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CN118811776A - A continuous preparation method of high-purity hydrogen peroxide - Google Patents

A continuous preparation method of high-purity hydrogen peroxide Download PDF

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CN118811776A
CN118811776A CN202411310947.2A CN202411310947A CN118811776A CN 118811776 A CN118811776 A CN 118811776A CN 202411310947 A CN202411310947 A CN 202411310947A CN 118811776 A CN118811776 A CN 118811776A
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hydrogen peroxide
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CN118811776B (en
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常青
李通
周树鹏
齐国庆
董庆蕊
常鹏举
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Shandong Xinlong Technology Co ltd
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    • C01BNON-METALLIC ELEMENTS; COMPOUNDS THEREOF; METALLOIDS OR COMPOUNDS THEREOF NOT COVERED BY SUBCLASS C01C
    • C01B15/00Peroxides; Peroxyhydrates; Peroxyacids or salts thereof; Superoxides; Ozonides
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Abstract

本发明提供一种高纯双氧水的连续制备方法,属于高纯双氧水领域。所述高纯双氧水的连续制备方法,由以下步骤组成:一级连续吸附、二级连续吸附、树脂连续吸附。本发明的高纯双氧水的连续制备方法,能够在实现高纯双氧水的连续化生产前提下,提高对工业级双氧水中杂质的处理效果,避免工业级双氧水中杂质对处理稳定性的影响,并有效提高各处理工段相互间的匹配性能,能够对工业级双氧水进行高效、稳定的连续纯化精制。The present invention provides a continuous preparation method of high-purity hydrogen peroxide, belonging to the field of high-purity hydrogen peroxide. The continuous preparation method of high-purity hydrogen peroxide consists of the following steps: primary continuous adsorption, secondary continuous adsorption, and resin continuous adsorption. The continuous preparation method of high-purity hydrogen peroxide of the present invention can improve the treatment effect of impurities in industrial-grade hydrogen peroxide under the premise of realizing continuous production of high-purity hydrogen peroxide, avoid the influence of impurities in industrial-grade hydrogen peroxide on treatment stability, and effectively improve the matching performance between each treatment section, so as to perform efficient and stable continuous purification and refining of industrial-grade hydrogen peroxide.

Description

一种高纯双氧水的连续制备方法A continuous preparation method of high-purity hydrogen peroxide

技术领域Technical Field

本发明涉及高纯双氧水领域,尤其是涉及一种高纯双氧水的连续制备方法。The invention relates to the field of high-purity hydrogen peroxide, in particular to a continuous preparation method of high-purity hydrogen peroxide.

背景技术Background Art

双氧水(过氧化氢)由于其独特的化学性能,用途十分广泛,应用领域不断扩大,近年来产量不断增加,在电子、医药、航空航天、食品等领域应用广泛。在电子行业,双氧水主要用来作为硅片清洗剂、光刻胶的剥离剂、印刷电路板蚀刻剂使用;在食品行业,双氧水主要用于对食品进行漂白、消毒等处理;在化工行业,双氧水主要用于作为脱氧剂、消毒剂、漂白剂、氧化剂使用。同时,在前述领域中,对双氧水在纯度等方面的要求大大超过了工业级双氧水,一般称为电子级双氧水、食品级双氧水等,统称为高纯双氧水。Due to its unique chemical properties, hydrogen peroxide (hydrogen peroxide) has a wide range of uses and its application areas are constantly expanding. In recent years, its production has continued to increase and it is widely used in the fields of electronics, medicine, aerospace, food, etc. In the electronics industry, hydrogen peroxide is mainly used as a silicon wafer cleaning agent, photoresist stripper, and printed circuit board etchant; in the food industry, hydrogen peroxide is mainly used for bleaching and disinfecting food; in the chemical industry, hydrogen peroxide is mainly used as a deoxidizer, disinfectant, bleaching agent, and oxidant. At the same time, in the aforementioned fields, the requirements for hydrogen peroxide in terms of purity and other aspects far exceed those of industrial-grade hydrogen peroxide. It is generally called electronic-grade hydrogen peroxide, food-grade hydrogen peroxide, etc., collectively referred to as high-purity hydrogen peroxide.

现有技术中,作为高纯双氧水制备的主要原料——工业级双氧水的生产工艺成熟,生产工艺路线主要包括有:蒽醌法、阴极还原法、电解法、异丙醇氧化法等。采用前述方法制备的工业级双氧水必须继续经过进一步的高纯处理,才能够制得满足各领域应用要求的高纯双氧水。现有的工业级双氧水的高纯生产方法主要有:精馏法、树脂吸附法、膜分离法、萃取法等。In the prior art, the production process of industrial-grade hydrogen peroxide, which is the main raw material for the preparation of high-purity hydrogen peroxide, is mature, and the production process routes mainly include: anthraquinone method, cathode reduction method, electrolysis method, isopropanol oxidation method, etc. The industrial-grade hydrogen peroxide prepared by the above methods must continue to undergo further high-purity treatment to obtain high-purity hydrogen peroxide that meets the application requirements of various fields. The existing high-purity production methods of industrial-grade hydrogen peroxide mainly include: distillation method, resin adsorption method, membrane separation method, extraction method, etc.

为实现高纯双氧水的连续化生产,并提高对高纯双氧水的纯化除杂效果,现有技术中公开有采用树脂吸附与膜分离联用的高纯双氧水连续化生产工艺。但是,工业级双氧水中含有的重金属杂质、过渡金属杂质、有机物杂质、有机碳杂质等会影响对工业级双氧水的树脂吸附处理效果,并降低树脂的吸附稳定性,导致采用的树脂吸附材料易于降解,物理性能衰退速度快,有效使用寿命较短;并且树脂吸附对工业级双氧水中的部分有机杂质的选择性不佳,还会直接加重后续的膜分离处理负担,降低膜分离过程的处理稳定性。In order to realize the continuous production of high-purity hydrogen peroxide and improve the purification and impurity removal effect of high-purity hydrogen peroxide, the prior art discloses a high-purity hydrogen peroxide continuous production process using a combination of resin adsorption and membrane separation. However, heavy metal impurities, transition metal impurities, organic impurities, organic carbon impurities, etc. contained in industrial-grade hydrogen peroxide will affect the resin adsorption treatment effect of industrial-grade hydrogen peroxide and reduce the adsorption stability of the resin, resulting in the resin adsorption material being easy to degrade, the physical properties decaying quickly, and the effective service life being short; and the resin adsorption has poor selectivity for some organic impurities in industrial-grade hydrogen peroxide, which will directly increase the burden of subsequent membrane separation treatment and reduce the treatment stability of the membrane separation process.

进一步的,为提高与树脂吸附工段的匹配能力,后续的膜分离过程中需要在高操作压力下进行;同时由于树脂吸附后双氧水中有机杂质的附着沉积污染,以及双氧水的强氧化性,直接导致膜分离过程中存在有膜通量衰减快、膜有效使用寿命短、与树脂吸附工段的匹配稳定性差的问题。Furthermore, in order to improve the matching ability with the resin adsorption section, the subsequent membrane separation process needs to be carried out under high operating pressure; at the same time, due to the adhesion and deposition pollution of organic impurities in hydrogen peroxide after resin adsorption, and the strong oxidizing property of hydrogen peroxide, the membrane separation process directly leads to the problems of rapid membrane flux attenuation, short effective membrane service life, and poor matching stability with the resin adsorption section.

由此,提供一种高纯双氧水的连续制备方法,能够在实现高纯双氧水的连续化生产前提下,提高对工业级双氧水中杂质的处理效果,避免工业级双氧水中杂质对处理稳定性的影响,并有效提高各处理工段相互间的匹配性能,能够对工业级双氧水进行高效、稳定的连续纯化精制,具有重要技术意义。Therefore, a continuous preparation method of high-purity hydrogen peroxide is provided, which can improve the treatment effect of impurities in industrial-grade hydrogen peroxide under the premise of realizing continuous production of high-purity hydrogen peroxide, avoid the influence of impurities in industrial-grade hydrogen peroxide on treatment stability, and effectively improve the matching performance between various treatment sections, and can carry out efficient and stable continuous purification and refining of industrial-grade hydrogen peroxide, which has important technical significance.

发明内容Summary of the invention

为解决现有技术中存在的技术问题,本发明提供一种高纯双氧水的连续制备方法,能够在实现高纯双氧水的连续化生产前提下,提高对工业级双氧水中杂质的处理效果,避免工业级双氧水中杂质对处理稳定性的影响,并有效提高各处理工段相互间的匹配性能,能够对工业级双氧水进行高效、稳定的连续纯化精制。In order to solve the technical problems existing in the prior art, the present invention provides a continuous preparation method of high-purity hydrogen peroxide, which can improve the treatment effect of impurities in industrial-grade hydrogen peroxide under the premise of realizing continuous production of high-purity hydrogen peroxide, avoid the influence of impurities in industrial-grade hydrogen peroxide on treatment stability, and effectively improve the matching performance between various treatment sections, so as to carry out efficient and stable continuous purification and refining of industrial-grade hydrogen peroxide.

为解决以上技术问题,本发明采取的技术方案如下:In order to solve the above technical problems, the technical solution adopted by the present invention is as follows:

一种高纯双氧水的连续制备方法,由以下步骤组成:一级连续吸附、二级连续吸附、树脂连续吸附。A continuous preparation method of high-purity hydrogen peroxide comprises the following steps: first-stage continuous adsorption, second-stage continuous adsorption and resin continuous adsorption.

所述一级连续吸附的方法为,浓度为45-50wt%的工业级双氧水以600-650L/h的进料速率,持续进料至装填有复合吸附剂的第一管式反应器内,控制物料在第一管式反应器内的一级连续吸附温度为5-8℃,物料停留时间为10-12min,经一级连续吸附,持续获得一级吸附液。The method for the primary continuous adsorption is that industrial-grade hydrogen peroxide with a concentration of 45-50wt% is continuously fed into a first tubular reactor filled with a composite adsorbent at a feeding rate of 600-650L/h, the primary continuous adsorption temperature of the material in the first tubular reactor is controlled to be 5-8°C, the material residence time is 10-12min, and the primary adsorption liquid is continuously obtained through the primary continuous adsorption.

所述一级连续吸附中,复合吸附剂在第一管式反应器内的装填量,为1h内流经第一管式反应器的工业级双氧水总重量的1.2-1.3%。In the first-stage continuous adsorption, the loading amount of the composite adsorbent in the first tubular reactor is 1.2-1.3% of the total weight of the industrial-grade hydrogen peroxide flowing through the first tubular reactor within 1 hour.

所述复合吸附剂,由以下步骤制得:改性处理、一级复合、二级复合;The composite adsorbent is prepared by the following steps: modification treatment, primary composite, and secondary composite;

所述改性处理的方法为,将活性炭颗粒投入至5-6倍重量的乙醇溶液(体积浓度50-55%)中,搅拌10-20min后,搅拌升温至30-35℃,保温搅拌滴入改性处理液;控制改性处理液的滴加时间为2-2.5h,滴加完成后,继续保温搅拌40-60min,抽滤分离获得固体物;将固体物置于恒温干燥箱内,90-95℃干燥12-14h,制得改性活性炭颗粒。The modification method comprises the following steps: putting activated carbon particles into an ethanol solution (volume concentration of 50-55%) of 5-6 times the weight thereof, stirring for 10-20 minutes, heating the solution to 30-35°C with stirring, and dripping the modified treatment solution with stirring and heat preservation; controlling the dripping time of the modified treatment solution to be 2-2.5 hours, and after the dripping is completed, continuing to stir and heat preservation for 40-60 minutes, and filtering and separating to obtain a solid; placing the solid in a constant temperature drying oven, and drying the solution at 90-95°C for 12-14 hours to obtain modified activated carbon particles.

