CN107522267A - A kind of multistage out-phase three-dimensional electrochemical reaction unit for waste water treatment - Google Patents
A kind of multistage out-phase three-dimensional electrochemical reaction unit for waste water treatment Download PDFInfo
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Classifications
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/46—Treatment of water, waste water, or sewage by electrochemical methods
- C02F1/461—Treatment of water, waste water, or sewage by electrochemical methods by electrolysis
- C02F1/46104—Devices therefor; Their operating or servicing
- C02F1/46109—Electrodes
- C02F1/46114—Electrodes in particulate form or with conductive and/or non conductive particles between them
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/46—Treatment of water, waste water, or sewage by electrochemical methods
- C02F1/461—Treatment of water, waste water, or sewage by electrochemical methods by electrolysis
- C02F1/467—Treatment of water, waste water, or sewage by electrochemical methods by electrolysis by electrochemical disinfection; by electrooxydation or by electroreduction
- C02F1/4672—Treatment of water, waste water, or sewage by electrochemical methods by electrolysis by electrochemical disinfection; by electrooxydation or by electroreduction by electrooxydation
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/46—Treatment of water, waste water, or sewage by electrochemical methods
- C02F1/461—Treatment of water, waste water, or sewage by electrochemical methods by electrolysis
- C02F1/46104—Devices therefor; Their operating or servicing
- C02F1/46109—Electrodes
- C02F2001/46133—Electrodes characterised by the material
- C02F2001/46138—Electrodes comprising a substrate and a coating
- C02F2001/46142—Catalytic coating
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2201/00—Apparatus for treatment of water, waste water or sewage
- C02F2201/46—Apparatus for electrochemical processes
- C02F2201/461—Electrolysis apparatus
- C02F2201/46105—Details relating to the electrolytic devices
- C02F2201/4619—Supplying gas to the electrolyte
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2305/00—Use of specific compounds during water treatment
- C02F2305/02—Specific form of oxidant
- C02F2305/023—Reactive oxygen species, singlet oxygen, OH radical
Landscapes
- Chemical & Material Sciences (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Electrochemistry (AREA)
- General Chemical & Material Sciences (AREA)
- Life Sciences & Earth Sciences (AREA)
- Hydrology & Water Resources (AREA)
- Engineering & Computer Science (AREA)
- Environmental & Geological Engineering (AREA)
- Water Supply & Treatment (AREA)
- Organic Chemistry (AREA)
- Water Treatment By Electricity Or Magnetism (AREA)
Abstract
Description
技术领域technical field
本发明属于污水处理技术领域,涉及一种多段异相三维电化学反应装置。The invention belongs to the technical field of sewage treatment and relates to a multi-stage heterogeneous three-dimensional electrochemical reaction device.
背景技术Background technique
目前国内大量高浓度和难降解工业废水的治理问题成为环境领域亟待解决的重大课题,这些工业废水有机物浓度高,可生化性差,成分复杂,含有生物致毒物质,传统的物化和生化处理方法具有较大的局限性。At present, the treatment of a large number of high-concentration and refractory industrial wastewater in China has become a major issue that needs to be solved urgently in the environmental field. These industrial wastewater have high concentrations of organic matter, poor biodegradability, complex components, and biological toxic substances. Traditional physicochemical and biochemical treatment methods have Greater limitations.
三维电化学技术是一种新型的高级氧化技术,是在传统的二维电化学反应器中填充粒子电极构成,具有处理效率高,水力停留时间短,占地面积少,废渣少,广谱适应性等优点,具有广阔的应用前景,成为目前国内外污染控制领域的研究热点之一。三维电化学的作用机理包括直接作用和间接作用。直接作用是在电极表面进行的电化学氧化和还原反应,电极表面既包括阴阳主电极表面,也包括所有粒子电极表面。众多的粒子电极极大增大了溶液与电极的接触面积,缩短了传质距离,提高了电流效率和污染物降解效果。Three-dimensional electrochemical technology is a new type of advanced oxidation technology. It is composed of particle electrodes filled in traditional two-dimensional electrochemical reactors. It has high treatment efficiency, short hydraulic retention time, small footprint, less waste residue, and broad spectrum adaptability It has broad application prospects and has become one of the research hotspots in the field of pollution control at home and abroad. The action mechanism of three-dimensional electrochemistry includes direct action and indirect action. The direct effect is the electrochemical oxidation and reduction reaction carried out on the electrode surface, which includes both the surface of the main electrode of the yin and yang, and the surface of all particle electrodes. Numerous particle electrodes greatly increase the contact area between the solution and the electrode, shorten the mass transfer distance, and improve the current efficiency and pollutant degradation effect.
