混合后倒入模具,置于氮气中,在高温炉500-600℃烧制得到电触媒材料。步骤3中,混合溶液对混合材料的组分起粘合作用。
将所制得的电触媒材料作为电极电解水时,电触媒将水中的分子置换,形成超氧离子,超氧离子穿入细菌内部,从而导致细菌死亡,达到杀菌效果。同时将氯气置换成次氯酸,当次氯酸氧化还原时,即可达到杀菌效果与除余氯效果。
以下通过具体的实施例来解释说明本方法所生产的电触媒的优点。
实施例一、将TiO2、RuO2、Zn/Cu(60/40)熔融颗粒、Pt以60:10:20:10的比例混合,再与7%PVDF混合后,放入10倍重量比的NMP溶剂溶解,进行搅浆混合后倒入2*5公分半圆尺寸的模具中,置于氮气中,在高温炉600℃烧制形成多孔复合材质的电触媒材料。将电触媒材料和碳棒作为电极,通入固定电压进行试验,结果显示当水中余氯0.5mg/L、流动水流速7L/min、滞留水量500毫升的条件下,初期1吨流水量余氯移除率75±3.2%,杀菌力可达77±2.1%,连续水流达5吨余氯移除率皆可以维持85-92%,杀菌力可达83-88%。
实施例二、将TiO2、RuO2、Zn/Cu(60/40)熔融颗粒、Pt以40:10:40:10的比例混合,再与7%PVDF混合后,放入10倍重量比的NMP溶剂溶解,进行搅浆混合后倒入2*5公分半圆尺寸的模具中,置于氮气中,在高温炉600℃烧制形成多孔复合材质的电触媒材料。将电触媒材料和碳棒作为电极,通入固定电压进行试验,结果显示当水中余氯0.5mg/L、流动水流速7L/min、滞留水量500毫升的条件下,初期1吨流水量余氯移除率88±2.1%,杀菌力可达85±1.4%,连续水流达5吨余氯移除率皆可以维持96-99%,杀菌力可达95-99%。
综上,本发明所合成的电触媒材料,其与碳棒一起作为电极时进行电解水时,可以提高超氧离子的释放速率,从而提高杀菌除余氯的效果,并且能保持杀菌除余氯效果的稳定性。
上述实施例并非限定本发明的产品形态和式样,任何所属技术领域的普通技术人员对其所做的适当变化或修饰,皆应视为不脱离本发明的专利范畴。

Claims (8)

1.一种电触媒材料的合成方法,其特征在于包括以下步骤:
步骤1、将锌和铜熔融混合,制得熔融颗粒;
步骤2、将二氧化钛、二氧化钌、熔融颗粒和铂粉混合,得到混合材料;将聚偏氟乙烯放入N-甲基吡咯烷酮溶剂溶解,得到混合溶液;
步骤3、将混合材料和混合溶液进行搅浆混合后倒入模具,置于氮气中,在高温炉烧制得到电触媒材料。
2.如权利要求1所述的一种电触媒材料的合成方法,其特征在于:所述步骤1中,锌与铜的质量份比值为为60:40。
3.如权利要求1所述的一种电触媒材料的合成方法,其特征在于:所述步骤1中,将锌和铜通过焙烧、煅烧或者烧结熔融混合。
4.如权利要求1所述的一种电触媒材料的合成方法,其特征在于:所述步骤2的混合材料的体积中,二氧化钛的占比为40-60%,二氧化钌的占比为5-20%,熔融颗粒的占比为20-40%,铂粉的占比为5-15%。
5.如权利要求1所述的一种电触媒材料的合成方法,其特征在于:所述步骤3中,混合材料和混合溶液的重量比为1:10。
6.如权利要求1所述的一种电触媒材料的合成方法,其特征在于:所述步骤3中,高温炉的烧制温度为500-600℃。
7.如权利要求1所述的一种电触媒材料的合成方法,其特征在于:所述步骤2中,铂粉的尺寸为微米或者纳米级。
8.如权利要求1所述的一种电触媒材料的合成方法,其特征在于:所述步骤2中,混合溶液中聚偏氟乙烯的浓度为7%。
CN201910412171.8A 2019-05-17 2019-05-17 一种用于杀菌除余氯的电触媒材料的合成方法 Expired - Fee Related CN110124688B (zh)

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