所述改性处理中,活性炭颗粒的粒径规格为180-200目;In the modification process, the particle size of the activated carbon particles is 180-200 mesh;

活性炭颗粒与改性处理液的重量比为1:4-4.2。The weight ratio of activated carbon particles to modified treatment liquid is 1:4-4.2.

所述改性处理液的制备方法为,将季戊四醇和氢氧化钠投入至N,N-二甲基甲酰胺中,在氮气气氛保护下,搅拌10-20min后,搅拌升温至55-60℃,保温搅拌滴入环氧氯丙烷,并控制环氧氯丙烷的滴加时间为50-60min;环氧氯丙烷滴加完成后,保温搅拌反应22-24h后,在真空度0.09-0.098MPa环境中,蒸发去除N,N-二甲基甲酰胺,获得蒸余物;将蒸余物与8.5-9倍重量的乙醇溶液(体积浓度50-55%)混合均匀,制得改性处理液。The preparation method of the modified treatment liquid comprises the following steps: adding pentaerythritol and sodium hydroxide into N,N-dimethylformamide, stirring for 10-20 minutes under the protection of nitrogen atmosphere, heating to 55-60°C with stirring, dripping epichlorohydrin with stirring while keeping the temperature, and controlling the dripping time of epichlorohydrin to be 50-60 minutes; after the dripping of epichlorohydrin is completed, keeping the temperature and stirring for reaction for 22-24 hours, evaporating and removing N,N-dimethylformamide in a vacuum environment of 0.09-0.098MPa to obtain a distillation residue; and uniformly mixing the distillation residue with 8.5-9 times the weight of an ethanol solution (volume concentration of 50-55%) to obtain a modified treatment liquid.

所述改性处理液的制备中,季戊四醇、氢氧化钠、N,N-二甲基甲酰胺、环氧氯丙烷的重量比为27-27.5:10-10.5:80-85:76-77。In the preparation of the modified treatment liquid, the weight ratio of pentaerythritol, sodium hydroxide, N,N-dimethylformamide and epichlorohydrin is 27-27.5:10-10.5:80-85:76-77.

所述一级复合的方法为,将改性活性炭颗粒投入至28-30倍重量的N,N-二甲基甲酰胺中,搅拌10-20min后,继续投入四氯化锆、六水硝酸钇、对苯二甲酸、2-氨基对苯二甲酸,超声分散10-20min后,置于密封的高压反应釜内,控制高压反应釜以10-12℃/min的升温速率,升温至120-130℃,保温反应32-36h后,自然冷却至室温,离心分离获得固体物;采用2-3倍重量的N,N-二甲基甲酰胺洗涤固体物后,再采用5-6倍重量的去离子水洗涤固体物,然后置于真空干燥箱内,在真空度0.08-0.09MPa,80-85℃温度环境中,保温干燥16-18h,制得一级复合物。The primary composite method comprises the following steps: adding modified activated carbon particles into 28-30 times the weight of N,N-dimethylformamide, stirring for 10-20 minutes, continuously adding zirconium tetrachloride, yttrium nitrate hexahydrate, terephthalic acid and 2-aminoterephthalic acid, ultrasonically dispersing for 10-20 minutes, placing the particles in a sealed autoclave, controlling the autoclave to heat up to 120-130°C at a heating rate of 10-12°C/min, keeping the temperature for reaction for 32-36 hours, naturally cooling to room temperature, and centrifuging to obtain a solid; washing the solid with 2-3 times the weight of N,N-dimethylformamide, and then washing the solid with 5-6 times the weight of deionized water, and then placing the particles in a vacuum drying oven, keeping the temperature for drying for 16-18 hours in an environment of 80-85°C and a vacuum degree of 0.08-0.09MPa, to obtain a primary composite.

所述一级复合中,改性活性炭颗粒、四氯化锆、六水硝酸钇、对苯二甲酸、2-氨基对苯二甲酸的重量比为120-130:25-25.5:8-8.2:12-12.5:7.3-7.5。In the primary composite, the weight ratio of modified activated carbon particles, zirconium tetrachloride, yttrium nitrate hexahydrate, terephthalic acid, and 2-aminoterephthalic acid is 120-130:25-25.5:8-8.2:12-12.5:7.3-7.5.

所述二级复合的方法为,室温条件下,将一级复合物、凹凸棒土投入至去离子水中,超声分散10-20min后,继续投入偏铝酸钠、氢氧化钠后,搅拌10-15min,继续搅拌滴入硅溶胶;控制硅溶胶的滴加时间为30-40min,滴加完成后,继续搅拌40-50min,停止搅拌并静置22-24h,获得预混液;将预混液置于密封的高压反应釜内,升温至100-105℃,保温反应6-7h后,自然冷却至室温,离心分离获得固体物;采用去离子水洗涤固体物至中性,然后置于真空干燥箱内,在真空度0.08-0.09MPa,80-85℃温度环境中,保温干燥至恒重,制得复合吸附剂。The secondary composite method comprises the following steps: adding the primary composite and attapulgite into deionized water at room temperature, ultrasonically dispersing for 10-20 minutes, adding sodium aluminate and sodium hydroxide, stirring for 10-15 minutes, and dropping silica sol with continued stirring; controlling the dropping time of silica sol to be 30-40 minutes, stirring for 40-50 minutes after the dropping is completed, stopping stirring and standing for 22-24 hours to obtain a premixed liquid; placing the premixed liquid in a sealed high-pressure reactor, heating it to 100-105° C., keeping it warm for 6-7 hours, naturally cooling it to room temperature, and centrifuging it to obtain a solid; washing the solid with deionized water until it is neutral, and then placing it in a vacuum drying oven, keeping it warm and drying it to a constant weight in an environment of a vacuum degree of 0.08-0.09 MPa and a temperature of 80-85° C. to obtain a composite adsorbent.

所述二级复合中,预混液中一级复合物、凹凸棒土、去离子水、偏铝酸钠、氢氧化钠、硅溶胶的重量比为27-27.5:2.2-2.6:200-220:16.2-16.5:16-17:38.5-40;In the secondary compound, the weight ratio of the primary compound, attapulgite, deionized water, sodium aluminate, sodium hydroxide, and silica sol in the premix is 27-27.5:2.2-2.6:200-220:16.2-16.5:16-17:38.5-40;

硅溶胶的质量浓度为28-30wt%。The mass concentration of silica sol is 28-30wt%.

所述二级连续吸附的方法为,一级吸附液持续进料至装填有复合吸附剂的第二管式反应器内,控制物料在第二管式反应器内的二级连续吸附温度为5-8℃,物料停留时间为8-10min,经二级连续吸附,持续获得二级吸附液。The method for secondary continuous adsorption is as follows: the primary adsorption liquid is continuously fed into a second tubular reactor filled with a composite adsorbent, the secondary continuous adsorption temperature of the material in the second tubular reactor is controlled to be 5-8°C, the material residence time is 8-10min, and the secondary adsorption liquid is continuously obtained through secondary continuous adsorption.

所述二级连续吸附中,复合吸附剂与一级连续吸附中采用的复合吸附剂相同;复合吸附剂在第二管式反应器内的装填量,为1h内流经第二管式反应器的一级吸附液总重量的0.9-1%。In the secondary continuous adsorption, the composite adsorbent is the same as the composite adsorbent used in the primary continuous adsorption; the loading amount of the composite adsorbent in the second tubular reactor is 0.9-1% of the total weight of the primary adsorption liquid flowing through the second tubular reactor within 1 hour.

所述树脂连续吸附的方法为,二级吸附液持续流经阳离子树脂吸附柱、阴离子树脂吸附柱后,经设置有0.1μm过滤膜的过滤器循环过滤后,制得高纯双氧水。The method for continuous resin adsorption is that the secondary adsorption liquid continuously flows through the cationic resin adsorption column and the anionic resin adsorption column, and then is cyclically filtered through a filter provided with a 0.1 μm filter membrane to obtain high-purity hydrogen peroxide.

所述树脂连续吸附中,阳离子树脂吸附柱内装填有含磺酸基的苯乙烯-二乙烯基苯共聚物的强酸性阳离子交换树脂,强酸性阳离子交换树脂的平均粒径为0.7-0.8mm;In the resin continuous adsorption, the cationic resin adsorption column is filled with a strong acidic cation exchange resin of a styrene-divinylbenzene copolymer containing a sulfonic acid group, and the average particle size of the strong acidic cation exchange resin is 0.7-0.8 mm;

阴离子树脂吸附柱内装填有季铵化的苯乙烯-二乙烯基苯共聚物的强碱性阴离子交换树脂,强碱性阴离子交换树脂的平均粒径为0.7-0.8mm。The anion resin adsorption column is filled with a strong basic anion exchange resin of a quaternized styrene-divinylbenzene copolymer, and the average particle size of the strong basic anion exchange resin is 0.7-0.8 mm.

与现有技术相比,本发明的有益效果为:Compared with the prior art, the present invention has the following beneficial effects:

(1)本发明的高纯双氧水的连续制备方法,采用复合吸附剂对工业级双氧水持续进行一级连续吸附、二级连续吸附,在复合吸附剂的制备中,采用季戊四醇与环氧氯丙烷制备的季铵化改性处理液对活性炭颗粒进行改性处理,通过季铵化改性处理液对活性炭的静电作用,在调整活性炭表面电荷分布的同时,与活性炭表面化合键键合,制备获得季铵化的改性活性炭颗粒,提高活性炭颗粒在后续一级复合、二级复合中与其他材料的结合性能;然后将改性活性炭颗粒与四氯化锆、对苯二甲酸配合,进行改性活性炭颗粒与金属有机框架材料的复合处理,同时,采用掺杂金属原料六水硝酸钇、掺杂有机配体原料2-氨基对苯二甲酸,进一步提高改性活性炭与金属有机框架材料的结合性能,并调节金属有机框架材料结晶度,提高复合吸附剂的稳定性,以及提高复合吸附剂对工业级双氧水中杂质的针对性吸附性能;然后将一级复合物与凹凸棒土结合后,采用原位生成沸石材料的方式,进一步将一级复合物与凹凸棒土、沸石材料进行复合处理,通过原位生成的方式,实现沸石材料与一级复合物、凹凸棒土的有效复合,制得复合吸附剂,有效提高复合吸附剂针对低温(5-8℃)、高浓度(45-50wt%)、大流量(600-650L/h)工业级双氧水的连续流吸附稳定性,并提高复合吸附剂针对低温、高浓度、大流量工业级双氧水的连续流吸附效果,并同步提高复合吸附剂的长期存储稳定性;在采用复合吸附剂对工业级双氧水持续进行一级连续吸附、二级连续吸附后,通过阳离子树脂吸附柱、阴离子树脂吸附柱配合进行连续吸附处理,制得高纯双氧水;前述各技术手段相互配合、协同作用,能够在实现高纯双氧水的连续化生产前提下,提高对工业级双氧水中杂质的处理效果,避免工业级双氧水中杂质对连续处理中复合吸附剂及吸附树脂的不利影响,有效提高各处理工段相互间的匹配性能,提高复合吸附剂及吸附树脂对工业级双氧水的连续流针对性吸附除杂,实现对工业级双氧水进行高效、稳定的连续纯化精制。(1) The continuous preparation method of high-purity hydrogen peroxide of the present invention comprises the following steps: using a composite adsorbent to continuously perform primary continuous adsorption and secondary continuous adsorption on industrial-grade hydrogen peroxide; in the preparation of the composite adsorbent, a quaternary ammonium modified treatment liquid prepared from pentaerythritol and epichlorohydrin is used to modify activated carbon particles; the quaternary ammonium modified treatment liquid is used to electrostatically act on the activated carbon, and while adjusting the charge distribution on the surface of the activated carbon, the quaternary ammonium modified treatment liquid is chemically bonded with the surface of the activated carbon to prepare quaternary ammonium modified activated carbon particles, thereby improving the binding performance of the activated carbon particles with other materials in subsequent primary and secondary composites; and then the modified activated carbon particles are bonded to the surface of the activated carbon particles. Carbon particles are combined with zirconium tetrachloride and terephthalic acid to carry out composite treatment of modified activated carbon particles and metal organic framework materials. At the same time, yttrium nitrate hexahydrate, a doped metal raw material, and 2-aminoterephthalic acid, a doped organic ligand raw material, are used to further improve the binding performance of the modified activated carbon and the metal organic framework material, and the crystallinity of the metal organic framework material is adjusted to improve the stability of the composite adsorbent and the targeted adsorption performance of the composite adsorbent for impurities in industrial-grade hydrogen peroxide. Then, after combining the primary composite with attapulgite, the primary composite is further combined with attapulgite and zeolite materials by in-situ generation of zeolite materials. The zeolite material is composited and effectively composited with the primary composite material and attapulgite by in-situ generation to obtain a composite adsorbent, which effectively improves the continuous flow adsorption stability of the composite adsorbent for low-temperature (5-8°C), high-concentration (45-50wt%), and large-flow (600-650L/h) industrial-grade hydrogen peroxide, and improves the continuous flow adsorption effect of the composite adsorbent for low-temperature, high-concentration, and large-flow industrial-grade hydrogen peroxide, and simultaneously improves the long-term storage stability of the composite adsorbent; when the composite adsorbent is used for continuous primary and secondary continuous adsorption of industrial-grade hydrogen peroxide Attached, high-purity hydrogen peroxide is prepared by continuous adsorption treatment through the combination of a cationic resin adsorption column and an anionic resin adsorption column; the aforementioned technical means cooperate with each other and work synergistically, and can improve the treatment effect of impurities in industrial-grade hydrogen peroxide under the premise of realizing continuous production of high-purity hydrogen peroxide, avoid the adverse effects of impurities in industrial-grade hydrogen peroxide on composite adsorbents and adsorption resins in continuous treatment, effectively improve the matching performance between various treatment sections, improve the continuous flow targeted adsorption and impurity removal of industrial-grade hydrogen peroxide by composite adsorbents and adsorption resins, and realize efficient and stable continuous purification and refining of industrial-grade hydrogen peroxide.

(2)本发明的高纯双氧水的连续制备方法,以浓度为47wt%,有机碳含量TOC为895.17ppm,氯根含量为484.53ppb,硝酸根含量为79.36ppb,硫酸根含量为125.32ppb,磷酸根含量为63.27ppb,硅含量为18.44ppb,钙含量为16ppt,钾含量为118ppt,钠含量为262ppt,铁含量为26ppt的工业级双氧水为原料,连续纯化处理12h后,第13h时制备的高纯双氧水的有机碳含量TOC为1.31-1.32ppm,氯根含量为6.84-6.90ppb,硝酸根含量为15.16-15.20ppb,硫酸根含量为7.20-7.22ppb,磷酸根含量为4.29-4.31ppb,硅含量为1.13-1.15ppb,钙含量不高于2ppt,钾含量不高于2ppt,钠含量不高于2ppt,铁含量不高于1ppt,蒸发残渣含量为5.2-5.3μg/g,粒径超过0.03μm的颗粒数量为18-19pcs/mL。(2) The continuous preparation method of high-purity hydrogen peroxide of the present invention uses industrial-grade hydrogen peroxide with a concentration of 47wt%, an organic carbon content of 895.17ppm TOC, a chloride content of 484.53ppb, a nitrate content of 79.36ppb, a sulfate content of 125.32ppb, a phosphate content of 63.27ppb, a silicon content of 18.44ppb, a calcium content of 16ppt, a potassium content of 118ppt, a sodium content of 262ppt, and an iron content of 26ppt as a raw material, and continuously purifies the high-purity hydrogen peroxide for 12h. The organic carbon content of the high-purity hydrogen peroxide prepared at the 13th hour is The TOC content is 1.31-1.32ppm, the chloride content is 6.84-6.90ppb, the nitrate content is 15.16-15.20ppb, the sulfate content is 7.20-7.22ppb, the phosphate content is 4.29-4.31ppb, the silicon content is 1.13-1.15ppb, the calcium content is not higher than 2ppt, the potassium content is not higher than 2ppt, the sodium content is not higher than 2ppt, the iron content is not higher than 1ppt, the evaporation residue content is 5.2-5.3μg/g, and the number of particles with a particle size exceeding 0.03μm is 18-19pcs/mL.

(3)本发明的高纯双氧水的连续制备方法,以浓度为47wt%,有机碳含量TOC为895.17ppm,氯根含量为484.53ppb,硝酸根含量为79.36ppb,硫酸根含量为125.32ppb,磷酸根含量为63.27ppb,硅含量为18.44ppb,钙含量为16ppt,钾含量为118ppt,钠含量为262ppt,铁含量为26ppt的工业级双氧水为原料,连续纯化处理192h后,第193h时制备的高纯双氧水的有机碳含量TOC为1.40-1.42ppm,氯根含量为7.35-7.41ppb,硝酸根含量为16.22-16.25ppb,硫酸根含量为7.66-7.69ppb,磷酸根含量为4.56-4.59ppb,硅含量为1.21-1.25ppb,钙含量不高于2ppt,钾含量不高于2ppt,钠含量不高于2ppt,铁含量不高于1ppt,蒸发残渣含量为5.5-5.6μg/g,粒径超过0.03μm的颗粒数量为19-20pcs/mL。(3) The method for continuously preparing high-purity hydrogen peroxide of the present invention uses industrial-grade hydrogen peroxide with a concentration of 47wt%, an organic carbon content of 895.17ppm TOC, a chloride content of 484.53ppb, a nitrate content of 79.36ppb, a sulfate content of 125.32ppb, a phosphate content of 63.27ppb, a silicon content of 18.44ppb, a calcium content of 16ppt, a potassium content of 118ppt, a sodium content of 262ppt, and an iron content of 26ppt as a raw material, and continuously purifies the high-purity hydrogen peroxide for 192h. The organic carbon content of the high-purity hydrogen peroxide prepared at the 193rd hour is 0.0847ppm. The carbon content TOC is 1.40-1.42ppm, the chloride content is 7.35-7.41ppb, the nitrate content is 16.22-16.25ppb, the sulfate content is 7.66-7.69ppb, the phosphate content is 4.56-4.59ppb, the silicon content is 1.21-1.25ppb, the calcium content is not higher than 2ppt, the potassium content is not higher than 2ppt, the sodium content is not higher than 2ppt, the iron content is not higher than 1ppt, the evaporation residue content is 5.5-5.6μg/g, and the number of particles with a particle size exceeding 0.03μm is 19-20pcs/mL.

(4)本发明的高纯双氧水的连续制备方法中,采用的复合吸附剂置于温度30℃,相对湿度70%环境中,静置存储180天后,用于高纯双氧水的连续制备中,以浓度为47wt%,有机碳含量TOC为895.17ppm,氯根含量为484.53ppb,硝酸根含量为79.36ppb,硫酸根含量为125.32ppb,磷酸根含量为63.27ppb,硅含量为18.44ppb,钙含量为16ppt,钾含量为118ppt,钠含量为262ppt,铁含量为26ppt的工业级双氧水为原料,连续纯化处理12h后,第13h时制备的高纯双氧水的有机碳含量TOC为1.34ppm,氯根含量为7.01ppb,硝酸根含量为15.56ppb,硫酸根含量为7.43ppb,磷酸根含量为4.43ppb,硅含量为1.17ppb,钙含量为1ppt,钾含量为2ppt,钠含量为2ppt,铁含量为1ppt,蒸发残渣含量为5.4μg/g,粒径超过0.03μm的颗粒数量为19pcs/mL。(4) In the continuous preparation method of high-purity hydrogen peroxide of the present invention, the composite adsorbent used is placed in an environment with a temperature of 30°C and a relative humidity of 70%, and after being stored for 180 days, it is used in the continuous preparation of high-purity hydrogen peroxide, with a concentration of 47wt%, an organic carbon content TOC of 895.17ppm, a chloride content of 484.53ppb, a nitrate content of 79.36ppb, a sulfate content of 125.32ppb, a phosphate content of 63.27ppb, a silicon content of 18.44ppb, a calcium content of 16ppt, a potassium content of 118ppt, and a sodium content of 262ppt. , industrial-grade hydrogen peroxide with an iron content of 26ppt was used as raw material. After continuous purification for 12 hours, the high-purity hydrogen peroxide prepared at the 13th hour had an organic carbon content TOC of 1.34ppm, a chloride content of 7.01ppb, a nitrate content of 15.56ppb, a sulfate content of 7.43ppb, a phosphate content of 4.43ppb, a silicon content of 1.17ppb, a calcium content of 1ppt, a potassium content of 2ppt, a sodium content of 2ppt, an iron content of 1ppt, an evaporation residue content of 5.4μg/g, and the number of particles with a particle size exceeding 0.03μm was 19pcs/mL.

具体实施方式DETAILED DESCRIPTION

为了对本发明的技术特征、目的和效果有更加清楚的理解,现说明本发明的具体实施方式。In order to have a clearer understanding of the technical features, purposes and effects of the present invention, the specific implementation methods of the present invention are now described.

实施例1Example 1

本实施例提供一种高纯双氧水的连续制备方法,进行处理的工业级双氧水的浓度为47wt%,有机碳含量TOC为895.17ppm,氯根含量为484.53ppb,硝酸根含量为79.36ppb,硫酸根含量为125.32ppb,磷酸根含量为63.27ppb,硅含量为18.44ppb,钙含量为16ppt,钾含量为118ppt,钠含量为262ppt,铁含量为26ppt。The present embodiment provides a continuous preparation method of high-purity hydrogen peroxide. The concentration of the treated industrial-grade hydrogen peroxide is 47wt%, the organic carbon content TOC is 895.17ppm, the chloride content is 484.53ppb, the nitrate content is 79.36ppb, the sulfate content is 125.32ppb, the phosphate content is 63.27ppb, the silicon content is 18.44ppb, the calcium content is 16ppt, the potassium content is 118ppt, the sodium content is 262ppt, and the iron content is 26ppt.