间接作用是指电场中引发的自由基链式反应,经过曝气溶解的氧气、阳极及粒子电极阳极端产生的氧气,在阴极和粒子电极阴极端还原生成氧化性极强的双氧水和羟基自由基,同时又在体系内电磁场及氧化还原电子对催化剂的作用下,产生大量氧化性极强的自由基,HO2 -·,O·,H·,O2 -·, O3 -·等。这些自由基与废水中有机物反应,生成不稳定的有机物自由基R·等,从而引发大量的自由基链式反应,从而将有机污染物逐步彻底氧化分解为CO2和H2O。The indirect effect refers to the chain reaction of free radicals induced in the electric field. After aeration, the dissolved oxygen, the oxygen generated at the anode and the anode of the particle electrode, are reduced at the cathode and the cathode of the particle electrode to generate highly oxidizing hydrogen peroxide and hydroxyl radicals. , and at the same time, under the action of the electromagnetic field and redox electrons in the system on the catalyst, a large number of highly oxidizing free radicals, such as HO 2 - ·, O·, H·, O 2 - ·, O 3 - ·, etc. are generated. These free radicals react with organic matter in wastewater to generate unstable organic free radicals R·, etc., which trigger a large number of free radical chain reactions, thereby gradually and completely oxidizing and decomposing organic pollutants into CO 2 and H 2 O.
目前三维电化学技术的实际工程应用还很少,设备投资高,运行费用高,没有成熟的设备和工艺。大规模运用三维电化学技术还需要在反应装置结构、粒子电极材料性质、催化剂种类性质、运行工艺条件等方面开展大量的基础研究工作和工程实践。At present, the actual engineering application of three-dimensional electrochemical technology is still very little, the equipment investment is high, the operation cost is high, and there is no mature equipment and process. The large-scale application of three-dimensional electrochemical technology also requires a lot of basic research work and engineering practice in terms of the structure of the reaction device, the properties of the particle electrode material, the nature of the catalyst type, and the operating process conditions.
发明内容Contents of the invention
本发明的目的是针对现有技术的不足而提供的一种结构简约、操作简单、易于维护和自动化控制,处理效率高、无需投加任何化学药剂、产泥量少、效率高的多段异相三维电化学反应装置。The purpose of the present invention is to provide a simple structure, simple operation, easy maintenance and automatic control, high processing efficiency, no need to add any chemical agents, low sludge production and high efficiency multi-stage out-of-phase Three-dimensional electrochemical reaction device.
为实现上述目的,本发明采用以下技术方案:To achieve the above object, the present invention adopts the following technical solutions:
一种用于废水治理的多段异相三维电化学反应装置,特点是该装置包括:本体、外置电源及外置气体发生器,所述本体前端设置进水口,末端设置出水口,其内至少设置二段反应器,各段反应器相串联并通过溢流口实现邻段反应器之间水相的联通,其中:A multi-stage heterogeneous three-dimensional electrochemical reaction device for wastewater treatment, characterized in that the device includes: a body, an external power supply and an external gas generator, the front end of the body is provided with a water inlet, and the end is provided with a water outlet, and at least Two-stage reactors are set up, and the reactors of each stage are connected in series and the water phase communication between the adjacent reactors is realized through the overflow port, wherein:
每段反应器被中间隔板分隔为至少两个反应室,并通过下端的布气排渣室实现反应室间水相的联通;每个反应室至少设置两块垂直平行排列的电极板,各反应室电极板正极和负极交替设置,并联连接外置电源;电极板之间填充粒子电极,粒子电极置于带有筛孔的筐中或堆置于反应室底部的孔板上;布气排渣室内设有曝气板、管或盘,通过气体管道连接外置气体发生器,每段反应器下端设有排空口。Each section of the reactor is divided into at least two reaction chambers by the middle partition, and the water phase communication between the reaction chambers is realized through the gas distribution and slag discharge chamber at the lower end; each reaction chamber is equipped with at least two vertically parallel electrode plates, each The positive and negative poles of the electrode plates in the reaction chamber are arranged alternately, and are connected in parallel to an external power supply; particle electrodes are filled between the electrode plates, and the particle electrodes are placed in a basket with sieve holes or stacked on the orifice plate at the bottom of the reaction chamber; The slag chamber is equipped with an aeration plate, tube or plate, and is connected to an external gas generator through a gas pipeline, and the lower end of each section of the reactor is provided with an emptying port.
