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CN114524493B - Ammonia recovery device and method for electrochemically treating nitrate wastewater - Google Patents

Ammonia recovery device and method for electrochemically treating nitrate wastewater Download PDF

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CN114524493B
CN114524493B CN202210088024.1A CN202210088024A CN114524493B CN 114524493 B CN114524493 B CN 114524493B CN 202210088024 A CN202210088024 A CN 202210088024A CN 114524493 B CN114524493 B CN 114524493B
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ammonia
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唐崇俭
姚福兵
吴星
柴立元
闵小波
李智卓
林璋
刘治功
唐溪
高天宇
肖睿洋
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    • 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
    • C02F1/4676Treatment of water, waste water, or sewage by electrochemical methods by electrolysis by electrochemical disinfection; by electrooxydation or by electroreduction by electroreduction
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    • C01INORGANIC CHEMISTRY
    • C01CAMMONIA; CYANOGEN; COMPOUNDS THEREOF
    • C01C1/00Ammonia; Compounds thereof
    • C01C1/02Preparation, purification or separation of ammonia
    • C01C1/026Preparation of ammonia from inorganic compounds
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
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    • C02F2101/16Nitrogen compounds, e.g. ammonia
    • C02F2101/163Nitrates
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    • Y02EREDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
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Abstract

本发明提供一种电化学处理硝酸盐废水的氨回收装置,包括电化学反应器,所述电化学反应器内设有阳极室和阴极室,所述阳极室和所述阴极室通过质子交换膜分隔设置,所述电化学反应器内还设有氨回收室;所述阳极室、阴极室和所述氨回收室依次相邻排布,所述阳极室内设有对电极,所述阴极室与所述氨回收室通过隔膜分隔设置,所述隔膜由电极材料和防水透气材料组成;所述氨回收装置还包括用于构成外循环的电解液存储罐、硝酸盐存储罐、氨吸收液存储罐、以及恒流泵。本发明能够将高浓硝酸盐转换为氨根离子,并能直接回收可利用的铵盐产品,在净化高浓硝酸盐废水的同时,以清洁环保的方式直接获得高纯度的资源化物质。

Figure 202210088024

The invention provides an ammonia recovery device for electrochemically treating nitrate wastewater, which includes an electrochemical reactor, an anode chamber and a cathode chamber are arranged in the electrochemical reactor, and the anode chamber and the cathode chamber pass through a proton exchange membrane Separately arranged, the electrochemical reactor is also provided with an ammonia recovery chamber; the anode chamber, cathode chamber and the ammonia recovery chamber are arranged adjacent to each other in sequence, the anode chamber is provided with a counter electrode, and the cathode chamber and the ammonia recovery chamber are arranged adjacent to each other. The ammonia recovery chamber is separated by a diaphragm, and the diaphragm is composed of an electrode material and a waterproof and breathable material; the ammonia recovery device also includes an electrolyte storage tank, a nitrate storage tank, and an ammonia absorption liquid storage tank for forming an external circulation , and a constant flow pump. The invention can convert high-concentration nitrate into ammonium ions, and can directly recover available ammonium salt products, and directly obtain high-purity resource-based substances in a clean and environment-friendly manner while purifying high-concentration nitrate wastewater.

Figure 202210088024

Description

一种电化学处理硝酸盐废水的氨回收装置及方法An ammonia recovery device and method for electrochemically treating nitrate wastewater

技术领域technical field

本发明涉及电化学还原硝酸盐回收氨领域,尤其涉及一种电化学处理硝酸 盐废水的氨回收装置及方法。The invention relates to the field of ammonia recovery by electrochemical reduction of nitrate, in particular to an ammonia recovery device and method for electrochemically treating nitrate wastewater.

背景技术Background technique

氮素是维持生命活动所必要的化学元素之一。水体中的氮素主要以有机氮 和无机氮两种形式存在。有机氮的主要代表是蛋白质、尿素等化合物,无机氮 包括氨氮(NH4 +或NH3)、硝酸盐(NO3 -)、亚硝酸盐(NO2 -)、氮气(N2)等。自然界 中的氮素在环境和各生物之间相互迁移转化构成了氮循环但由于工业生产中未 经处理或处理未达标排放的大量含氮废水,破坏氮循环,从而引发氮素污染。 其中高浓度NO3 -废水是造成氮循环失衡的主要原因之一。冶炼钢铁、电镀、化 肥、核燃料以及电子元件等行业产生的废水中均含有较高浓度NO3 -。如在核工 业中利用浓硝酸清洗金属器件的废水中NO3 -浓度高达50000mg N/L。所以,如 何有效地处理工业中产生的高浓度NO3 -废水成为了水污染控制领域的难点之 一。Nitrogen is one of the chemical elements necessary to maintain life activities. Nitrogen in water mainly exists in two forms: organic nitrogen and inorganic nitrogen. The main representatives of organic nitrogen are compounds such as protein and urea, and inorganic nitrogen includes ammonia nitrogen (NH 4 + or NH 3 ), nitrate (NO 3 - ), nitrite (NO 2 - ), nitrogen (N 2 ), etc. The transfer and transformation of nitrogen in nature between the environment and various organisms constitutes the nitrogen cycle, but due to the large amount of nitrogen-containing wastewater discharged without treatment or treatment that fails to meet the standards in industrial production, the nitrogen cycle is destroyed, thereby causing nitrogen pollution. Among them, high-concentration NO 3 -wastewater is one of the main causes of nitrogen cycle imbalance. The wastewater produced by iron and steel smelting, electroplating, chemical fertilizer, nuclear fuel and electronic components all contains high concentration of NO 3 - . For example, in the nuclear industry, the concentration of NO 3 in the waste water used to clean metal devices with concentrated nitric acid is as high as 50,000 mg N/L. Therefore, how to effectively treat the high-concentration NO 3 -wastewater produced in industry has become one of the difficulties in the field of water pollution control.

氨(NH3)是制造化肥、医药及染料等化工产品不可或缺的原料,更凭借其零 碳、大能量密度、高含氢量、便于储存及燃烧不排放二氧化碳(CO2)等特性已成 为一种潜在的绿色能源载体和燃料。目前,NH3合成主要依赖哈珀-波施 (Haber-Bosch)工艺,全球年生产总量约2亿吨,是世界上产量第二大的化工商 品。但该方法反应条件苛刻(高温高压300~500℃、200~300atm)、能耗高(全球 能耗的1~2%),且排放大量CO2、CH4等温室气体。根据中华人民共和国化工 行业标准《HG/T 4487-2012》合成单位产品NH3排放的碳约1.5tCO2/tNH3。氨 能源协会(Ammonia EnergyAssociation)初步统计,全球每年生产NH3排放的碳 量占全球碳排放总量的~1.6%。Ammonia (NH 3 ) is an indispensable raw material for the manufacture of chemical products such as fertilizers , medicines, and dyes. It has become a Become a potential green energy carrier and fuel. At present, the synthesis of NH mainly relies on the Haber-Bosch (Haber-Bosch) process, and the global annual production total is about 200 million tons, which is the second largest chemical product in the world. However, this method has harsh reaction conditions (high temperature and pressure 300-500°C, 200-300 atm), high energy consumption (1-2% of global energy consumption), and emits a large amount of greenhouse gases such as CO 2 and CH 4 . According to the chemical industry standard "HG/T 4487-2012" of the People's Republic of China, the carbon emission per unit product NH 3 is about 1.5tCO 2 /tNH 3 . According to the preliminary statistics of the Ammonia Energy Association, the global annual production of NH 3 emits 1.6% of the global carbon emissions.