所述高纯双氧水的连续制备方法,具体为:The continuous preparation method of high-purity hydrogen peroxide is specifically as follows:

1、一级连续吸附1. First-stage continuous adsorption

工业级双氧水以600L/h的进料速率,持续进料至装填有复合吸附剂的第一管式反应器内,控制物料在第一管式反应器内的一级连续吸附温度为5℃,物料停留时间为10min,经一级连续吸附,持续获得一级吸附液。Industrial-grade hydrogen peroxide was continuously fed into the first tubular reactor filled with the composite adsorbent at a feed rate of 600 L/h. The primary continuous adsorption temperature of the material in the first tubular reactor was controlled to be 5°C, and the material residence time was 10 min. After the primary continuous adsorption, the primary adsorption liquid was continuously obtained.

其中,复合吸附剂在第一管式反应器内的装填量,为1h内流经第一管式反应器的工业级双氧水总重量的1.2%。The loading amount of the composite adsorbent in the first tubular reactor is 1.2% of the total weight of the industrial-grade hydrogen peroxide flowing through the first tubular reactor within 1 hour.

所述复合吸附剂,由以下步骤制得:The composite adsorbent is prepared by the following steps:

1)改性处理1) Modification treatment

将活性炭颗粒投入至5倍重量的乙醇溶液(体积浓度50%)中,搅拌10min后,搅拌升温至30℃,保温搅拌滴入改性处理液;控制改性处理液的滴加时间为2h,滴加完成后,继续保温搅拌40min,抽滤分离获得固体物;将固体物置于恒温干燥箱内,90℃干燥12h,制得改性活性炭颗粒。Put the activated carbon particles into 5 times the weight of ethanol solution (volume concentration of 50%), stir for 10 minutes, then heat up to 30°C with stirring, and drip the modified treatment liquid while keeping warm and stirring; control the addition time of the modified treatment liquid to be 2 hours, and after the addition is completed, continue to keep warm and stir for 40 minutes, and filter and separate to obtain the solid; place the solid in a constant temperature drying oven and dry it at 90°C for 12 hours to obtain modified activated carbon particles.

其中,活性炭颗粒的粒径规格为180目。Among them, the particle size specification of activated carbon particles is 180 mesh.

活性炭颗粒与改性处理液的重量比为1:4。The weight ratio of activated carbon particles to modified treatment liquid is 1:4.

改性处理液的制备方法为,将季戊四醇和氢氧化钠投入至N,N-二甲基甲酰胺中,在氮气气氛保护下,搅拌10min后,搅拌升温至55℃,保温搅拌滴入环氧氯丙烷,并控制环氧氯丙烷的滴加时间为50min;环氧氯丙烷滴加完成后,保温搅拌反应22h后,在真空度0.09MPa环境中,蒸发去除N,N-二甲基甲酰胺,获得蒸余物;将蒸余物与8.5倍重量的乙醇溶液(体积浓度50%)混合均匀,制得改性处理液。The preparation method of the modified treatment liquid is as follows: pentaerythritol and sodium hydroxide are added to N,N-dimethylformamide, and the mixture is stirred for 10 minutes under the protection of a nitrogen atmosphere, and then the mixture is heated to 55°C with stirring, and epichlorohydrin is added dropwise with stirring while keeping the temperature constant, and the dropping time of epichlorohydrin is controlled to be 50 minutes; after the dropping of epichlorohydrin is completed, the mixture is stirred and reacted for 22 hours with keeping the temperature constant, and then N,N-dimethylformamide is evaporated and removed in a vacuum environment of 0.09 MPa to obtain a distillation residue; the distillation residue is evenly mixed with 8.5 times the weight of an ethanol solution (volume concentration of 50%) to obtain a modified treatment liquid.

季戊四醇、氢氧化钠、N,N-二甲基甲酰胺、环氧氯丙烷的重量比为27:10:80:76。The weight ratio of pentaerythritol, sodium hydroxide, N,N-dimethylformamide and epichlorohydrin is 27:10:80:76.

2)一级复合2) First-level compound

将改性活性炭颗粒投入至28倍重量的N,N-二甲基甲酰胺中,搅拌10min后,继续投入四氯化锆、六水硝酸钇、对苯二甲酸、2-氨基对苯二甲酸,超声分散10min后,置于密封的高压反应釜内,控制高压反应釜以10℃/min的升温速率,升温至120℃,保温反应32h后,自然冷却至室温,离心分离获得固体物;采用2倍重量的N,N-二甲基甲酰胺洗涤固体物后,再采用5倍重量的去离子水洗涤固体物,然后置于真空干燥箱内,在真空度0.08MPa,80℃温度环境中,保温干燥16h,制得一级复合物。The modified activated carbon particles were added into 28 times the weight of N,N-dimethylformamide, stirred for 10 minutes, and then zirconium tetrachloride, yttrium nitrate hexahydrate, terephthalic acid and 2-aminoterephthalic acid were added. After ultrasonic dispersion for 10 minutes, the mixture was placed in a sealed high-pressure reactor, and the high-pressure reactor was heated to 120°C at a heating rate of 10°C/min. After the reaction was kept warm for 32 hours, the mixture was naturally cooled to room temperature and centrifuged to obtain a solid. The solid was washed with 2 times the weight of N,N-dimethylformamide and then with 5 times the weight of deionized water. The solid was then placed in a vacuum drying oven and kept warm and dried for 16 hours at a vacuum degree of 0.08 MPa and a temperature of 80°C to obtain a primary composite.

其中,改性活性炭颗粒、四氯化锆、六水硝酸钇、对苯二甲酸、2-氨基对苯二甲酸的重量比为120:25:8:12:7.3。Among them, the weight ratio of modified activated carbon particles, zirconium tetrachloride, yttrium nitrate hexahydrate, terephthalic acid, and 2-aminoterephthalic acid is 120:25:8:12:7.3.

3)二级复合3) Secondary compound

室温条件下,将一级复合物、凹凸棒土投入至去离子水中,超声分散10min后,继续投入偏铝酸钠、氢氧化钠后,搅拌10min,继续搅拌滴入硅溶胶;控制硅溶胶的滴加时间为30min,滴加完成后,继续搅拌40min,停止搅拌并静置22h,获得预混液;将预混液置于密封的高压反应釜内,升温至100℃,保温反应6h后,自然冷却至室温,离心分离获得固体物;采用去离子水洗涤固体物至中性,然后置于真空干燥箱内,在真空度0.08MPa,80℃温度环境中,保温干燥至恒重,制得复合吸附剂。Under room temperature, the primary composite and attapulgite were added to deionized water, and after ultrasonic dispersion for 10 minutes, sodium aluminate and sodium hydroxide were added, and the mixture was stirred for 10 minutes. Silica sol was added dropwise while stirring; the addition time of silica sol was controlled to be 30 minutes. After the addition was completed, the mixture was stirred for 40 minutes, and the stirring was stopped and allowed to stand for 22 hours to obtain a premixed liquid; the premixed liquid was placed in a sealed high-pressure reactor, heated to 100°C, kept warm for 6 hours, naturally cooled to room temperature, and centrifuged to obtain a solid; the solid was washed with deionized water until it was neutral, and then placed in a vacuum drying oven, kept warm and dried to constant weight at a vacuum degree of 0.08 MPa and a temperature of 80°C to obtain a composite adsorbent.

其中,预混液中一级复合物、凹凸棒土、去离子水、偏铝酸钠、氢氧化钠、硅溶胶的重量比为27:2.2:200:16.2:16:38.5。Among them, the weight ratio of the primary composite, attapulgite, deionized water, sodium aluminate, sodium hydroxide and silica sol in the premix is 27:2.2:200:16.2:16:38.5.

硅溶胶的质量浓度为28wt%。The mass concentration of silica sol is 28wt%.

2、二级连续吸附2. Secondary continuous adsorption

一级吸附液持续进料至装填有复合吸附剂的第二管式反应器内,控制物料在第二管式反应器内的二级连续吸附温度为5℃,物料停留时间为8min,经二级连续吸附,持续获得二级吸附液。The primary adsorption liquid is continuously fed into the second tubular reactor filled with the composite adsorbent, the secondary continuous adsorption temperature of the material in the second tubular reactor is controlled to be 5°C, the material residence time is 8min, and the secondary adsorption liquid is continuously obtained through the secondary continuous adsorption.

其中,复合吸附剂与一级连续吸附中采用的复合吸附剂相同;复合吸附剂在第二管式反应器内的装填量,为1h内流经第二管式反应器的一级吸附液总重量的0.9%。The composite adsorbent is the same as the composite adsorbent used in the primary continuous adsorption; the loading amount of the composite adsorbent in the second tubular reactor is 0.9% of the total weight of the primary adsorption liquid flowing through the second tubular reactor within 1 hour.

3、树脂连续吸附3. Continuous adsorption of resin

二级吸附液持续流经阳离子树脂吸附柱、阴离子树脂吸附柱后,经设置有0.1μm过滤膜的过滤器循环过滤后,制得高纯双氧水。The secondary adsorption liquid continuously flows through the cationic resin adsorption column and the anionic resin adsorption column, and then is cyclically filtered through a filter provided with a 0.1 μm filter membrane to obtain high-purity hydrogen peroxide.

其中,阳离子树脂吸附柱内装填有含磺酸基的苯乙烯-二乙烯基苯共聚物的强酸性阳离子交换树脂(牌号为三菱DIAION UBK08H H+强酸性阳离子交换树脂),强酸性阳离子交换树脂的平均粒径为0.7mm。The cationic resin adsorption column is filled with a strongly acidic cation exchange resin of styrene-divinylbenzene copolymer containing sulfonic acid groups (brand name: Mitsubishi DIAION UBK08H H + strongly acidic cation exchange resin), and the average particle size of the strongly acidic cation exchange resin is 0.7 mm.

阴离子树脂吸附柱内装填有季铵化的苯乙烯-二乙烯基苯共聚物的强碱性阴离子交换树脂(牌号为朗盛MonoPlus MP800强碱性阴离子交换树脂),强碱性阴离子交换树脂的平均粒径为0.7mm。The anion resin adsorption column is filled with a strong basic anion exchange resin of quaternized styrene-divinylbenzene copolymer (brand name: LANXESS MonoPlus MP800 strong basic anion exchange resin), and the average particle size of the strong basic anion exchange resin is 0.7 mm.

实施例2Example 2

本实施例提供一种高纯双氧水的连续制备方法,进行处理的工业级双氧水的浓度为47wt%,有机碳含量TOC为895.17ppm,氯根含量为484.53ppb,硝酸根含量为79.36ppb,硫酸根含量为125.32ppb,磷酸根含量为63.27ppb,硅含量为18.44ppb,钙含量为16ppt,钾含量为118ppt,钠含量为262ppt,铁含量为26ppt。The present embodiment provides a continuous preparation method of high-purity hydrogen peroxide. The concentration of the treated industrial-grade hydrogen peroxide is 47wt%, the organic carbon content TOC is 895.17ppm, the chloride content is 484.53ppb, the nitrate content is 79.36ppb, the sulfate content is 125.32ppb, the phosphate content is 63.27ppb, the silicon content is 18.44ppb, the calcium content is 16ppt, the potassium content is 118ppt, the sodium content is 262ppt, and the iron content is 26ppt.

所述高纯双氧水的连续制备方法,具体为:The continuous preparation method of high-purity hydrogen peroxide is specifically as follows:

1、一级连续吸附1. First-stage continuous adsorption

工业级双氧水以630L/h的进料速率,持续进料至装填有复合吸附剂的第一管式反应器内,控制物料在第一管式反应器内的一级连续吸附温度为6℃,物料停留时间为11min,经一级连续吸附,持续获得一级吸附液。Industrial-grade hydrogen peroxide was continuously fed into the first tubular reactor filled with the composite adsorbent at a feed rate of 630 L/h. The primary continuous adsorption temperature of the material in the first tubular reactor was controlled to be 6°C, and the material residence time was 11 min. After primary continuous adsorption, the primary adsorption liquid was continuously obtained.