所述电极板为掺硼金刚石薄膜极板(BDD)、钛基过渡金属氧化物涂层电极(DSA)、不锈钢极板、石墨极板或合金极板中的一种。优选的,阳极采用掺硼金刚石薄膜电极(BDD)、钛基过渡金属氧化物涂层电极(DSA)中的一种;阴极采用不锈钢电极、石墨电极中的一种。The electrode plate is one of a boron-doped diamond film plate (BDD), a titanium-based transition metal oxide coating electrode (DSA), a stainless steel plate, a graphite plate or an alloy plate. Preferably, the anode is one of boron-doped diamond film electrode (BDD) and titanium-based transition metal oxide coating electrode (DSA); the cathode is one of stainless steel electrode and graphite electrode.
所述粒子电极以颗粒为基体,其上负载有用于异相催化污染物降解和去除的催化剂;所述基体为颗粒活性炭、三氧化二铝颗粒或沸石颗粒,单独使用或者两种或数种混合使用;催化剂为二氧化钛、金属或过渡金属氧化物一种或数种混合。优选的,粒子电极采用活性炭颗粒或活性炭颗粒掺杂三氧化二铝颗粒为基体,基体负载纳米二氧化钛、锰氧化物、铜氧化物、铁氧化物、钌氧化物、钯氧化物、钴氧化物、银氧化物、铈氧化物、钛氧化物、锌氧化物等的一种或几种为粒子电极。The particle electrode is based on particles, on which are loaded catalysts for the degradation and removal of pollutants in heterogeneous catalysis; the substrate is granular activated carbon, aluminum oxide particles or zeolite particles, used alone or in combination of two or more Use; The catalyst is one or more mixtures of titanium dioxide, metal or transition metal oxides. Preferably, the particle electrode uses activated carbon particles or activated carbon particles doped with aluminum oxide particles as the matrix, and the matrix supports nano-titanium dioxide, manganese oxide, copper oxide, iron oxide, ruthenium oxide, palladium oxide, cobalt oxide, One or more of silver oxide, cerium oxide, titanium oxide, zinc oxide, etc. are particle electrodes.
所述填料筐为数个水平或垂直串接。The stuffing baskets are connected in series horizontally or vertically.
所述外置电源设置为一台或数台,每段反应器设置一台或数段反应器共用一台。The external power supply is set to one or several sets, and each section of reactor is provided with one or several sections of reactors share one.
所述布气排渣室为倒锥体或矩形体结构,优选的,设计为长方体结构,布气排渣室底部设置一定倾斜角度,有利于泥渣的排放和污水的排空。所述布气排渣室内设有曝气板、管或盘;曝气板、管或盘通过气体管道连接外置气体发生器;The air distribution and slagging chamber is an inverted cone or rectangular structure. Preferably, it is designed as a cuboid structure. The bottom of the air distribution and slagging chamber is provided with a certain inclination angle, which is conducive to the discharge of sludge and sewage. The air distribution and slag discharge chamber is equipped with an aeration plate, tube or plate; the aeration plate, tube or plate is connected to an external gas generator through a gas pipeline;
所述外置气体发生器为空气压缩机或臭氧发生器。优选的,通过气体管道连接外置的空气压缩机或臭氧发生器,向反应器内提供压缩空气或臭氧。The external gas generator is an air compressor or an ozone generator. Preferably, an external air compressor or an ozone generator is connected through a gas pipeline to provide compressed air or ozone into the reactor.
所述排空口用于泥渣的清理及污水的排空。The emptying port is used for cleaning mud and slag and emptying sewage.
本发明用于B/C小于0.3的难降解有机废水的降解,废水在进入本发明装置前需要进行预处理,预处理一般采用混凝沉淀技术去除废水中的悬浮物、胶体杂质及钙、镁、磷、金属离子等,减少这些干扰因子对催化剂的毒害作用。The present invention is used for the degradation of refractory organic waste water with B/C less than 0.3. The waste water needs to be pretreated before entering the device of the present invention. Coagulation sedimentation technology is generally used for pretreatment to remove suspended solids, colloidal impurities and calcium and magnesium in the waste water. , phosphorus, metal ions, etc., to reduce the poisonous effect of these interfering factors on the catalyst.