由此可见,将硝酸盐废水中的NO3 -转化NH4 +进而回收NH3的方式,不仅 能够完成对硝酸盐废水的处理,还能以清洁的方式获得NH3。目前,虽然已有 相关研究采用电化学反应的方式将NO3 -转化成为NH4 +,但是,现有的研究主 要集中在NH4 +的选择性,鲜有涉及NH3的回收利用,而且,现有的研究从高浓 硝酸盐废水中回收氨的效果也并不理想。It can be seen that the method of converting NO 3 - in nitrate wastewater into NH 4 + and then recovering NH 3 can not only complete the treatment of nitrate wastewater, but also obtain NH 3 in a clean way. At present, although there have been related studies that use electrochemical reactions to convert NO 3 - into NH 4 + , the existing studies mainly focus on the selectivity of NH 4 + , and rarely involve the recovery and utilization of NH 3 , and, The effect of the existing research on recovering ammonia from high-concentration nitrate wastewater is not ideal.

鉴于此,有必要提供一种电化学处理硝酸盐废水的氨回收装置及方法,以 解决或至少缓解上述氨回收利用不便、以及高浓硝酸盐废水处理困难的缺陷。In view of this, it is necessary to provide an ammonia recovery device and method for electrochemically treating nitrate wastewater, to solve or at least alleviate the above-mentioned disadvantages of ammonia recovery inconvenience and high-concentration nitrate wastewater treatment difficulties.

发明内容Contents of the invention

本发明的主要目的是提供一种电化学处理硝酸盐废水的氨回收装置及方 法,旨在解决上述氨回收利用不便、以及高浓硝酸盐废水处理困难的技术问题。The main purpose of the present invention is to provide an ammonia recovery device and method for electrochemically treating nitrate wastewater, aiming to solve the above-mentioned technical problems of inconvenient ammonia recovery and difficult treatment of high-concentration nitrate wastewater.

为实现上述目的,本发明提供了一种电化学处理硝酸盐废水的氨回收装置, 包括电化学反应器,所述电化学反应器内设有阳极室和阴极室,所述阳极室和 所述阴极室通过质子交换膜分隔设置,所述电化学反应器内还设有氨回收室;To achieve the above object, the present invention provides an ammonia recovery device for electrochemically treating nitrate wastewater, comprising an electrochemical reactor, an anode chamber and a cathode chamber are arranged in the electrochemical reactor, and the anode chamber and the The cathode chamber is separated by a proton exchange membrane, and the electrochemical reactor is also provided with an ammonia recovery chamber;

所述阳极室、阴极室和所述氨回收室依次相邻排布,所述阳极室内设有对 电极,所述阴极室与所述氨回收室通过隔膜分隔设置,所述隔膜包括空气电极;The anode chamber, the cathode chamber and the ammonia recovery chamber are adjacently arranged successively, the anode chamber is provided with a counter electrode, the cathode chamber is separated from the ammonia recovery chamber by a diaphragm, and the diaphragm includes an air electrode;

所述氨回收装置还包括电解液存储罐、硝酸盐存储罐、氨吸收液存储罐、 以及恒流泵;The ammonia recovery device also includes an electrolyte storage tank, a nitrate storage tank, an ammonia absorption liquid storage tank, and a constant flow pump;

其中,所述电解液存储罐的出液部通过所述恒流泵与所述阳极室的进液口 连通设置;所述硝酸盐存储罐的出液部通过所述恒流泵与所述阴极室的进液口 连通设置;所述氨吸收液存储罐的出液部通过所述恒流泵与所述氨回收室的进 液口连通设置。Wherein, the liquid outlet of the electrolyte storage tank is communicated with the liquid inlet of the anode chamber through the constant flow pump; the liquid outlet of the nitrate storage tank is connected with the cathode through the constant flow pump. The liquid inlet of the chamber is connected; the liquid outlet of the ammonia absorption liquid storage tank is connected with the liquid inlet of the ammonia recovery chamber through the constant flow pump.

进一步地,所述对电极为形稳性阳极,所述形稳性阳极包括氧化铅、氧化 铱、氧化钌和硼掺杂金刚石薄膜电极中的其中一种。Further, the counter electrode is a shape-stable anode, and the shape-stable anode includes one of lead oxide, iridium oxide, ruthenium oxide and boron-doped diamond film electrodes.

进一步地,所述阴极室内设有参比电极;所述参比电极包括银氯化银、饱 和甘汞和标准氢电极中的其中一种。Further, the cathode chamber is provided with a reference electrode; the reference electrode includes one of silver silver chloride, saturated calomel and a standard hydrogen electrode.

进一步地,所述空气电极的制备过程包括:将具有电化学还原硝酸盐活性 的材料与乙炔黑混合后均匀涂覆于防水透气膜表面,得所述空气电极;Further, the preparation process of the air electrode includes: mixing the material with electrochemical reduction nitrate activity with acetylene black and evenly coating it on the surface of the waterproof and breathable membrane to obtain the air electrode;

其中,所述具有电化学还原硝酸盐活性的材料包括钛铁矿、磷化钴、纳米 零价铁、四氧化三钴、纳米零价铜以及二氧化钛中的其中一种或多种。Wherein, the material with electrochemical reduction nitrate activity includes one or more of ilmenite, cobalt phosphide, nano-zero-valent iron, tricobalt tetroxide, nano-zero-valent copper and titanium dioxide.

进一步地,所述电解液存储罐内存储有阳极电解液,所述阳极电解液包括 硫酸钠溶液。Further, the anolyte is stored in the electrolyte storage tank, and the anolyte includes sodium sulfate solution.

进一步地,所述硝酸盐存储罐内存储有硝酸盐废水,所述硝酸盐废水中硝 酸盐的浓度范围为500-50000mg N/L。Further, nitrate wastewater is stored in the nitrate storage tank, and the concentration range of nitrate in the nitrate wastewater is 500-50000mg N/L.

进一步地,所述氨吸收液存储罐内存储有氨吸收液,所述氨吸收液包括硫 酸溶液、盐酸溶液和碳酸溶液中的其中一种。Further, the ammonia absorption liquid is stored in the ammonia absorption liquid storage tank, and the ammonia absorption liquid includes one of sulfuric acid solution, hydrochloric acid solution and carbonic acid solution.

进一步地,所述电解液存储罐的进液部与所述阳极室的出液口连通设置; 所述硝酸盐存储罐的进液部与所述阴极室的出液口连通设置;所述氨吸收液存 储罐的进液部与所述氨回收室的出液口连通设置。Further, the liquid inlet of the electrolyte storage tank is communicated with the liquid outlet of the anode chamber; the liquid inlet of the nitrate storage tank is communicated with the liquid outlet of the cathode chamber; the ammonia The liquid inlet of the absorption liquid storage tank communicates with the liquid outlet of the ammonia recovery chamber.