其中,复合吸附剂在第一管式反应器内的装填量,为1h内流经第一管式反应器的工业级双氧水总重量的1.25%。The loading amount of the composite adsorbent in the first tubular reactor is 1.25% of the total weight of the industrial-grade hydrogen peroxide flowing through the first tubular reactor within 1 hour.

所述复合吸附剂,由以下步骤制得:The composite adsorbent is prepared by the following steps:

1)改性处理1) Modification treatment

将活性炭颗粒投入至5.5倍重量的乙醇溶液(体积浓度52%)中,搅拌15min后,搅拌升温至32℃,保温搅拌滴入改性处理液;控制改性处理液的滴加时间为2.2h,滴加完成后,继续保温搅拌50min,抽滤分离获得固体物;将固体物置于恒温干燥箱内,92℃干燥13h,制得改性活性炭颗粒。The activated carbon particles were put into 5.5 times the weight of ethanol solution (volume concentration of 52%), stirred for 15 minutes, then heated to 32°C with stirring, and the modified treatment liquid was dripped into the solution while keeping the temperature and stirring; the addition time of the modified treatment liquid was controlled to be 2.2 hours. After the addition was completed, the solution was kept warm and stirred for 50 minutes, and the solid was separated by suction; the solid was placed in a constant temperature drying oven and dried at 92°C for 13 hours to obtain modified activated carbon particles.

其中,活性炭颗粒的粒径规格为190目。Among them, the particle size specification of activated carbon particles is 190 mesh.

活性炭颗粒与改性处理液的重量比为1:4.1。The weight ratio of activated carbon particles to modified treatment liquid is 1:4.1.

改性处理液的制备方法为,将季戊四醇和氢氧化钠投入至N,N-二甲基甲酰胺中,在氮气气氛保护下,搅拌15min后,搅拌升温至58℃,保温搅拌滴入环氧氯丙烷,并控制环氧氯丙烷的滴加时间为55min;环氧氯丙烷滴加完成后,保温搅拌反应23h后,在真空度0.095MPa环境中,蒸发去除N,N-二甲基甲酰胺,获得蒸余物;将蒸余物与8.7倍重量的乙醇溶液(体积浓度52%)混合均匀,制得改性处理液。The preparation method of the modified treatment liquid is as follows: pentaerythritol and sodium hydroxide are added to N,N-dimethylformamide, and the mixture is stirred for 15 minutes under the protection of a nitrogen atmosphere, and then the mixture is heated to 58°C with stirring, and epichlorohydrin is added dropwise with stirring while keeping the temperature constant, and the dropping time of epichlorohydrin is controlled to be 55 minutes; after the dropping of epichlorohydrin is completed, the mixture is stirred and reacted for 23 hours with keeping the temperature constant, and then N,N-dimethylformamide is evaporated and removed in a vacuum environment of 0.095 MPa to obtain a distillation residue; the distillation residue is evenly mixed with 8.7 times the weight of an ethanol solution (volume concentration of 52%) to obtain a modified treatment liquid.

季戊四醇、氢氧化钠、N,N-二甲基甲酰胺、环氧氯丙烷的重量比为27.2:10.1:82:76.5。The weight ratio of pentaerythritol, sodium hydroxide, N,N-dimethylformamide and epichlorohydrin is 27.2:10.1:82:76.5.

2)一级复合2) First-level compound

将改性活性炭颗粒投入至29倍重量的N,N-二甲基甲酰胺中,搅拌15min后,继续投入四氯化锆、六水硝酸钇、对苯二甲酸、2-氨基对苯二甲酸,超声分散15min后,置于密封的高压反应釜内,控制高压反应釜以11℃/min的升温速率,升温至125℃,保温反应34h后,自然冷却至室温,离心分离获得固体物;采用2.5倍重量的N,N-二甲基甲酰胺洗涤固体物后,再采用5.5倍重量的去离子水洗涤固体物,然后置于真空干燥箱内,在真空度0.085MPa,82℃温度环境中,保温干燥17h,制得一级复合物。The modified activated carbon particles were added into 29 times the weight of N,N-dimethylformamide, stirred for 15 minutes, and then zirconium tetrachloride, yttrium nitrate hexahydrate, terephthalic acid and 2-aminoterephthalic acid were added. After ultrasonic dispersion for 15 minutes, the mixture was placed in a sealed high-pressure reactor, and the high-pressure reactor was heated to 125°C at a heating rate of 11°C/min. After the reaction was kept warm for 34 hours, the mixture was naturally cooled to room temperature and centrifuged to obtain a solid. The solid was washed with 2.5 times the weight of N,N-dimethylformamide, and then washed with 5.5 times the weight of deionized water. The solid was then placed in a vacuum drying oven, kept warm and dried for 17 hours at a vacuum degree of 0.085 MPa and a temperature of 82°C to obtain a primary composite.

其中,改性活性炭颗粒、四氯化锆、六水硝酸钇、对苯二甲酸、2-氨基对苯二甲酸的重量比为125:25.3:8.1:12.2:7.4。Among them, the weight ratio of modified activated carbon particles, zirconium tetrachloride, yttrium nitrate hexahydrate, terephthalic acid, and 2-aminoterephthalic acid is 125:25.3:8.1:12.2:7.4.

3)二级复合3) Secondary compound

室温条件下,将一级复合物、凹凸棒土投入至去离子水中,超声分散15min后,继续投入偏铝酸钠、氢氧化钠后,搅拌12min,继续搅拌滴入硅溶胶;控制硅溶胶的滴加时间为35min,滴加完成后,继续搅拌45min,停止搅拌并静置23h,获得预混液;将预混液置于密封的高压反应釜内,升温至102℃,保温反应6.5h后,自然冷却至室温,离心分离获得固体物;采用去离子水洗涤固体物至中性,然后置于真空干燥箱内,在真空度0.085MPa,82℃温度环境中,保温干燥至恒重,制得复合吸附剂。At room temperature, the primary composite and attapulgite were added to deionized water, and after ultrasonic dispersion for 15 minutes, sodium aluminate and sodium hydroxide were added, and the mixture was stirred for 12 minutes. Silica sol was added dropwise while continuing to stir. The addition time of silica sol was controlled to be 35 minutes. After the addition was completed, the mixture was stirred for 45 minutes, and the stirring was stopped and allowed to stand for 23 hours to obtain a premixed liquid. The premixed liquid was placed in a sealed high-pressure reactor, heated to 102°C, and kept warm for reaction for 6.5 hours, and then naturally cooled to room temperature and centrifuged to obtain a solid. The solid was washed with deionized water until it was neutral, and then placed in a vacuum drying oven, and kept warm and dried to constant weight at a vacuum degree of 0.085 MPa and a temperature of 82°C to obtain a composite adsorbent.

其中,预混液中一级复合物、凹凸棒土、去离子水、偏铝酸钠、氢氧化钠、硅溶胶的重量比为27.2:2.5:210:16.4:16.5:39.5。Among them, the weight ratio of the primary composite, attapulgite, deionized water, sodium aluminate, sodium hydroxide and silica sol in the premix is 27.2:2.5:210:16.4:16.5:39.5.

硅溶胶的质量浓度为29wt%。The mass concentration of silica sol is 29wt%.

2、二级连续吸附2. Secondary continuous adsorption

一级吸附液持续进料至装填有复合吸附剂的第二管式反应器内,控制物料在第二管式反应器内的二级连续吸附温度为6℃,物料停留时间为9min,经二级连续吸附,持续获得二级吸附液。The primary adsorption liquid is continuously fed into the second tubular reactor filled with the composite adsorbent, the secondary continuous adsorption temperature of the material in the second tubular reactor is controlled to be 6°C, the material residence time is 9 minutes, and the secondary adsorption liquid is continuously obtained through the secondary continuous adsorption.

其中,复合吸附剂与一级连续吸附中采用的复合吸附剂相同;复合吸附剂在第二管式反应器内的装填量,为1h内流经第二管式反应器的一级吸附液总重量的0.95%。The composite adsorbent is the same as the composite adsorbent used in the primary continuous adsorption; the loading amount of the composite adsorbent in the second tubular reactor is 0.95% of the total weight of the primary adsorption liquid flowing through the second tubular reactor within 1 hour.

3、树脂连续吸附3. Continuous adsorption of resin

二级吸附液持续流经阳离子树脂吸附柱、阴离子树脂吸附柱后,经设置有0.1μm过滤膜的过滤器循环过滤后,制得高纯双氧水。The secondary adsorption liquid continuously flows through the cationic resin adsorption column and the anionic resin adsorption column, and then is cyclically filtered through a filter provided with a 0.1 μm filter membrane to obtain high-purity hydrogen peroxide.

其中,阳离子树脂吸附柱内装填有含磺酸基的苯乙烯-二乙烯基苯共聚物的强酸性阳离子交换树脂(牌号为三菱DIAION UBK08H H+强酸性阳离子交换树脂),强酸性阳离子交换树脂的平均粒径为0.75mm。The cationic resin adsorption column is filled with a strongly acidic cation exchange resin of styrene-divinylbenzene copolymer containing sulfonic acid groups (brand name: Mitsubishi DIAION UBK08H H + strongly acidic cation exchange resin), and the average particle size of the strongly acidic cation exchange resin is 0.75 mm.

阴离子树脂吸附柱内装填有季铵化的苯乙烯-二乙烯基苯共聚物的强碱性阴离子交换树脂(牌号为朗盛MonoPlus MP800强碱性阴离子交换树脂),强碱性阴离子交换树脂的平均粒径为0.75mm。The anion resin adsorption column is filled with a strong basic anion exchange resin of quaternized styrene-divinylbenzene copolymer (brand name: LANXESS MonoPlus MP800 strong basic anion exchange resin), and the average particle size of the strong basic anion exchange resin is 0.75 mm.

实施例3Example 3

本实施例提供一种高纯双氧水的连续制备方法,进行处理的工业级双氧水的浓度为47wt%,有机碳含量TOC为895.17ppm,氯根含量为484.53ppb,硝酸根含量为79.36ppb,硫酸根含量为125.32ppb,磷酸根含量为63.27ppb,硅含量为18.44ppb,钙含量为16ppt,钾含量为118ppt,钠含量为262ppt,铁含量为26ppt。The present embodiment provides a continuous preparation method of high-purity hydrogen peroxide. The concentration of the treated industrial-grade hydrogen peroxide is 47wt%, the organic carbon content TOC is 895.17ppm, the chloride content is 484.53ppb, the nitrate content is 79.36ppb, the sulfate content is 125.32ppb, the phosphate content is 63.27ppb, the silicon content is 18.44ppb, the calcium content is 16ppt, the potassium content is 118ppt, the sodium content is 262ppt, and the iron content is 26ppt.