本发明的多段异相三维电化学处理是将催化污染物降解的催化剂负载在粒子电极上,在电场能量推动下,异相催化降解水相中的污染物,以直接和间接氧化还原作用,对污水中结构复杂的有机分子实施无选择性的氧化分解或还原改性,开环断键,提高B/C,同时大幅度去除COD,降解有机胺及氨氮。The multi-stage heterogeneous three-dimensional electrochemical treatment of the present invention is to load the catalyst that catalyzes the degradation of pollutants on the particle electrode, and under the promotion of electric field energy, the pollutants in the water phase are degraded by heterogeneous catalysis, and the direct and indirect redox effects are used to Organic molecules with complex structures in sewage are non-selectively oxidatively decomposed or reductively modified to open rings and break bonds, improve B/C, and at the same time greatly remove COD and degrade organic amines and ammonia nitrogen.
本发明的有益效果Beneficial effects of the present invention
1)本发明用于处理难降解有机废水,具有以下优势:1) The present invention is used to treat refractory organic wastewater and has the following advantages:
a抗冲击负荷能力强,处理效果稳定,出水水质优良;a Strong impact load resistance, stable treatment effect, excellent water quality;
b管理方便,模块化反应装置,成套技术,并精确控制,从而保证处理工艺的稳定运行;b Convenient management, modular reaction device, complete set of technology, and precise control, so as to ensure the stable operation of the treatment process;
c结构紧凑、运行费用低。c Compact structure, low operating costs.
3)本发明装置可实现对难降解有机废水的高效处理,保护生态环境,为难降解有机废水的治理解决了关键性技术难题。3) The device of the present invention can realize efficient treatment of refractory organic wastewater, protect the ecological environment, and solve key technical problems for the treatment of refractory organic wastewater.
附图说明Description of drawings
图1为本发明结构示意图;Fig. 1 is a structural representation of the present invention;
图2为本发明实施例2结构示意图;Fig. 2 is the structural representation of embodiment 2 of the present invention;
图3为本发明实施例3结构示意图;Fig. 3 is a schematic structural diagram of Embodiment 3 of the present invention;
图4为本发明实施例4结构示意图。Fig. 4 is a schematic structural diagram of Embodiment 4 of the present invention.
具体实施方式detailed description
以下结合说明书附图和具体实施例对本发明作进一步描述,但并不因此而限制本发明的保护范围。The present invention will be further described below in conjunction with the accompanying drawings and specific embodiments, but the protection scope of the present invention is not limited thereby.
参阅图1,本发明包括由多段(≥2段)反应器串联组成的本体1,邻段反应器之间实现水相联通的溢流口2,分隔反应器的中间隔板3,被中间隔板分隔的反应室4,反应器下端的布气排渣室5,设置在反应室的两块或以上垂直平行排列的电极板6,外置电源7,填充于电极板之间的粒子电极8,用于堆置粒子电极的底部孔板10,布气排渣室内设置的曝气板、管或盘11,气体管道12及气体发生器13,反应器下端的排空口14,反应装置的进水口15,出水口16。Referring to Figure 1, the present invention includes a body 1 composed of multiple (≥ 2) reactors connected in series, an overflow port 2 that realizes water phase communication between adjacent reactors, and an intermediate partition 3 that separates the reactors. Plate-separated reaction chamber 4, gas distribution and slag discharge chamber 5 at the lower end of the reactor, two or more electrode plates 6 arranged vertically and parallelly in the reaction chamber, external power supply 7, and particle electrodes 8 filled between the electrode plates , the bottom orifice plate 10 for stacking particle electrodes, the aeration plate, tube or disc 11 arranged in the air distribution and slagging chamber, the gas pipeline 12 and the gas generator 13, the emptying port 14 at the lower end of the reactor, and the Water inlet 15, water outlet 16.