进一步地,所述阳极室的进液口与出液口对向设置,且所述阳极室的进液 口的高度低于出液口;Further, the liquid inlet of the anode chamber is arranged opposite to the liquid outlet, and the height of the liquid inlet of the anode chamber is lower than the liquid outlet;

所述阴极室的进液口与出液口对向设置,且所述阴极室的进液口的高度低 于出液口;The liquid inlet of the cathode chamber is opposite to the liquid outlet, and the height of the liquid inlet of the cathode chamber is lower than the liquid outlet;

所述氨回收室的进液口与出液口对向设置,且所述所述氨回收室的进液口 的高度低于出液口。The liquid inlet of the ammonia recovery chamber is opposite to the liquid outlet, and the height of the liquid inlet of the ammonia recovery chamber is lower than the liquid outlet.

本发明还提供一种氨回收的方法,采用如上述任意一项所述的氨回收装置 从硝酸盐废水中回收氨。The present invention also provides a method for ammonia recovery, using the ammonia recovery device as described in any one of the above to reclaim ammonia from nitrate wastewater.

与现有技术相比,本发明具有以下优点:Compared with the prior art, the present invention has the following advantages:

本发明能够将高浓硝酸盐转换为可直接回收利用的铵盐产品,在净化高浓 硝酸盐废水的同时,以清洁环保的方式直接获得高纯度的资源化物质。具体地:The invention can convert high-concentration nitrate into ammonium salt products that can be directly recycled, and directly obtain high-purity resource-based substances in a clean and environmentally friendly manner while purifying high-concentration nitrate wastewater. specifically:

1、本发明将隔膜和氨吸收室结合,由于隔膜为导电、且具有电化学还原硝 酸盐为铵根离子性能的防水透气膜,可以在电化学反应的条件下使硝酸根转换 为铵根离子,并借助pH的局部升高促进铵根离子转换为氨气,从而在隔膜的 两侧形成压差,使氨气在持续性生成的过程中从阴极室进入氨回收室内,然后 在氨回收室内转换为氨盐产品。1. The present invention combines the diaphragm and the ammonia absorption chamber. Because the diaphragm is conductive and has the performance of electrochemically reducing nitrate to ammonium ion, it can convert nitrate into ammonium under the condition of electrochemical reaction. ions, and with the help of a local increase in pH to promote the conversion of ammonium ions into ammonia gas, so that a pressure difference is formed on both sides of the diaphragm, so that ammonia gas enters the ammonia recovery chamber from the cathode chamber during the continuous generation process, and then the ammonia gas is recovered Indoor conversion to ammonia salt products.

2、本发明将外循环模式与电化学反应器结合,恒流泵将存储罐中的电解液、 硝酸盐废水以及氨吸收液泵入相应的电解池,并从上部的出液口直接回到存储 罐,可以使溶液一直处于流动和均匀状态,省去了搅拌的环节,还减少了设备 占地,并节约了能源。此外,阴极室中硝酸盐溶液一直处于恒流状态,类似于 电容去离子模型,在电场驱动下电化学反硝化产生的铵根离子可定向移动到导 电性防水透气膜表面,有利于氨的回收;而且,氨回收室内处于循环恒流的状 态,可以持续吸收进入氨回收室内的氨气,确保隔膜两侧持续存在压差。2. The present invention combines the external circulation mode with the electrochemical reactor, and the constant flow pump pumps the electrolyte, nitrate waste water and ammonia absorption liquid in the storage tank into the corresponding electrolytic cell, and directly returns to the electrolytic cell from the upper liquid outlet. The storage tank can keep the solution in a flowing and uniform state, eliminating the need for stirring, reducing the equipment footprint, and saving energy. In addition, the nitrate solution in the cathode chamber has been in a constant flow state, similar to the capacitive deionization model, and the ammonium ions generated by electrochemical denitrification under the electric field drive can move to the surface of the conductive waterproof gas-permeable membrane, which is conducive to the removal of ammonia. recovery; moreover, the ammonia recovery chamber is in a state of constant circulation, which can continuously absorb the ammonia gas entering the ammonia recovery chamber to ensure that there is a continuous pressure difference on both sides of the diaphragm.

附图说明Description of drawings

为了更清楚地说明本发明实施例或现有技术中的技术方案,下面将对实施 例或现有技术描述中所需要使用的附图作简单地介绍,显而易见地,下面描述 中的附图仅仅是本发明的一些实施例,对于本领域普通技术人员来讲,在不付 出创造性劳动的前提下,还可以根据这些附图示出的结构获得其他的附图。In order to more clearly illustrate the technical solutions in the embodiments of the present invention or the prior art, the following will briefly introduce the drawings that need to be used in the description of the embodiments or the prior art. Obviously, the accompanying drawings in the following description are only These are some embodiments of the present invention. For those skilled in the art, other drawings can also be obtained according to the structures shown in these drawings without creative work.

图1为本发明一实施例中氨回收装置的模块示意图;Fig. 1 is the module schematic diagram of ammonia recovery device in an embodiment of the present invention;

图2为本发明一实施例中电化学反应器的结构示意图;Fig. 2 is the structural representation of electrochemical reactor in an embodiment of the present invention;

图3为本发明另一实施例中电化学反应器的结构示意图(未示出对电极和 参比电极);Fig. 3 is the structural representation of electrochemical reactor in another embodiment of the present invention (counter electrode and reference electrode are not shown);

图4为本发明实施例2中处理高浓度硝酸盐废水的数据效果图。Fig. 4 is a data effect diagram of treating high-concentration nitrate wastewater in Example 2 of the present invention.

附图标记:1、电化学反应器;2、阳极室;3、对电极;4、质子交换膜;5、 阴极室;6、参比电极;7、隔膜;8、氨回收室;9、电解液存储罐;10、硝酸 盐存储罐;11、氨吸收液存储罐;12、恒流泵;13、第一壳体;14、第一垫片; 15、第二垫片;16、第二壳体;17、第三垫片;18、第四垫片;19、第三壳体。Reference signs: 1, electrochemical reactor; 2, anode chamber; 3, counter electrode; 4, proton exchange membrane; 5, cathode chamber; 6, reference electrode; 7, diaphragm; 8, ammonia recovery chamber; 9, Electrolyte storage tank; 10. Nitrate storage tank; 11. Ammonia absorption liquid storage tank; 12. Constant flow pump; 13. The first shell; 14. The first gasket; 15. The second gasket; 16. The second gasket Two casings; 17, the third gasket; 18, the fourth gasket; 19, the third casing.

本发明目的的实现、功能特点及优点将结合实施方式,参照附图做进一步 说明。The realization of the object of the present invention, function characteristic and advantage will be described further with reference to accompanying drawing in conjunction with embodiment.