所述高纯双氧水的连续制备方法,具体为:The continuous preparation method of high-purity hydrogen peroxide is specifically as follows:

1、一级连续吸附1. First-stage continuous adsorption

工业级双氧水以650L/h的进料速率,持续进料至装填有复合吸附剂的第一管式反应器内,控制物料在第一管式反应器内的一级连续吸附温度为8℃,物料停留时间为12min,经一级连续吸附,持续获得一级吸附液。Industrial-grade hydrogen peroxide was continuously fed into the first tubular reactor filled with the composite adsorbent at a feeding rate of 650 L/h. The primary continuous adsorption temperature of the material in the first tubular reactor was controlled to be 8°C, and the material residence time was 12 min. After the primary continuous adsorption, the primary adsorption liquid was continuously obtained.

其中,复合吸附剂在第一管式反应器内的装填量,为1h内流经第一管式反应器的工业级双氧水总重量的1.3%。The loading amount of the composite adsorbent in the first tubular reactor is 1.3% of the total weight of the industrial-grade hydrogen peroxide flowing through the first tubular reactor within 1 hour.

所述复合吸附剂,由以下步骤制得:The composite adsorbent is prepared by the following steps:

1)改性处理1) Modification treatment

将活性炭颗粒投入至6倍重量的乙醇溶液(体积浓度55%)中,搅拌20min后,搅拌升温至35℃,保温搅拌滴入改性处理液;控制改性处理液的滴加时间为2.5h,滴加完成后,继续保温搅拌60min,抽滤分离获得固体物;将固体物置于恒温干燥箱内,95℃干燥14h,制得改性活性炭颗粒。Put the activated carbon particles into 6 times the weight of ethanol solution (volume concentration of 55%), stir for 20 minutes, then heat up to 35°C with stirring, and drip the modified treatment liquid while keeping warm and stirring; control the addition time of the modified treatment liquid to 2.5 hours, and after the addition is completed, continue to keep warm and stir for 60 minutes, and filter and separate to obtain the solid; place the solid in a constant temperature drying oven and dry it at 95°C for 14 hours to obtain modified activated carbon particles.

其中,活性炭颗粒的粒径规格为200目。Among them, the particle size specification of activated carbon particles is 200 mesh.

活性炭颗粒与改性处理液的重量比为1:4.2。The weight ratio of activated carbon particles to modified treatment liquid is 1:4.2.

改性处理液的制备方法为,将季戊四醇和氢氧化钠投入至N,N-二甲基甲酰胺中,在氮气气氛保护下,搅拌20min后,搅拌升温至60℃,保温搅拌滴入环氧氯丙烷,并控制环氧氯丙烷的滴加时间为60min;环氧氯丙烷滴加完成后,保温搅拌反应24h后,在真空度0.098MPa环境中,蒸发去除N,N-二甲基甲酰胺,获得蒸余物;将蒸余物与9倍重量的乙醇溶液(体积浓度55%)混合均匀,制得改性处理液。The preparation method of the modified treatment liquid is as follows: pentaerythritol and sodium hydroxide are added to N,N-dimethylformamide, and the mixture is stirred for 20 minutes under the protection of a nitrogen atmosphere, and then the mixture is heated to 60°C with stirring, and epichlorohydrin is added dropwise with stirring while keeping the temperature constant, and the dropping time of epichlorohydrin is controlled to be 60 minutes; after the dropping of epichlorohydrin is completed, the mixture is stirred and reacted for 24 hours with keeping the temperature constant, and then N,N-dimethylformamide is evaporated and removed in a vacuum environment of 0.098 MPa to obtain a distillation residue; the distillation residue is evenly mixed with 9 times the weight of an ethanol solution (volume concentration of 55%) to obtain a modified treatment liquid.

季戊四醇、氢氧化钠、N,N-二甲基甲酰胺、环氧氯丙烷的重量比为27.5:10.5:85:77。The weight ratio of pentaerythritol, sodium hydroxide, N,N-dimethylformamide and epichlorohydrin is 27.5:10.5:85:77.

2)一级复合2) First-level compound

将改性活性炭颗粒投入至30倍重量的N,N-二甲基甲酰胺中,搅拌20min后,继续投入四氯化锆、六水硝酸钇、对苯二甲酸、2-氨基对苯二甲酸,超声分散20min后,置于密封的高压反应釜内,控制高压反应釜以12℃/min的升温速率,升温至130℃,保温反应36h后,自然冷却至室温,离心分离获得固体物;采用3倍重量的N,N-二甲基甲酰胺洗涤固体物后,再采用6倍重量的去离子水洗涤固体物,然后置于真空干燥箱内,在真空度0.09MPa,85℃温度环境中,保温干燥18h,制得一级复合物。The modified activated carbon particles were added into 30 times the weight of N,N-dimethylformamide, stirred for 20 minutes, and then zirconium tetrachloride, yttrium nitrate hexahydrate, terephthalic acid and 2-aminoterephthalic acid were added. After ultrasonic dispersion for 20 minutes, the mixture was placed in a sealed high-pressure reactor, and the high-pressure reactor was heated to 130°C at a heating rate of 12°C/min. After the reaction was kept warm for 36 hours, the mixture was naturally cooled to room temperature and centrifuged to obtain a solid. The solid was washed with 3 times the weight of N,N-dimethylformamide and then with 6 times the weight of deionized water. The solid was then placed in a vacuum drying oven and kept warm and dried for 18 hours at a vacuum degree of 0.09 MPa and a temperature of 85°C to obtain a primary composite.

其中,改性活性炭颗粒、四氯化锆、六水硝酸钇、对苯二甲酸、2-氨基对苯二甲酸的重量比为130:25.5:8.2:12.5:7.5。Among them, the weight ratio of modified activated carbon particles, zirconium tetrachloride, yttrium nitrate hexahydrate, terephthalic acid, and 2-aminoterephthalic acid is 130:25.5:8.2:12.5:7.5.

3)二级复合3) Secondary compound

室温条件下,将一级复合物、凹凸棒土投入至去离子水中,超声分散20min后,继续投入偏铝酸钠、氢氧化钠后,搅拌15min,继续搅拌滴入硅溶胶;控制硅溶胶的滴加时间为40min,滴加完成后,继续搅拌50min,停止搅拌并静置24h,获得预混液;将预混液置于密封的高压反应釜内,升温至105℃,保温反应7h后,自然冷却至室温,离心分离获得固体物;采用去离子水洗涤固体物至中性,然后置于真空干燥箱内,在真空度0.09MPa,85℃温度环境中,保温干燥至恒重,制得复合吸附剂。At room temperature, the primary composite and attapulgite were added to deionized water, and after ultrasonic dispersion for 20 minutes, sodium aluminate and sodium hydroxide were added, and the mixture was stirred for 15 minutes. Silica sol was added dropwise while continuing to stir. The addition time of silica sol was controlled to be 40 minutes. After the addition was completed, the mixture was stirred for 50 minutes, and the stirring was stopped and allowed to stand for 24 hours to obtain a premixed solution. The premixed solution was placed in a sealed high-pressure reactor, heated to 105°C, and kept warm for 7 hours, then naturally cooled to room temperature, and centrifuged to obtain a solid. The solid was washed with deionized water until it was neutral, and then placed in a vacuum drying oven, and kept warm and dried to constant weight at a vacuum degree of 0.09 MPa and a temperature of 85°C to obtain a composite adsorbent.

其中,预混液中一级复合物、凹凸棒土、去离子水、偏铝酸钠、氢氧化钠、硅溶胶的重量比为27.5:2.6:220:16.5:17:40。Among them, the weight ratio of the primary composite, attapulgite, deionized water, sodium aluminate, sodium hydroxide and silica sol in the premix is 27.5:2.6:220:16.5:17:40.

硅溶胶的质量浓度为30wt%。The mass concentration of silica sol is 30wt%.

2、二级连续吸附2. Secondary continuous adsorption

一级吸附液持续进料至装填有复合吸附剂的第二管式反应器内,控制物料在第二管式反应器内的二级连续吸附温度为8℃,物料停留时间为10min,经二级连续吸附,持续获得二级吸附液。The primary adsorption liquid is continuously fed into the second tubular reactor filled with the composite adsorbent, the secondary continuous adsorption temperature of the material in the second tubular reactor is controlled to be 8°C, the material residence time is 10min, and the secondary adsorption liquid is continuously obtained through the secondary continuous adsorption.

其中,复合吸附剂与一级连续吸附中采用的复合吸附剂相同;复合吸附剂在第二管式反应器内的装填量,为1h内流经第二管式反应器的一级吸附液总重量的1%。The composite adsorbent is the same as the composite adsorbent used in the primary continuous adsorption; the loading amount of the composite adsorbent in the second tubular reactor is 1% of the total weight of the primary adsorption liquid flowing through the second tubular reactor within 1 hour.

3、树脂连续吸附3. Continuous adsorption of resin

二级吸附液持续流经阳离子树脂吸附柱、阴离子树脂吸附柱后,经设置有0.1μm过滤膜的过滤器循环过滤后,制得高纯双氧水。The secondary adsorption liquid continuously flows through the cationic resin adsorption column and the anionic resin adsorption column, and then is cyclically filtered through a filter provided with a 0.1 μm filter membrane to obtain high-purity hydrogen peroxide.

其中,阳离子树脂吸附柱内装填有含磺酸基的苯乙烯-二乙烯基苯共聚物的强酸性阳离子交换树脂(牌号为三菱DIAION UBK08H H+强酸性阳离子交换树脂),强酸性阳离子交换树脂的平均粒径为0.8mm。The cationic resin adsorption column is filled with a strongly acidic cation exchange resin of styrene-divinylbenzene copolymer containing sulfonic acid groups (brand name: Mitsubishi DIAION UBK08H H + strongly acidic cation exchange resin), and the average particle size of the strongly acidic cation exchange resin is 0.8 mm.

阴离子树脂吸附柱内装填有季铵化的苯乙烯-二乙烯基苯共聚物的强碱性阴离子交换树脂(牌号为朗盛MonoPlus MP800强碱性阴离子交换树脂),强碱性阴离子交换树脂的平均粒径为0.8mm。The anion resin adsorption column is filled with a strong basic anion exchange resin of quaternized styrene-divinylbenzene copolymer (brand name: LANXESS MonoPlus MP800 strong basic anion exchange resin), and the average particle size of the strong basic anion exchange resin is 0.8 mm.

对比例1Comparative Example 1

采用实施例2的技术方案,其不同之处在于:1)复合吸附剂的制备中,省略改性处理步骤;将活性炭颗粒直接用于一级复合中;2)一级复合步骤中,省略六水硝酸钇、2-氨基对苯二甲酸的添加。The technical solution of Example 2 is adopted, but the differences are as follows: 1) in the preparation of the composite adsorbent, the modification treatment step is omitted; the activated carbon particles are directly used in the primary composite; 2) in the primary composite step, the addition of yttrium nitrate hexahydrate and 2-aminoterephthalic acid is omitted.

对比例1中采用的工业级双氧水的规格与实施例2相同。The specifications of the industrial-grade hydrogen peroxide used in Comparative Example 1 are the same as those in Example 2.

对比例2Comparative Example 2

采用实施例2的技术方案,其不同之处在于:改性处理步骤中,采用十八烷基三甲基氯化铵的乙醇溶液替代改性处理液;其中,十八烷基三甲基氯化铵的乙醇溶液中,十八烷基三甲基氯化铵的质量百分比含量为6wt%,乙醇溶液的体积浓度为52%;2)省略二级复合步骤,将一级复合物作为吸附剂用于一级连续吸附、二级连续吸附步骤中。The technical scheme of Example 2 is adopted, except that: in the modification treatment step, an ethanol solution of octadecyltrimethylammonium chloride is used instead of the modification treatment liquid; wherein, in the ethanol solution of octadecyltrimethylammonium chloride, the mass percentage content of octadecyltrimethylammonium chloride is 6wt%, and the volume concentration of the ethanol solution is 52%; 2) the secondary composite step is omitted, and the primary composite is used as an adsorbent in the primary continuous adsorption and secondary continuous adsorption steps.