实施例1Example 1
参阅图1,本实施例设为依次串联四段反应器,各段反应器之间通过溢流口2实现水流的联通。中间隔板3将每段反应器分隔为均等体积的两个反应室4,反应室4之间通过反应室4下端布气排渣室5相连通,布气排渣室5设计为倒锥体结构。每个反应室设置两块垂直平行排列的电极板6,电极板6并联连接外置电源7。阳极电极板采用钛基钌铱电极,阴极采用纯钛基电极。电极板之间填充的粒子电极8采用颗粒活性炭基体负载纳米级二氧化钛,粒子电极8放置于反应室4底部设置的多孔筛板10上。布气排渣室5内设置曝气板11,通过气体管道12连接外置的空气压缩机13,向反应器内提供压缩空气。反应器下端设置排空口14,用于泥渣的清理及污水的排空。反应装置前端设置进水口15,后端设置出水口16。Referring to FIG. 1 , in this embodiment, four stages of reactors are connected in series in sequence, and the flow of water between each stage of reactors is realized through an overflow port 2 . The middle partition 3 divides each section of the reactor into two reaction chambers 4 of equal volume. The reaction chambers 4 are connected through the air distribution and slagging chamber 5 at the lower end of the reaction chamber 4. The air distribution and slagging chamber 5 is designed as an inverted cone structure. Each reaction chamber is provided with two vertical and parallel electrode plates 6, and the electrode plates 6 are connected to an external power supply 7 in parallel. The anode electrode plate uses a titanium-based ruthenium-iridium electrode, and the cathode uses a pure titanium-based electrode. The particle electrode 8 filled between the electrode plates adopts granular activated carbon matrix to support nano-scale titanium dioxide, and the particle electrode 8 is placed on the porous sieve plate 10 provided at the bottom of the reaction chamber 4 . An aeration plate 11 is installed in the air distribution and slag discharge chamber 5, and an external air compressor 13 is connected through a gas pipeline 12 to provide compressed air to the reactor. The lower end of the reactor is provided with an emptying port 14 for cleaning sludge and emptying sewage. A water inlet 15 is arranged at the front end of the reaction device, and a water outlet 16 is arranged at the rear end.
本实施例是这样工作的:This example works like this:
多段异相三维电化学反应装置用于处理高浓度难降解(B/C小于0.3)有机废水,异相催化广谱降解有机污染物,氧化分解或还原改性,开环断键,提高B/C,同时大幅度去除COD,降解有机胺及氨氮。在污水进入多段异相三维电化学反应装置前需要进行前处理,二维电化学混凝或传统化学混凝,去除废水中的悬浮物、胶体杂质及钙、镁、磷、金属离子等,同时去除一定的COD。反应装置先安装好电极板,接线,连接电源,反应器内加装粒子电极,接通电源,将经过前处理的废水由进水口15进入多段异相三维电化学反应装置,废水进入第一反应室,经过下部多孔筛板10和布气排渣室5进入第二反应室,再由第二反应室和第三反应室上端的溢流口进入第三反应室,以此类推,废水在流经各个反应室时,部分污染物质吸附在主电极表面和粒子电极表面,在电场能量推动下,这些污染物在阴阳电极表面和众多粒子电极表面进行直接氧化作用和还原作用。同时,经过曝气溶解的氧气、阳极及粒子电极阳极端产生的氧气,在阴极和粒子电极阴极端还原生成氧化性极强的双氧水和羟基自由基,同时又在体系内电磁场及氧化还原电子对催化作用下,产生大量氧化性极强的自由基,HO2 -·,O·,H·,O2 -·, O3 -·等。这些自由基与废水中有机物反应,生成不稳定的有机物自由基R·等,从而引发大量的自由基链式反应。废水在流经各个反应室时,在电极表面直接作用和自由基链式反应的间接作用下,其中的难降解有机物逐步被降解,从大分子有机物逐步断键开环降解为小分子有机物,部分有机物被彻底氧化分解为CO2和H2O。最终出水从出水口16进入后续的处理或进入出水池。The multi-stage heterogeneous three-dimensional electrochemical reaction device is used to treat high-concentration refractory (B/C less than 0.3) organic wastewater, heterogeneously catalyze broad-spectrum degradation of organic pollutants, oxidative decomposition or reduction modification, ring-opening and bond breaking, and increase B/C C. At the same time, COD is greatly removed, and organic amines and ammonia nitrogen are degraded. Before the sewage enters the multi-stage heterogeneous three-dimensional electrochemical reaction device, pretreatment is required, two-dimensional electrochemical coagulation or traditional chemical coagulation, to remove suspended solids, colloidal impurities, calcium, magnesium, phosphorus, metal ions, etc. in the wastewater, and at the same time Remove certain COD. The reaction device first installs the electrode plate, connects the wires, connects the power supply, installs the particle electrode in the reactor, connects the power supply, and passes the pre-treated wastewater into the multi-stage heterogeneous three-dimensional electrochemical reaction device through the water inlet 15, and the wastewater enters the first reaction chamber, enters the second reaction chamber through the lower perforated sieve plate 10 and the air distribution and slag discharge chamber 5, and then enters the third reaction chamber through the overflow port at the upper end of the second reaction chamber and the third reaction chamber, and so on, the waste water flows through In each reaction chamber, some pollutants are adsorbed on the surface of the main electrode and the surface of the particle electrode. Driven by the energy of the electric field, these pollutants undergo direct oxidation and reduction on the surface of the cathode and anode electrodes and the surfaces of many particle electrodes. At the same time, the oxygen dissolved by aeration, the anode and the oxygen produced at the anode of the particle electrode are reduced at the cathode and the cathode of the particle electrode to generate highly oxidizing hydrogen peroxide and hydroxyl radicals. At the same time, the electromagnetic field and redox electron pairs in the system Under the action of catalysis, a large number of highly oxidizing free radicals are produced, such as HO 2 - ·, O·, H·, O 2 - ·, O 3 - ·, etc. These free radicals react with organic matter in wastewater to generate unstable organic free radicals R·, etc., thereby triggering a large number of free radical chain reactions. When the wastewater flows through each reaction chamber, under the direct action of the electrode surface and the indirect action of the free radical chain reaction, the refractory organic matter in it is gradually degraded, and the macromolecular organic matter is gradually broken and ring-opened to degrade into small molecular organic matter. Organic matter is completely oxidized and decomposed into CO 2 and H 2 O. Finally, the effluent enters the subsequent treatment or enters the effluent pool from the water outlet 16 .