具体实施方式Detailed ways

下面将结合本发明实施方式中的附图,对本发明实施方式中的技术方案进 行清楚、完整地描述,显然,所描述的实施方式仅仅是本发明的一部分实施方 式,而不是全部的实施方式。基于本发明中的实施方式,本领域普通技术人员 在没有作出创造性劳动前提下所获得的所有其他实施方式,都属于本发明保护 的范围。The technical solutions in the embodiments of the present invention will be clearly and completely described below in conjunction with the accompanying drawings in the embodiments of the present invention. Obviously, the described embodiments are only part of the embodiments of the present invention, not all of them. Way. Based on the implementation modes in the present invention, all other implementation modes obtained by persons of ordinary skill in the art without creative work, all belong to the protection scope of the present invention.

需要说明,本发明实施方式中所有方向性指示(诸如上、下……)仅用于解 释在某一特定姿态(如附图所示)下各部件之间的相对位置关系、运动情况等, 如果该特定姿态发生改变时,则该方向性指示也相应地随之改变。It should be noted that all directional indications (such as up, down, ...) in the embodiments of the present invention are only used to explain the relative positional relationship, motion, etc. , if the specific attitude changes, the directional indication changes accordingly.

另外,在本发明中如涉及“第一”、“第二”等的描述仅用于描述目的,而不 能理解为指示或暗示其相对重要性或者隐含指明所指示的技术特征的数量。由 此,限定有“第一”、“第二”的特征可以明示或者隐含地包括至少一个该特征。In addition, descriptions such as "first", "second" and so on in the present invention are only for description purposes, and cannot be understood as indicating or implying their relative importance or implicitly specifying the quantity of indicated technical features. Therefore, the features defined as "first" and "second" may explicitly or implicitly include at least one of these features.

并且,本发明各个实施方式之间的技术方案可以相互结合,但是必须是以 本领域普通技术人员能够实现为基础,当技术方案的结合出现相互矛盾或无法 实现时应当认为这种技术方案的结合不存在,也不在本发明要求的保护范围之 内。Moreover, the technical solutions among the various embodiments of the present invention can be combined with each other, but it must be based on the realization of those skilled in the art. When the combination of technical solutions is contradictory or cannot be realized, it should be considered that the combination of technical solutions Does not exist, nor within the scope of protection required by the present invention.

应注意的是,现有技术对于高浓度的硝酸盐处理是缺失的,同时,一般用 于硝酸盐电化学还原回收氨的电极材料的制备都较为复杂,成本较高,距工业 化还有一定的研究空间。It should be noted that the existing technology is lacking in the treatment of high-concentration nitrates. At the same time, the preparation of electrode materials generally used for the electrochemical reduction of nitrates to recover ammonia is relatively complicated and costly, and there is still a certain distance from industrialization. research space.

为了在实现高浓硝酸盐废水净化的同时回收NH3资源,参照图1-3所示, 本发明提供了一种电化学处理硝酸盐废水的氨回收装置,包括电化学反应器1, 所述电化学反应器1内设有阳极室2和阴极室5,所述阳极室2和所述阴极室5 通过质子交换膜4分隔设置。In order to reclaim NH resources while realizing the purification of high-concentration nitrate wastewater, as shown in FIGS. The electrochemical reactor 1 is provided with an anode chamber 2 and a cathode chamber 5 , and the anode chamber 2 and the cathode chamber 5 are separated by a proton exchange membrane 4 .

在此基础上,为了实现氨的回收,所述电化学反应器1内还设有氨回收室 8,以在所述氨回收室8内获得铵盐产品。On this basis, in order to realize the recovery of ammonia, the ammonia recovery chamber 8 is also provided in the described electrochemical reactor 1, to obtain the ammonium salt product in the described ammonia recovery chamber 8.

为了保证电化学反应的进行,所述阳极室2、阴极室5和所述氨回收室8 依次相邻排布,所述阳极室2内设有对电极3。所述阴极室5与所述氨回收室8 通过隔膜7分隔设置,所述隔膜7为空气电极,主要由电极材料和防水透气材 料组成。当然,在进行电化学反应的过程中,所述电化学反应装置的内部需与 外部隔绝,同时还需要引入外部的电源装置进行供电,通过采用外加电源装置 施加恒压或恒流驱动开展电化学处理高浓度硝酸盐废水回收氨的研究;其中, 所述电源装置可以为电化学工作站、稳压电源、直流电源或横电位仪。In order to ensure the carrying out of the electrochemical reaction, the anode chamber 2, the cathode chamber 5 and the ammonia recovery chamber 8 are adjacently arranged in sequence, and the anode chamber 2 is provided with a counter electrode 3. The cathode chamber 5 is separated from the ammonia recovery chamber 8 by a diaphragm 7, and the diaphragm 7 is an air electrode mainly composed of an electrode material and a waterproof and breathable material. Of course, in the process of carrying out the electrochemical reaction, the inside of the electrochemical reaction device needs to be isolated from the outside, and at the same time, an external power supply device needs to be introduced for power supply, and the electrochemical reaction device is carried out by applying a constant voltage or constant current drive by using an external power supply device. Research on treating high-concentration nitrate wastewater and recovering ammonia; wherein, the power supply device can be an electrochemical workstation, a stabilized power supply, a DC power supply or a transverse potentiometer.

需说明的是,所述对电极3充当阳极,而所述隔膜7在充当阴极(工作电极) 的基础上,其还可以使氨气顺利进入所述氨回收室8内,在反应进行过程中, 所述隔膜7处的pH会升至10甚至更高,因此由硝酸根转化而来的铵根离子会 在所述隔膜7处(靠近阴极室5的一侧)产生大量氨气,使得隔膜7两侧形成压 差,进而确保氨气穿过所述隔膜7进入所述氨回收室8内。It should be noted that the counter electrode 3 acts as an anode, and the diaphragm 7 can also make ammonia enter the ammonia recovery chamber 8 smoothly on the basis of serving as a cathode (working electrode). , the pH at the diaphragm 7 will rise to 10 or even higher, so the ammonium ions converted by nitrate will generate a large amount of ammonia gas at the diaphragm 7 (the side near the cathode chamber 5), making the diaphragm A pressure difference is formed on both sides of the 7, thereby ensuring that ammonia passes through the diaphragm 7 and enters the ammonia recovery chamber 8.

此外,为了在减少设备占地和节约能源的情况下提高反应和回收的效率, 所述氨回收装置还包括电解液存储罐9、硝酸盐存储罐10、氨吸收液存储罐11、 以及恒流泵12;其中,所述电解液存储罐9的出液部通过所述恒流泵12与所 述阳极室2的进液口连通设置,所述电解液存储罐9的进液部与所述阳极室2 的出液口连通设置;所述硝酸盐存储罐10的出液部通过所述恒流泵12与所述 阴极室5的进液口连通设置,所述硝酸盐存储罐10的进液部与所述阴极室5 的出液口连通设置;所述氨吸收液存储罐11的出液部通过所述恒流泵12与所 述氨回收室8的进液口连通设置,所述氨吸收液存储罐11的进液部与所述氨回 收室8的出液口连通设置。In addition, in order to improve the efficiency of reaction and recovery while reducing equipment footprint and saving energy, the ammonia recovery device also includes an electrolyte storage tank 9, a nitrate storage tank 10, an ammonia absorption liquid storage tank 11, and a constant flow Pump 12; wherein, the liquid outlet portion of the electrolyte storage tank 9 is communicated with the liquid inlet port of the anode chamber 2 through the constant flow pump 12, and the liquid inlet portion of the electrolyte storage tank 9 is connected to the liquid inlet port of the anode chamber 2. The liquid outlet of the anode chamber 2 is communicated with and arranged; the liquid outlet of the nitrate storage tank 10 is communicated with the liquid inlet of the cathode chamber 5 by the constant flow pump 12, and the inlet of the nitrate storage tank 10 The liquid part is communicated with the liquid outlet of the cathode chamber 5; the liquid outlet of the ammonia absorption liquid storage tank 11 is communicated with the liquid inlet of the ammonia recovery chamber 8 through the constant flow pump 12, and the The liquid inlet portion of the ammonia absorption liquid storage tank 11 communicates with the liquid outlet of the ammonia recovery chamber 8.