对比例2中采用的工业级双氧水的规格与实施例2相同。The specifications of the industrial-grade hydrogen peroxide used in Comparative Example 2 are the same as those in Example 2.

采用实施例1-3、对比例1-2的高纯双氧水的连续制备方法,对浓度为47wt%,有机碳含量TOC为895.17ppm,氯根含量为484.53ppb,硝酸根含量为79.36ppb,硫酸根含量为125.32ppb,磷酸根含量为63.27ppb,硅含量为18.44ppb,钙含量为16ppt,钾含量为118ppt,钠含量为262ppt,铁含量为26ppt的工业级双氧水进行连续处理12h后,对第13h时制备的高纯双氧水进行取样检测杂质含量,并检测高纯双氧水的蒸发残渣含量、粒径超过0.03μm的颗粒数量。具体结果如下表所示:The continuous preparation method of high-purity hydrogen peroxide of Example 1-3 and Comparative Example 1-2 was used to continuously treat industrial-grade hydrogen peroxide with a concentration of 47wt%, an organic carbon content of 895.17ppm TOC, a chloride content of 484.53ppb, a nitrate content of 79.36ppb, a sulfate content of 125.32ppb, a phosphate content of 63.27ppb, a silicon content of 18.44ppb, a calcium content of 16ppt, a potassium content of 118ppt, a sodium content of 262ppt, and an iron content of 26ppt for 12h. The high-purity hydrogen peroxide prepared at the 13th hour was sampled to detect the impurity content, and the evaporation residue content of the high-purity hydrogen peroxide and the number of particles with a particle size exceeding 0.03μm were detected. The specific results are shown in the following table:

进一步的,采用实施例1-3、对比例1-2的高纯双氧水的连续制备方法,对浓度为47wt%,有机碳含量TOC为895.17ppm,氯根含量为484.53ppb,硝酸根含量为79.36ppb,硫酸根含量为125.32ppb,磷酸根含量为63.27ppb,硅含量为18.44ppb,钙含量为16ppt,钾含量为118ppt,钠含量为262ppt,铁含量为26ppt的工业级双氧水进行连续处理192h后,对第193h时制备的高纯双氧水进行取样检测杂质含量,并检测高纯双氧水的蒸发残渣含量、粒径超过0.03μm的颗粒数量。具体结果如下表所示:Further, the continuous preparation method of high-purity hydrogen peroxide of Example 1-3 and Comparative Example 1-2 was used to continuously treat industrial-grade hydrogen peroxide with a concentration of 47wt%, an organic carbon content of 895.17ppm, a chloride content of 484.53ppb, a nitrate content of 79.36ppb, a sulfate content of 125.32ppb, a phosphate content of 63.27ppb, a silicon content of 18.44ppb, a calcium content of 16ppt, a potassium content of 118ppt, a sodium content of 262ppt, and an iron content of 26ppt for 192h, and then the high-purity hydrogen peroxide prepared at the 193rd hour was sampled to detect the impurity content, and the evaporation residue content of the high-purity hydrogen peroxide and the number of particles with a particle size exceeding 0.03μm were detected. The specific results are shown in the following table:

进一步的,分别将实施例2、对比例1-2的复合吸附剂置于温度30℃,相对湿度70%环境中,静置存储180天后,分别对应采用实施例2、对比例1-2高纯双氧水的连续制备方法,对浓度为47wt%,有机碳含量TOC为895.17ppm,氯根含量为484.53ppb,硝酸根含量为79.36ppb,硫酸根含量为125.32ppb,磷酸根含量为63.27ppb,硅含量为18.44ppb,钙含量为16ppt,钾含量为118ppt,钠含量为262ppt,铁含量为26ppt的工业级双氧水进行连续处理12h后,对第13h时制备的高纯双氧水进行取样检测杂质含量,并检测高纯双氧水的蒸发残渣含量、粒径超过0.03μm的颗粒数量。具体结果如下表所示:Further, the composite adsorbents of Example 2 and Comparative Examples 1-2 were placed in an environment with a temperature of 30°C and a relative humidity of 70%, and after being stored for 180 days, the continuous preparation methods of high-purity hydrogen peroxide of Example 2 and Comparative Examples 1-2 were respectively used to continuously treat industrial-grade hydrogen peroxide with a concentration of 47wt%, an organic carbon content of 895.17ppm, a chloride content of 484.53ppb, a nitrate content of 79.36ppb, a sulfate content of 125.32ppb, a phosphate content of 63.27ppb, a silicon content of 18.44ppb, a calcium content of 16ppt, a potassium content of 118ppt, a sodium content of 262ppt, and an iron content of 26ppt for 12h, and the high-purity hydrogen peroxide prepared at the 13th hour was sampled to detect the impurity content, and the evaporation residue content of the high-purity hydrogen peroxide and the number of particles with a particle size exceeding 0.03μm were detected. The specific results are shown in the following table:

可以看出,本发明的高纯双氧水的连续制备方法,采用复合吸附剂对工业级双氧水持续进行一级连续吸附、二级连续吸附,在复合吸附剂的制备中,采用季戊四醇与环氧氯丙烷制备的季铵化改性处理液对活性炭颗粒进行改性处理,通过季铵化改性处理液对活性炭的静电作用,在调整活性炭表面电荷分布的同时,与活性炭表面化合键键合,制备获得季铵化的改性活性炭颗粒,提高活性炭颗粒在后续一级复合、二级复合中与其他材料的结合性能;然后将改性活性炭颗粒与四氯化锆、对苯二甲酸配合,进行改性活性炭颗粒与金属有机框架材料的复合处理,同时,采用掺杂金属原料六水硝酸钇、掺杂有机配体原料2-氨基对苯二甲酸,进一步提高改性活性炭与金属有机框架材料的结合性能,并调节金属有机框架材料结晶度,提高复合吸附剂的稳定性,以及提高复合吸附剂对工业级双氧水中杂质的针对性吸附性能;然后将一级复合物与凹凸棒土结合后,采用原位生成沸石材料的方式,进一步将一级复合物与凹凸棒土、沸石材料进行复合处理,通过原位生成的方式,实现沸石材料与一级复合物、凹凸棒土的有效复合,制得复合吸附剂,有效提高复合吸附剂针对低温(5-8℃)、高浓度(45-50wt%)、大流量(600-650L/h)工业级双氧水的连续流吸附稳定性,并提高复合吸附剂针对低温、高浓度、大流量工业级双氧水的连续流吸附效果,并同步提高复合吸附剂的长期存储稳定性;在采用复合吸附剂对工业级双氧水持续进行一级连续吸附、二级连续吸附后,通过阳离子树脂吸附柱、阴离子树脂吸附柱配合进行连续吸附处理,制得高纯双氧水;前述各技术手段相互配合、协同作用,能够在实现高纯双氧水的连续化生产前提下,提高对工业级双氧水中杂质的处理效果,避免工业级双氧水中杂质对连续处理中复合吸附剂及吸附树脂的不利影响,有效提高各处理工段相互间的匹配性能,提高复合吸附剂及吸附树脂对工业级双氧水的连续流针对性吸附除杂,实现对工业级双氧水进行高效、稳定的连续纯化精制。It can be seen that the continuous preparation method of high-purity hydrogen peroxide of the present invention uses a composite adsorbent to continuously perform primary continuous adsorption and secondary continuous adsorption on industrial-grade hydrogen peroxide. In the preparation of the composite adsorbent, a quaternary ammonium modification treatment liquid prepared by pentaerythritol and epichlorohydrin is used to modify the activated carbon particles. The quaternary ammonium modification treatment liquid has an electrostatic effect on the activated carbon. While adjusting the charge distribution on the surface of the activated carbon, it is chemically bonded with the surface of the activated carbon to prepare quaternary ammonium modified activated carbon particles, thereby improving the binding performance of the activated carbon particles with other materials in subsequent primary and secondary composites; and then the modified activated carbon particles are added to the composite adsorbent. The modified activated carbon particles are combined with zirconium tetrachloride and terephthalic acid to carry out a composite treatment of the modified activated carbon particles and the metal organic framework material. At the same time, the metal raw material yttrium nitrate hexahydrate and the organic ligand raw material 2-aminoterephthalic acid are used to further improve the binding performance of the modified activated carbon and the metal organic framework material, and the crystallinity of the metal organic framework material is adjusted to improve the stability of the composite adsorbent and the targeted adsorption performance of the composite adsorbent for impurities in industrial-grade hydrogen peroxide. Then, after the primary composite is combined with attapulgite, the primary composite is further combined with the attapulgite by in-situ generation of zeolite material. The composite adsorbent is prepared by in-situ generation to achieve effective composite of zeolite material, primary composite material and attapulgite, which effectively improves the continuous flow adsorption stability of the composite adsorbent for low-temperature (5-8°C), high-concentration (45-50wt%) and large-flow (600-650L/h) industrial-grade hydrogen peroxide, and improves the continuous flow adsorption effect of the composite adsorbent for low-temperature, high-concentration and large-flow industrial-grade hydrogen peroxide, and simultaneously improves the long-term storage stability of the composite adsorbent; when the composite adsorbent is used for continuous primary adsorption and secondary continuous adsorption of industrial-grade hydrogen peroxide After adsorption, a cationic resin adsorption column and an anionic resin adsorption column are used to carry out continuous adsorption treatment to obtain high-purity hydrogen peroxide; the aforementioned technical means cooperate with each other and work synergistically, and can improve the treatment effect of impurities in industrial-grade hydrogen peroxide on the premise of realizing continuous production of high-purity hydrogen peroxide, avoid the adverse effects of impurities in industrial-grade hydrogen peroxide on composite adsorbents and adsorption resins in continuous treatment, effectively improve the matching performance between various treatment sections, improve the continuous flow targeted adsorption and impurity removal of industrial-grade hydrogen peroxide by composite adsorbents and adsorption resins, and realize efficient and stable continuous purification and refining of industrial-grade hydrogen peroxide.