以某化学控股股份有限公司吡啶类杀虫剂生产废水处理为例,该废水为高有机物含量、高盐、难降解的有机废水,经过混凝处理后的水质指标为:CODcr 19110 mg/L,BOD1146 mg/L,NH3-N 38.5 mg/L,Cl- 8879 mg/L。经过混凝处理后的吡啶类杀虫剂生产废水由进水口15进入实施例1的多段异相三维电化学反应装置,出水从出水口16流出反应装置。连续进出水,水力停留时间160min,电压强度0.5V/cm,连续运行10d后,出水指标为:CODcr3862 mg/L,BOD 686 mg/L,NH3-N 15 mg/L,Cl- 1624 mg/L。BOD5/COD由0.06提高至0.18,可生化性明显提高。出水放置14天后在显微镜下观察到活跃的微生物和原生动物(以纤毛虫类为主)。出水可调节负荷进入后续的生物处理装置以及后续的脱盐装置。Take the treatment of pyridine insecticide production wastewater in a chemical holding company as an example. The wastewater is organic wastewater with high organic content, high salt, and refractory degradation. The water quality index after coagulation treatment is: CODcr 19110 mg/L, BOD1146 mg/L, NH 3 -N 38.5 mg/L, Cl - 8879 mg/L. After the coagulation treatment, the pyridine insecticide production wastewater enters the multi-stage heterogeneous three-dimensional electrochemical reaction device of the embodiment 1 through the water inlet 15 , and the effluent flows out of the reaction device through the water outlet 16 . Continuous water inflow and outflow, hydraulic retention time 160min, voltage intensity 0.5V/cm, after 10 days of continuous operation, the effluent indicators are: CODcr3862 mg/L, BOD 686 mg/L, NH 3 -N 15 mg/L, Cl - 1624 mg/L L. BOD 5 /COD increased from 0.06 to 0.18, and the biodegradability was obviously improved. Active microorganisms and protozoa (mainly ciliates) were observed under the microscope after being left in the water for 14 days. The effluent can adjust the load to enter the subsequent biological treatment unit and the subsequent desalination unit.