需注意的是,在所述恒流泵12的作用下不仅可以使所述阳极室2、所述阴 极室5和所述氨回收室8内的物质可以实现循环流动,从而起到搅拌和换液的 作用;而且,由于所述阴极室5内的物质处于流动过程中,在电场的驱动下, 所述阴极室5内产生的铵根离子很容易定向移动至所述隔膜7的表面,在高pH 的作用下生成氨气,确保所述隔膜7在所述阴极室5的一侧具有高气压,与此 同时,由于进入所述氨回收室8内的氨气会在转化为氨盐产品后参与循环流动, 因此,可以保证所述阴极室5一侧的氨气持续的进入所述氨回收室8,并转换 为所需的铵盐产品。It should be noted that, under the action of the constant flow pump 12, not only can the substances in the anode chamber 2, the cathode chamber 5 and the ammonia recovery chamber 8 be circulated, thereby stirring and The effect of changing the liquid; and, because the material in the cathode chamber 5 is in the flow process, under the drive of the electric field, the ammonium ion generated in the cathode chamber 5 is easy to move to the surface of the diaphragm 7 in an orientation, Ammonia is generated under the action of high pH, ensuring that the diaphragm 7 has a high pressure on one side of the cathode chamber 5, and at the same time, because the ammonia entering the ammonia recovery chamber 8 will be converted into ammonia salt Participate in circulating flow after product, therefore, can guarantee that the ammonia gas on one side of described cathode chamber 5 continuously enters described ammonia recovery chamber 8, and is converted into required ammonium salt product.

还需注意的是,由于铵根离子转换为氨气属于可逆反应,在上述条件下, 氨气持续进入所述氨回收室8,还可以进一步保证所述铵根离子向氨气的转换 效率,从而提高氨的回收效率和回收速度,进而又能保证上述条件的形成。It should also be noted that since the conversion of ammonium ions to ammonia belongs to a reversible reaction, under the above conditions, ammonia continues to enter the ammonia recovery chamber 8, which can further ensure the conversion efficiency of the ammonium ions to ammonia. Thereby, the recovery efficiency and recovery speed of ammonia are improved, and the formation of the above-mentioned conditions can be ensured.

在上述实施方式的具体过程为:在电化学反应的基础下,进入所述阴极室 5内的硝酸根离子会转换为铵根离子;所述隔膜7表面由于电解水或硝酸盐还 原致使pH值升高,有利于铵根离子向氨的转化;当铵根离子开始向氨转化时, 所述隔膜7两侧会形成压差,使得转化后的氨进入所述氨回收室8内,并被所 述氨回收室8内循环流动的硫酸溶液等物质转换为氨盐产品,从而实现硝酸盐 废水的净化和氨产品的获取。The specific process in the above-mentioned embodiment is: on the basis of electrochemical reaction, the nitrate ions entering the cathode chamber 5 will be converted into ammonium ions; value rises, which is beneficial to the conversion of ammonium ions to ammonia; when ammonium ions start to convert to ammonia, a pressure difference will be formed on both sides of the diaphragm 7, so that the converted ammonia enters the ammonia recovery chamber 8, and The sulfuric acid solution and other substances circulating in the ammonia recovery chamber 8 are converted into ammonia salt products, thereby realizing the purification of nitrate wastewater and the acquisition of ammonia products.

作为对所述对电极3的说明,所述对电极3为形稳性阳极,所述形稳性阳 极包括氧化铅、氧化铱、氧化钌和硼掺杂金刚石薄膜电极中的其中一种。As an illustration to the counter electrode 3, the counter electrode 3 is a shape-stable anode, and the shape-stable anode includes one of lead oxide, iridium oxide, ruthenium oxide and boron-doped diamond film electrodes.

作为对所述电化学反应器1的说明,所述电化学反应器1可以为三电极体 系,以三电极体系进行反应时,可以在所述阴极室5内设置参比电极6。所述 参比电极6包括银氯化银、饱和甘汞和标准氢电极中的其中一种。As an illustration to the electrochemical reactor 1, the electrochemical reactor 1 can be a three-electrode system, and when reacting with the three-electrode system, a reference electrode 6 can be set in the cathode chamber 5. Described reference electrode 6 comprises wherein a kind of in silver silver chloride, saturated calomel and standard hydrogen electrode.

作为对所述隔膜7的说明,所述隔膜7可以形容为导电、且具有电化学还 原硝酸盐为铵根离子性能的防水透气膜,即空气电极。所述空气电极的制备过 程包括:将具有电化学还原硝酸盐活性的材料与乙炔黑混合后均匀涂覆于防水 透气膜表面,得所述空气电极;其中,所述具有电化学还原硝酸盐活性的材料 包括钛铁矿、磷化钴、纳米零价铁、四氧化三钴、纳米零价铜以及二氧化钛中 的其中一种或多种。As an illustration to the diaphragm 7, the diaphragm 7 can be described as a waterproof and gas-permeable membrane that is conductive and has the performance of electrochemically reducing nitrate to ammonium ions, i.e. an air electrode. The preparation process of the air electrode includes: mixing the material with electrochemical reduction nitrate activity with acetylene black and evenly coating it on the surface of the waterproof and gas-permeable membrane to obtain the air electrode; wherein, the electrochemical reduction nitrate Active materials include one or more of ilmenite, cobalt phosphide, nano-zero-valent iron, tricobalt tetroxide, nano-zero-valent copper, and titanium dioxide.

示例性地,所述隔膜7的制备过程可以包括:在聚四氟乙烯表面涂布钛铁 矿粉末和乙炔黑的混合物,得所述隔膜7。由于所述隔膜7中含有钛铁矿,因 此,其具有较高的稳定性、耐腐蚀性和导电性,不仅可以对第浓度硝酸盐废水 进行净化,还可以对高浓度废水进行净化。例如,可以对硝酸盐的浓度范围为 500-50000mg N/L的硝酸盐废水进行净化,并获得铵盐产品。Exemplarily, the preparation process of the diaphragm 7 may include: coating a mixture of ilmenite powder and acetylene black on the surface of polytetrafluoroethylene to obtain the diaphragm 7. Because the diaphragm 7 contains ilmenite, it has high stability, corrosion resistance and electrical conductivity, and can not only purify the low-concentration nitrate wastewater, but also purify high-concentration wastewater. For example, it is possible to purify nitrate wastewater with a nitrate concentration range of 500-50000mg N/L and obtain ammonium salt products.