通过对比例1可以看出,复合吸附剂的制备中,省略改性处理步骤,以及在一级复合步骤中,省略六水硝酸钇、2-氨基对苯二甲酸的添加后,缺少季铵化改性处理液对活性炭颗粒的表面改性作用,以及缺少掺杂金属原料六水硝酸钇、掺杂有机配体原料2-氨基对苯二甲酸对金属有机框架材料与改性活性炭颗粒结合的促进作用,及其对复合吸附剂吸附稳定性的改善;对比例1在采用工业级双氧水制备高纯双氧水中,对工业级双氧水的纯化效果降低,具体表现为第13h时制备的高纯双氧水的杂质含量均出现一定程度的升高;同时在长期连续运行过程中,对工业级双氧水的纯化效果降低明显,杂质残留增加后续树脂连续吸附的处理压力,影响树脂吸附材料的吸附稳定性,与一级连续吸附、二级连续吸附的匹配处理性能降低,具体表现为第193h时制备的高纯双氧水的杂质含量均出现明显升高;同时,复合吸附剂的长期存储稳定性也出现一定程度的降低,具体表现为复合吸附剂静置存储180天后,对工业级双氧水的纯化效果出现一定程度的降低。It can be seen from Comparative Example 1 that in the preparation of the composite adsorbent, the modification treatment step is omitted, and in the primary composite step, the addition of yttrium nitrate hexahydrate and 2-aminoterephthalic acid is omitted, and the surface modification effect of the quaternary ammonium modification treatment liquid on the activated carbon particles is lacking, and the promotion effect of the metal-doped raw material yttrium nitrate hexahydrate and the organic ligand-doped raw material 2-aminoterephthalic acid on the combination of the metal organic framework material and the modified activated carbon particles, and the improvement of the adsorption stability of the composite adsorbent are lacking; in Comparative Example 1, in the preparation of high-purity hydrogen peroxide using industrial-grade hydrogen peroxide, the purification effect of industrial-grade hydrogen peroxide is reduced, which is specifically manifested in the preparation at the 13th hour. The impurity content of the high-purity hydrogen peroxide prepared at the 193rd hour increased significantly; at the same time, the purification effect of industrial-grade hydrogen peroxide was significantly reduced during long-term continuous operation, and the residual impurities increased the processing pressure of subsequent resin continuous adsorption, affecting the adsorption stability of the resin adsorption material, and reducing the matching processing performance with the first-stage continuous adsorption and the second-stage continuous adsorption, which was specifically manifested in that the impurity content of the high-purity hydrogen peroxide prepared at the 193rd hour increased significantly; at the same time, the long-term storage stability of the composite adsorbent was also reduced to a certain extent, which was specifically manifested in that after the composite adsorbent was stored for 180 days, the purification effect of industrial-grade hydrogen peroxide was reduced to a certain extent.

通过对比例2可以看出,复合吸附剂的制备中,采用常规季铵盐物质十八烷基三甲基氯化铵的乙醇溶液替代改性处理液;以及省略二级复合步骤后,对于活性炭颗粒的表面改性效果降低,与后续一级复合步骤中金属有机框架材料的结合性能降低;同时,无法进一步与凹凸棒土及沸石材料原位复合,在低温、高浓度、大流量条件下对工业级双氧水的连续流吸附稳定性及吸附效果降低,且复合吸附剂的长期存储稳定性降低;具体表现为第13h时制备的高纯双氧水的杂质含量均出现一定程度的升高;具体表现为连续制备的高纯双氧水的杂质含量均出现一定程度的升高;以及在复合吸附剂静置存储180天后,对工业级双氧水的纯化效果出现一定程度的降低。It can be seen from Comparative Example 2 that in the preparation of the composite adsorbent, an ethanol solution of a conventional quaternary ammonium salt substance octadecyltrimethylammonium chloride is used instead of the modified treatment liquid; and after the secondary composite step is omitted, the surface modification effect of the activated carbon particles is reduced, and the binding performance with the metal organic framework material in the subsequent primary composite step is reduced; at the same time, it is impossible to further in-situ composite with attapulgite and zeolite materials, and the continuous flow adsorption stability and adsorption effect of industrial-grade hydrogen peroxide under low temperature, high concentration and large flow conditions are reduced, and the long-term storage stability of the composite adsorbent is reduced; specifically, the impurity content of the high-purity hydrogen peroxide prepared at the 13th hour increases to a certain extent; specifically, the impurity content of the continuously prepared high-purity hydrogen peroxide increases to a certain extent; and after the composite adsorbent is stored for 180 days, the purification effect of industrial-grade hydrogen peroxide decreases to a certain extent.

除非另有说明,本发明中所采用的百分数均为质量百分数。Unless otherwise specified, all percentages used in the present invention are by mass.

最后应说明的是:以上所述仅为本发明的优选实施例而已,并不用于限制本发明,尽管参照前述实施例对本发明进行了详细的说明,对于本领域的技术人员来说,其依然可以对前述各实施例所记载的技术方案进行修改,或者对其中部分技术特征进行等同替换。凡在本发明的精神和原则之内,所作的任何修改、等同替换、改进等,均应包含在本发明的保护范围之内。Finally, it should be noted that the above description is only a preferred embodiment of the present invention and is not intended to limit the present invention. Although the present invention has been described in detail with reference to the aforementioned embodiments, those skilled in the art can still modify the technical solutions described in the aforementioned embodiments or replace some of the technical features therein by equivalents. Any modification, equivalent replacement, improvement, etc. made within the spirit and principle of the present invention shall be included in the protection scope of the present invention.

Claims (10)

1. The continuous preparation method of the high-purity hydrogen peroxide is characterized by comprising the following steps of: primary continuous adsorption, secondary continuous adsorption and resin continuous adsorption;
Continuously feeding industrial grade hydrogen peroxide with the concentration of 45-50wt% into a first tubular reactor filled with a composite adsorbent, and continuously obtaining a first adsorption liquid through first-stage continuous adsorption;
the composite adsorbent is prepared by the following steps: modification treatment, primary compounding and secondary compounding;
The modification treatment method comprises the steps of adding activated carbon particles into ethanol solution, stirring and heating to 30-35 ℃, and dropwise adding modification treatment liquid under the condition of heat preservation and stirring; after the modification treatment is completed, continuing to keep the temperature and stir, separating to obtain solid matters, and drying to obtain modified activated carbon particles;
the preparation method of the modified treatment liquid comprises the steps of adding pentaerythritol and sodium hydroxide into N, N-dimethylformamide, stirring and heating to 55-60 ℃ under the protection of nitrogen atmosphere, and dropwise adding epichlorohydrin under the condition of heat preservation and stirring; after the addition of the epichlorohydrin is completed, carrying out heat preservation and stirring reaction, and removing N, N-dimethylformamide by vacuum evaporation to obtain a steam residue; uniformly mixing the steam residue with an ethanol solution to prepare a modified treatment solution;
the primary compounding method comprises the steps of putting modified activated carbon particles into N, N-dimethylformamide, continuously putting zirconium tetrachloride, yttrium nitrate hexahydrate, terephthalic acid and 2-amino terephthalic acid after uniform dispersion, putting the mixture into a sealed high-pressure reaction kettle, heating to 120-130 ℃, carrying out heat preservation reaction, and separating to obtain a solid; washing and drying the solid to obtain a first-stage compound;
The secondary compounding method comprises the steps of putting the primary compound and the attapulgite into deionized water at room temperature, continuously putting sodium metaaluminate and sodium hydroxide after uniform dispersion, and stirring and dripping silica sol; after the silica sol is added dropwise, stirring and standing are carried out to obtain a premix; placing the premixed solution in a sealed high-pressure reaction kettle, heating to 100-105 ℃, preserving heat, reacting, and separating to obtain a solid; washing and drying the solid to obtain a composite adsorbent;
the method for the secondary continuous adsorption comprises the steps that primary adsorption liquid is continuously fed into a second tubular reactor filled with a composite adsorbent, and the secondary adsorption liquid is continuously obtained through the secondary continuous adsorption;
The composite adsorbent adopted in the secondary continuous adsorption is the same as the composite adsorbent adopted in the primary continuous adsorption;
and the secondary adsorption liquid is subjected to continuous adsorption by resin to prepare high-purity hydrogen peroxide.
2. The continuous preparation method of high-purity hydrogen peroxide according to claim 1, wherein the resin continuous adsorption method is that the secondary adsorption liquid continuously flows through a cation resin adsorption column and an anion resin adsorption column and then is filtered to prepare high-purity hydrogen peroxide;
The cation resin adsorption column is filled with strong acid cation exchange resin of styrene-divinylbenzene copolymer containing sulfonic acid groups; the anion resin adsorption column is filled with strong alkaline anion exchange resin of quaternized styrene-divinylbenzene copolymer.
3. The continuous preparation method of high-purity hydrogen peroxide according to claim 1, wherein in the primary continuous adsorption, the primary continuous adsorption temperature of the material in the first tubular reactor is 5-8 ℃, and the material residence time is 10-12min;
in the secondary continuous adsorption, the secondary continuous adsorption temperature of the materials in the second tubular reactor is 5-8 ℃, and the retention time of the materials is 8-10min.
4. The continuous production method of high purity hydrogen peroxide according to claim 1, wherein in the primary continuous adsorption, the feeding rate of industrial grade hydrogen peroxide to the first tubular reactor is 600 to 650L/h;
the filling amount of the composite adsorbent in the first tubular reactor is 1.2-1.3% of the total weight of industrial grade hydrogen peroxide flowing through the first tubular reactor within 1 h;
in the secondary continuous adsorption, the loading of the composite adsorbent in the second tubular reactor is 0.9-1% of the total weight of the primary adsorption liquid flowing through the second tubular reactor within 1 h.
5. The continuous preparation method of high-purity hydrogen peroxide according to claim 1, wherein in the modification treatment, the weight ratio of the activated carbon particles to the ethanol solution to the modification treatment solution is 1:5-6:4-4.2;
The volume concentration of the ethanol solution is 50-55%;
Controlling the dripping time of the modified treatment liquid to be 2-2.5h; the heat preservation stirring time after the modification treatment is completed is 40-60min;
the particle size specification of the activated carbon particles is 180-200 meshes.
6. The continuous production method of high purity hydrogen peroxide according to claim 1, wherein in the production of the modification treatment liquid, the addition time of epichlorohydrin is controlled to be 50-60min;
the reaction time of heat preservation and stirring after the completion of the dripping of the epichlorohydrin is 22-24 hours;
the weight ratio of pentaerythritol to sodium hydroxide to N, N-dimethylformamide to epichlorohydrin is 27-27.5:10-10.5:80-85:76-77;
The weight ratio of the distilled residue to the ethanol solution is 1:8.5-9;
the volume concentration of the ethanol solution is 50-55%.
7. The continuous preparation method of high-purity hydrogen peroxide according to claim 1, wherein in the primary compounding, the weight ratio of the modified activated carbon particles to the N, N-dimethylformamide is 1:28-30;
the heating rate for heating to 120-130 ℃ is 10-12 ℃/min;
the reaction time is 32-36h at 120-130 ℃;
the weight ratio of the modified activated carbon particles to the zirconium tetrachloride to the yttrium nitrate hexahydrate to the terephthalic acid to the 2-amino terephthalic acid is 120-130:25-25.5:8-8.2:12-12.5:7.3-7.5.
8. The continuous preparation method of high-purity hydrogen peroxide according to claim 1, wherein in the secondary compounding, the dropwise adding time of the silica sol is controlled to be 30-40min;
Stirring time after silica sol dripping is 40-50min, and standing time is 22-24h;
the reaction time is 6-7h at 100-105 ℃.
9. The continuous preparation method of high-purity hydrogen peroxide according to claim 1, wherein in the secondary compounding, the weight ratio of the primary compound, attapulgite, deionized water, sodium metaaluminate, sodium hydroxide and silica sol in the premix is 27-27.5:2.2-2.6:200-220:16.2-16.5:16-17:38.5-40;
the mass concentration of the silica sol is 28-30wt%.
10. The continuous production method of high-purity hydrogen peroxide according to claim 2, wherein in the resin continuous adsorption, the average particle diameter of the strong acid cation exchange resin used is 0.7-0.8mm; the average particle diameter of the strong-alkaline anion exchange resin is 0.7-0.8mm;
the filtration was carried out by circulating filtration using a filter provided with a 0.1 μm filtration membrane.
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