实施例2Example 2
参阅图2,本实施例设为依次串联四段反应器,各段反应器之间通过溢流口2实现水流的联通。中间隔板3将每段反应器分隔为均等体积的两个反应室4,反应室4之间通过反应室4下端布气排渣室5相连通,布气排渣室5设计为倒锥体结构。每个反应室设置两块垂直平行排列的电极板6,电极板6并联连接外置电源7。反应器阳极电极板采用掺硼金刚石薄膜极板(BDD),阴极采用不锈钢电极。粒子电极8采用颗粒活性炭基体负载锰氧化物、铜氧化物和铁氧化物,粒子电极8填充于带有筛孔的填料筐9中,反应室4中多个填料筐9水平或垂直串接。布气排渣室5内设置曝气板11,通过气体管道12连接外置的空气压缩机13,向反应器内提供压缩空气。反应器下端设置排空口14,用于泥渣的清理及污水的排空。反应装置前端设置进水口15,后端设置出水口16。本实施例工作过程同实施例1。Referring to FIG. 2 , in this embodiment, four stages of reactors are set in series in series, and the flow of water between each stage of reactors is realized through the overflow port 2 . The middle partition 3 divides each section of the reactor into two reaction chambers 4 of equal volume. The reaction chambers 4 are connected through the air distribution and slagging chamber 5 at the lower end of the reaction chamber 4. The air distribution and slagging chamber 5 is designed as an inverted cone structure. Each reaction chamber is provided with two vertical and parallel electrode plates 6, and the electrode plates 6 are connected to an external power supply 7 in parallel. The anode electrode plate of the reactor is made of boron-doped diamond film plate (BDD), and the cathode is made of stainless steel electrode. The particle electrode 8 adopts the granular activated carbon matrix to support manganese oxide, copper oxide and iron oxide. The particle electrode 8 is filled in the packing basket 9 with sieve holes, and multiple packing baskets 9 in the reaction chamber 4 are connected in series horizontally or vertically. An aeration plate 11 is installed in the air distribution and slag discharge chamber 5, and an external air compressor 13 is connected through a gas pipeline 12 to provide compressed air to the reactor. The lower end of the reactor is provided with an emptying port 14 for cleaning sludge and emptying sewage. A water inlet 15 is arranged at the front end of the reaction device, and a water outlet 16 is arranged at the rear end. The working process of this embodiment is the same as that of Embodiment 1.
以河北某化工集团碳脂类(丁二酸二甲脂;丁二酸二异丙脂;丁二酰丁二酸二甲脂等)生产废水为例,经过混凝处理后的水质指标为:CODcr 63252 mg/L,BOD 0 mg/L,Cl-135 mg/L。经过混凝处理后的碳脂类生产废水由进水口15进入实施例2的多段异相三维电化学反应装置,出水从出水口16流出反应装置。连续进出水,水力停留时间200min,电压强度1.0V/cm,连续运行8d后,出水指标为:CODcr 6847 mg/L,BOD 1621 mg/L,Cl- 19 mg/L。BOD5/COD由0提高至0.24,可生化性明显提高。出水可调节负荷进入后续的生物处理装置以及后续的脱盐装置。Taking carbon lipids (dimethyl succinate; diisopropyl succinate; dimethyl succinate, etc.) production wastewater from a chemical group in Hebei as an example, the water quality index after coagulation treatment is: CODcr 63252 mg/L, BOD 0 mg/L, Cl - 135 mg/L. After the coagulation treatment, the carbon lipid production wastewater enters the multi-stage heterogeneous three-dimensional electrochemical reaction device of the embodiment 2 through the water inlet 15 , and the effluent flows out of the reaction device through the water outlet 16 . Continuous water inflow and outflow, hydraulic retention time 200min, voltage intensity 1.0V/cm, after 8 days of continuous operation, the effluent indicators are: CODcr 6847 mg/L, BOD 1621 mg/L, Cl - 19 mg/L. BOD 5 /COD increased from 0 to 0.24, and the biodegradability was obviously improved. The effluent can adjust the load to enter the subsequent biological treatment unit and the subsequent desalination unit.
实施例3Example 3
参阅图3,本实施例设为依次串联四段反应器,各段反应器之间通过溢流口2实现水流的联通。中间隔板3将每段反应器分隔为均等体积的两个反应室4,反应室4之间通过反应室4下端布气排渣室5相连通,布气排渣室5设计为长方体结构。每个反应室设置两块垂直平行排列的电极板6,电极板6并联连接外置电源7。反应器阳极电极板采用钛基钌铱电极,阴极采用石墨电极。粒子电极8采用颗粒活性炭基体负载锰氧化物、铜氧化物、铁氧化物,粒子电极8填充于带有筛孔的填料筐9中,反应室4中多个填料筐9水平或垂直串接。布气排渣室5内设置曝气板11,通过气体管道12连接外置的臭氧发生器13,向反应器内提供压缩臭氧。反应器下端设置排空口14,用于泥渣的清理及污水的排空。反应装置前端设置进水口15,后端设置出水口16。本实施例工作过程同实施例1。Referring to FIG. 3 , in this embodiment, four reactors are connected in series in sequence, and the water flow is connected through the overflow port 2 between each reactor. The middle partition 3 divides each section of the reactor into two reaction chambers 4 of equal volume. The reaction chambers 4 are connected through the air distribution and slagging chamber 5 at the lower end of the reaction chamber 4. The air distribution and slagging chamber 5 is designed as a cuboid structure. Each reaction chamber is provided with two vertical and parallel electrode plates 6, and the electrode plates 6 are connected to an external power supply 7 in parallel. The anode electrode plate of the reactor adopts titanium-based ruthenium iridium electrode, and the cathode adopts graphite electrode. The particle electrode 8 uses a granular activated carbon matrix to load manganese oxide, copper oxide, and iron oxide. The particle electrode 8 is filled in a packing basket 9 with sieve holes, and multiple packing baskets 9 in the reaction chamber 4 are connected in series horizontally or vertically. An aeration plate 11 is installed in the air distribution and slag discharge chamber 5, and an external ozone generator 13 is connected through a gas pipeline 12 to provide compressed ozone into the reactor. The lower end of the reactor is provided with an emptying port 14 for cleaning sludge and emptying sewage. A water inlet 15 is arranged at the front end of the reaction device, and a water outlet 16 is arranged at the rear end. The working process of this embodiment is the same as that of Embodiment 1.