作为对所述电解液存储罐9、所述硝酸盐存储罐10、以及所述氨吸收液存 储罐11的说明,所述电解液存储罐9内存储有阳极电解液,所述阳极电解液包 括硫酸钠溶液。所述硝酸盐存储罐10内存储有硝酸盐废水,所述硝酸盐废水中 硝酸盐的浓度范围可以为500-50000mg N/L。所述氨吸收液存储罐11内存储有 氨吸收液,所述氨吸收液包括硫酸溶液、盐酸溶液和碳酸溶液中的其中一种。As an illustration of the electrolyte storage tank 9, the nitrate storage tank 10, and the ammonia absorption liquid storage tank 11, an anolyte is stored in the electrolyte storage tank 9, and the anolyte Including sodium sulfate solution. Nitrate waste water is stored in the nitrate storage tank 10, and the concentration range of nitrate in the nitrate waste water can be 500-50000mg N/L. The ammonia absorption liquid storage tank 11 is stored with ammonia absorption liquid, and the ammonia absorption liquid includes one of sulfuric acid solution, hydrochloric acid solution and carbonic acid solution.

作为上述实施方式的一个优选方案,为了确保液体的循环流动,所述阳极 室2的进液口与出液口对向设置,且所述阳极室2的进液口的高度低于出液口; 所述阴极室5的进液口与出液口对向设置,且所述阴极室5的进液口的高度低 于出液口;所述氨回收室8的进液口与出液口对向设置,且所述所述氨回收室 8的进液口的高度低于出液口。其中,对于所述阴极室5而言,除了能够保证 液体的循环流动,所述阴极室5的进液口低于出液口,还可以使氨气在自下至 上的运动过程中进入所述氨回收,提高回收效率。As a preferred version of the above embodiment, in order to ensure the circulation of liquid, the liquid inlet of the anode chamber 2 is opposite to the liquid outlet, and the height of the liquid inlet of the anode chamber 2 is lower than the liquid outlet ; The liquid inlet and the liquid outlet of the cathode chamber 5 are oppositely arranged, and the height of the liquid inlet of the cathode chamber 5 is lower than the liquid outlet; the liquid inlet and the liquid outlet of the ammonia recovery chamber 8 It is arranged oppositely, and the height of the liquid inlet of the said ammonia recovery chamber 8 is lower than the liquid outlet. Wherein, for the cathode chamber 5, in addition to ensuring the circulating flow of the liquid, the liquid inlet of the cathode chamber 5 is lower than the liquid outlet, and ammonia gas can also be allowed to enter the chamber during the movement from bottom to top. Ammonia recovery, improve recovery efficiency.

本发明还提供了一种氨回收的方法,采用如上述任意实施方式所述的氨回 收装置从硝酸盐废水中回收氨。The present invention also provides a method for ammonia recovery, using the ammonia recovery device as described in any of the above embodiments to recover ammonia from nitrate wastewater.

为了便于对上述实施方式进行理解,现举例说明:In order to facilitate the understanding of the above-mentioned implementation manner, an example is given to illustrate:

实施例1Example 1

参照图1-3所示,一种氨回收装置,包括电解液存储罐9、硝酸盐存储罐 10、氨吸收液存储罐11、恒流泵12、以及电化学反应器1。Shown with reference to Fig. 1-3, a kind of ammonia recovery device comprises electrolyte storage tank 9, nitrate storage tank 10, ammonia absorption liquid storage tank 11, constant flow pump 12, and electrochemical reactor 1.

所述电化学反应器1包括依次横向排布的第一壳体13、第二壳体16和第 三壳体19,所述第一壳体13上在横向上内凹形成有阳极室2,所述第二壳体 16上形成有横向贯穿的阴极室5,所述第三壳体19在横向上内凹形成有氨回收 室8,所述阳极室2和所述氨回收室8相对设置,所述阳极室2内设有对电极3, 所述阴极室5内设有参比电极6。Described electrochemical reactor 1 comprises the first shell 13, the second shell 16 and the 3rd shell 19 that are arranged laterally successively, and described first shell 13 is concavely formed with anode chamber 2 laterally, The second casing 16 is formed with a cathode chamber 5 that runs through it laterally, and the third casing 19 is concavely formed with an ammonia recovery chamber 8 in the lateral direction, and the anode chamber 2 and the ammonia recovery chamber 8 are relatively arranged. , the anode chamber 2 is provided with a counter electrode 3, and the cathode chamber 5 is provided with a reference electrode 6.

所述第一壳体13与所述第二壳体16之间依次设有第一垫片14、质子交换 膜4和第二垫片15;所述第二壳体16与所述第三壳体19之间依次设有第三垫 片17、所述隔膜7(即空气电极)和第四垫片18,所述第一垫片14、所述第二垫 片15、所述第三垫片17和所述第四垫片18均形成有横向贯穿的通道,以便于 电化学反应的进行和物质的移动。The first gasket 14, the proton exchange membrane 4 and the second gasket 15 are arranged successively between the first casing 13 and the second casing 16; the second casing 16 and the third casing The third gasket 17, the diaphragm 7 (i.e. the air electrode) and the fourth gasket 18 are sequentially arranged between the body 19, the first gasket 14, the second gasket 15, the third gasket Both the sheet 17 and the fourth gasket 18 are formed with transversely penetrating passages, so as to facilitate the electrochemical reaction and the movement of substances.

所述第一壳体13、所述第一垫片14、所述第二垫片15、所述质子交换膜4、 所述第二壳体16、所述第三垫片17、所述隔膜7、所述第四垫片18和所述第 三壳体19通过紧固件密封连接。The first housing 13, the first gasket 14, the second gasket 15, the proton exchange membrane 4, the second housing 16, the third gasket 17, the diaphragm 7. The fourth gasket 18 and the third housing 19 are hermetically connected by fasteners.

所述阳极室2、所述阴极室5和所述氨回收室8均的下部均开设有进液口, 上部均开设有出液口;所述阳极室2的进液口通过所述恒流泵12与所述电解液 存储罐9连通设置,所述阳极室2的出液口也与所述电解液储存罐连通设置; 所述阴极室5的进液口通过所述恒流泵12与所述硝酸盐存储罐10连通设置, 所述阴极室5的出液口也与所述硝酸盐储存罐连通设置;所述氨回收室8的进 液口通过所述恒流泵12与所述氨吸收液存储罐11连通设置,所述氨回收室8 的出液口也与所述氨吸收液存罐连通设置。The lower parts of the anode chamber 2, the cathode chamber 5 and the ammonia recovery chamber 8 are all provided with a liquid inlet, and the upper parts are all provided with a liquid outlet; the liquid inlet of the anode chamber 2 passes through the constant current The pump 12 is communicated with the electrolyte storage tank 9, and the liquid outlet of the anode chamber 2 is also communicated with the electrolyte storage tank; the liquid inlet of the cathode chamber 5 is connected with the constant flow pump 12 The nitrate storage tank 10 is communicated, and the liquid outlet of the cathode chamber 5 is also communicated with the nitrate storage tank; the liquid inlet of the ammonia recovery chamber 8 is connected to the The ammonia absorption liquid storage tank 11 is communicated with and arranged, and the liquid outlet of the ammonia recovery chamber 8 is also communicated with the ammonia absorption liquid storage tank.

实施例2Example 2

采用实施例1中的氨回收装置开展电化学处理高浓度硝酸盐废水回收氨的 实验。Adopt the ammonia recovery device among the embodiment 1 to carry out the experiment of electrochemical treatment high-concentration nitrate wastewater reclaiming ammonia.

其中,阳极电解液采用0.1M的硫酸钠(50mL);高浓度硝酸盐废水采用超 纯水配置的模拟硝酸盐废水(50mL),所述模拟硝酸盐废水包含0.1M硫酸钠和 1000mg N/L硝酸盐;氨吸收液采用0.1M硫酸(50mL);形稳性阳极采用二氧 化钌(4cm×4cm);参比电极6选用银氯化银。Wherein, the anolyte adopts 0.1M sodium sulfate (50mL); the high-concentration nitrate wastewater adopts the simulated nitrate wastewater (50mL) configured by ultrapure water, and the simulated nitrate wastewater contains 0.1M sodium sulfate and 1000mg N/L Nitrate; Ammonia absorption solution adopts 0.1M sulfuric acid (50mL); Shape stability anode adopts ruthenium dioxide (4cm * 4cm); Reference electrode 6 selects silver silver chloride for use.

隔膜7(4cm×4cm)的制备过程为:采用200mg钛铁矿粉末与25mg乙炔 黑混合,得到混合物;将混合物分散于5mL 10g/L聚偏氟乙二烯的氮-氮二甲 基吡咯烷酮溶液,得到黑色浆液;将黑色浆液利用喷涂机均匀涂覆于聚四氟乙 烯防水透气膜表面,得到所述隔膜(即空气电极)。The preparation process of diaphragm 7 (4cm×4cm) is as follows: 200mg ilmenite powder is mixed with 25mg acetylene black to obtain a mixture; the mixture is dispersed in 5mL 10g/L polyvinylidene fluoride nitrogen-nitrogen dimethyl pyrrolidone solution , Obtain the black slurry; The black slurry is evenly coated on the surface of the polytetrafluoroethylene waterproof and breathable membrane by a sprayer to obtain the diaphragm (i.e. the air electrode).

恒流泵12的流动速率为120μL/min,采用万通电化学工作站对隔膜施加 -1.9Vvs.Ag/AgCl的恒定电压。The flow rate of the constant flow pump 12 is 120 μL/min, and a constant voltage of -1.9Vvs.Ag/AgCl is applied to the diaphragm by a Metrohm electrochemical workstation.

实验结果如图4所示,在电解反应10h后,硝酸盐的去除率、铵根离子的 生成率和的氨回收率分别为91.1%,77.6%和85.9%;其中,铵根离子的生成率 指代:降解的硝酸盐中铵根离子的转化率;氨的回收率指代:转化的铵根离子 中氨的回收率。由此可见,本发明所提供的氨回收装置和方法可以同步实现处 理高浓硝酸盐废水和回收氨的双重目标。Experimental result as shown in Figure 4, after electrolysis reaction 10h, the removal rate of nitrate, the generation rate of ammonium ion and the ammonia recovery rate are respectively 91.1%, 77.6% and 85.9%; Wherein, the generation rate of ammonium ion Refers to: the conversion rate of ammonium ions in the degraded nitrate; the recovery rate of ammonia refers to the recovery rate of ammonia in the converted ammonium ions. It can be seen that the ammonia recovery device and method provided by the present invention can simultaneously realize the dual goals of processing high-concentration nitrate wastewater and reclaiming ammonia.

本发明的上述技术方案中,以上仅为本发明的优选实施例,并非因此限制 本发明的专利范围,凡是在本发明的技术构思下,利用本发明说明书及附图内 容所作的等效结构变换,或直接/间接运用在其他相关的技术领域均包括在本发 明的专利保护范围。Among the above-mentioned technical schemes of the present invention, the above are only preferred embodiments of the present invention, and are not intended to limit the scope of patents of the present invention. Under the technical conception of the present invention, the equivalent structures made by utilizing the description of the present invention and the contents of the accompanying drawings Transformation, or direct/indirect use in other related technical fields are all included in the patent protection scope of the present invention.

Claims (9)

1.一种电化学处理硝酸盐废水的氨回收装置,包括电化学反应器,所述电化学反应器内设有阳极室和阴极室,所述阳极室和所述阴极室通过质子交换膜分隔设置,其特征在于,所述电化学反应器内还设有氨回收室;1. An ammonia recovery device for electrochemically treating nitrate waste water, comprising an electrochemical reactor, wherein an anode chamber and a cathode chamber are provided in the electrochemical reactor, and the anode chamber and the cathode chamber are separated by a proton exchange membrane Setting, it is characterized in that, the ammonia recovery chamber is also arranged in the described electrochemical reactor; 所述阳极室、所述阴极室和所述氨回收室依次相邻排布,所述阳极室内设有对电极,所述阴极室与所述氨回收室通过隔膜分隔设置,所述隔膜包括空气电极;The anode chamber, the cathode chamber and the ammonia recovery chamber are arranged adjacently in sequence, the anode chamber is provided with a counter electrode, the cathode chamber and the ammonia recovery chamber are separated by a diaphragm, and the diaphragm includes air electrode; 所述空气电极的制备过程包括:将具有电化学还原硝酸盐活性的材料与乙炔黑混合后均匀涂覆于防水透气膜表面,得所述空气电极;The preparation process of the air electrode includes: mixing a material with electrochemical reduction nitrate activity with acetylene black and then uniformly coating the surface of the waterproof and breathable membrane to obtain the air electrode; 所述氨回收装置还包括电解液存储罐、硝酸盐废水存储罐、氨吸收液存储罐、以及恒流泵;The ammonia recovery device also includes an electrolyte storage tank, a nitrate wastewater storage tank, an ammonia absorption liquid storage tank, and a constant flow pump; 其中,所述电解液存储罐的出液部通过所述恒流泵与所述阳极室的进液口连通设置;所述硝酸盐废水存储罐的出液部通过所述恒流泵与所述阴极室的进液口连通设置;所述氨吸收液存储罐的出液部通过所述恒流泵与所述氨回收室的进液口连通设置;Wherein, the liquid outlet of the electrolyte storage tank is connected to the liquid inlet of the anode chamber through the constant flow pump; the liquid outlet of the nitrate wastewater storage tank is connected to the anode chamber through the constant flow pump The liquid inlet port of the cathode chamber is connected; the liquid outlet part of the ammonia absorption liquid storage tank is connected with the liquid inlet port of the ammonia recovery chamber through the constant flow pump; 所述电解液存储罐的进液部与所述阳极室的出液口连通设置;所述硝酸盐废水存储罐的进液部与所述阴极室的出液口连通设置;所述氨吸收液存储罐的进液部与所述氨回收室的出液口连通设置。The liquid inlet part of the electrolyte storage tank is connected with the liquid outlet of the anode chamber; the liquid inlet part of the nitrate wastewater storage tank is connected with the liquid outlet of the cathode chamber; the ammonia absorption liquid The liquid inlet part of the storage tank is communicated with the liquid outlet port of the ammonia recovery chamber. 2.根据权利要求1所述的氨回收装置,其特征在于,所述对电极为形稳性阳极,所述形稳性阳极包括氧化铅、氧化铱、氧化钌和硼掺杂金刚石薄膜电极中的其中一种。2. The ammonia recovery device according to claim 1, wherein the counter electrode is a shape-stable anode, and the shape-stable anode includes lead oxide, iridium oxide, ruthenium oxide, and boron-doped diamond film electrodes. one of the 3.根据权利要求1所述的氨回收装置,其特征在于,所述阴极室内设有参比电极;所述参比电极包括银氯化银、饱和甘汞和标准氢电极中的其中一种。3. Ammonia recovery device according to claim 1, characterized in that, the cathode chamber is provided with a reference electrode; the reference electrode comprises one of silver silver chloride, saturated calomel and a standard hydrogen electrode . 4.根据权利要求1所述的氨回收装置,其特征在于,所述具有电化学还原硝酸盐活性的材料包括钛铁矿、磷化钴、纳米零价铁、四氧化三钴、纳米零价铜以及二氧化钛中的其中一种或多种。4. Ammonia recovery device according to claim 1, characterized in that, said materials with electrochemical reduction of nitrate activity include ilmenite, cobalt phosphide, nanometer zero-valent iron, tricobalt tetroxide, nanometer zerovalent copper and titanium dioxide one or more of them. 5.根据权利要求1所述的氨回收装置,其特征在于,所述电解液存储罐内存储有阳极电解液,所述阳极电解液包括硫酸钠溶液。5. The ammonia recovery device according to claim 1, characterized in that, an anolyte is stored in the electrolyte storage tank, and the anolyte comprises sodium sulfate solution. 6. 根据权利要求1所述的氨回收装置,其特征在于,所述硝酸盐废水存储罐内存储有硝酸盐废水,所述硝酸盐废水中硝酸盐的浓度范围为500-50000 mg N/L。6. Ammonia recovery device according to claim 1, is characterized in that, nitrate wastewater is stored in the nitrate wastewater storage tank, and the concentration range of nitrate in the nitrate wastewater is 500-50000 mg N/L . 7.根据权利要求1所述的氨回收装置,其特征在于,所述氨吸收液存储罐内存储有氨吸收液,所述氨吸收液包括硫酸溶液、盐酸溶液和碳酸溶液中的其中一种。7. The ammonia recovery device according to claim 1, wherein the ammonia absorption liquid is stored in the ammonia absorption liquid storage tank, and the ammonia absorption liquid comprises one of sulfuric acid solution, hydrochloric acid solution and carbonic acid solution . 8.根据权利要求1所述的氨回收装置,其特征在于,所述阳极室的进液口与出液口对向设置,且所述阳极室的进液口的高度低于出液口;8. The ammonia recovery device according to claim 1, wherein the liquid inlet and the liquid outlet of the anode chamber are oppositely arranged, and the height of the liquid inlet of the anode chamber is lower than the liquid outlet; 所述阴极室的进液口与出液口对向设置,且所述阴极室的进液口的高度低于出液口;The liquid inlet of the cathode chamber is opposite to the liquid outlet, and the height of the liquid inlet of the cathode chamber is lower than the liquid outlet; 所述氨回收室的进液口与出液口对向设置,且所述氨回收室的进液口的高度低于出液口。The liquid inlet and the liquid outlet of the ammonia recovery chamber are oppositely arranged, and the height of the liquid inlet of the ammonia recovery chamber is lower than the liquid outlet. 9.一种氨回收的方法,其特征在于,采用如权利要求1-8任意一项所述的氨回收装置从硝酸盐废水中回收氨。9. A method for ammonia recovery, characterized in that the ammonia recovery device as claimed in any one of claims 1-8 is used to recover ammonia from nitrate wastewater.
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Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN104466212A (en) * 2014-12-10 2015-03-25 哈尔滨工业大学宜兴环保研究院 Ammonia recovery unit based on microbial fuel cell
CN104787977A (en) * 2015-04-17 2015-07-22 湖南大学 Continuous flow integrated electrode bio-membrane reactor and nitrate removal technology
CN106450398A (en) * 2016-10-06 2017-02-22 浙江大学 Method for quickly building microbial fuel cell nitrification system
CN106745676A (en) * 2016-11-25 2017-05-31 浙江工商大学 A kind of ecological many negative electrode urine processing devices and method

Family Cites Families (13)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
GB2267290A (en) * 1992-05-27 1993-12-01 Electricity Ass Tech A Process for the electrolytic destruction of nitrate in aqueous liquids
JP5873085B2 (en) * 2010-07-21 2016-03-01 カンブリアン イノベーション エルエルシー Bio-electrochemical system for treating wastewater and method for treating acid gas
CN105883982B (en) * 2016-04-22 2017-04-12 浙江大学 Device and method for recycling nitrogen and phosphorus of wastewater
CN205575731U (en) * 2016-04-22 2016-09-14 浙江大学 A device for retrieving waste water nitrogen phosphorus
CN106784943B (en) * 2016-12-19 2019-05-14 华南理工大学 A kind of membrane electrode of fuel batter with proton exchange film of high power density and preparation method thereof
CN206422151U (en) * 2017-01-03 2017-08-18 华南理工大学 A kind of microbiological fuel cell reactor
CN108928931B (en) * 2018-07-12 2021-08-20 大连理工大学 A Novel CoFe2O4/CNFs Cathode Catalytic Membrane Coupled Microbial Fuel Cell Two-stage Tandem System and Its Application
CN110436583A (en) * 2019-08-27 2019-11-12 辽宁拓启环保科技有限公司 A kind of depth removes the electrochemical appliance and its application method of nitrate in water removal
CN110681417A (en) * 2019-09-20 2020-01-14 太原理工大学 A kind of preparation method of nano Co3O4/carbon nanotube integrated air electrode catalytic material
CN110921796A (en) * 2019-10-30 2020-03-27 同济大学 Synchronous hydrogen and oxygen production system and method for electrochemical recovery of sewage nitrogen and phosphorus
WO2021127156A1 (en) * 2019-12-17 2021-06-24 Ohmium International, Inc. Systems and methods of water treatment for hydrogen production
CN111167513B (en) * 2019-12-25 2021-02-19 同济大学 A flexible electrocatalytic membrane for removing nitrate in water and its preparation method and application
CN111115767B (en) * 2020-01-19 2024-07-19 中南大学 Method and device for continuous deep purification treatment of thallium-containing industrial wastewater

Patent Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN104466212A (en) * 2014-12-10 2015-03-25 哈尔滨工业大学宜兴环保研究院 Ammonia recovery unit based on microbial fuel cell
CN104787977A (en) * 2015-04-17 2015-07-22 湖南大学 Continuous flow integrated electrode bio-membrane reactor and nitrate removal technology
CN106450398A (en) * 2016-10-06 2017-02-22 浙江大学 Method for quickly building microbial fuel cell nitrification system
CN106745676A (en) * 2016-11-25 2017-05-31 浙江工商大学 A kind of ecological many negative electrode urine processing devices and method

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