以三乙胺废水处理为例。分子筛合成晶化母液废水含有各类有机胺,其中有代表性的是三乙胺盐酸盐。此类废水是典型的高浓度、高盐度和难生物降解的废水。由于缺乏有效的处理手段,目前这类废水主要是进行高温焚烧,处理成本高昂,难以维持。本实施例中,经过混凝前处理后的三乙胺废水的水质指标为:CODcr 46131 mg/L,BOD 545 mg/L,三乙胺浓度28172 mg/L, Cl-14605 mg/L。经过混凝处理后的三乙胺废水由进水口15进入实施例3的多段异相三维电化学反应装置,出水从出水口16流出反应装置。连续进出水,水力停留时间200min,电压强度0.8V/cm,连续运行15d后,出水指标为:CODcr 8863 mg/L,BOD1265 mg/L,三乙胺6402 mg/L,Cl-3934mg/L,COD 去除率81%,三乙胺去除率77%,Cl-去除率73%,B/C由0.012提高至0.14。出水经过调整负荷后可进入后续的生物处理装置以及后续的脱盐装置。Take triethylamine wastewater treatment as an example. Molecular sieve synthetic crystallization mother liquid wastewater contains various organic amines, the representative of which is triethylamine hydrochloride. This kind of wastewater is typical wastewater with high concentration, high salinity and difficult biodegradation. Due to the lack of effective treatment means, this kind of wastewater is mainly incinerated at high temperature at present, and the treatment cost is high and it is difficult to maintain. In this example, the water quality indicators of triethylamine wastewater after pre-coagulation treatment are: CODcr 46131 mg/L, BOD 545 mg/L, triethylamine concentration 28172 mg/L, Cl - 14605 mg/L. The coagulated triethylamine waste water enters the multi-stage heterogeneous three-dimensional electrochemical reaction device of embodiment 3 through the water inlet 15 , and the effluent flows out of the reaction device through the water outlet 16 . Continuous water inflow and outflow, hydraulic retention time 200min, voltage intensity 0.8V/cm, after 15 days of continuous operation, the effluent indicators are: CODcr 8863 mg/L, BOD1265 mg/L, triethylamine 6402 mg/L, Cl - 3934mg/L, The removal rate of COD was 81%, the removal rate of triethylamine was 77%, the removal rate of Cl - was 73%, and the B/C increased from 0.012 to 0.14. After the load is adjusted, the effluent can enter the subsequent biological treatment unit and the subsequent desalination unit.
实施例4Example 4
参阅图4,本实施例设为依次串联四段反应器,各段反应器之间通过溢流口2实现水流的联通。中间隔板3将每段反应器分隔为均等体积的两个反应室4,反应室4之间通过反应室4下端布气排渣室5相连通,布气排渣室5设计为长方体结构。每个反应室设置两块垂直平行排列的电极板6,电极板6并联连接外置电源7。反应器阳极电极板采用不锈钢,阴极采用不锈钢电极。粒子电极8采用颗粒h基体活性炭颗粒负载铜氧化物和铁氧化物,粒子电极8放置于反应室4底部设置的多孔筛板10上。布气排渣室5内设置曝气板11,通过气体管道12连接外置的臭氧发生器13,向反应器内提供压缩臭氧。反应器下端设置排空口14,用于泥渣的清理及污水的排空。反应装置前端设置进水口15,后端设置出水口16。本实施例工作过程同实施例1。Referring to FIG. 4 , in this embodiment, four stages of reactors are set in series in series, and the flow of water between each stage of reactors is realized through the overflow port 2 . The middle partition 3 divides each section of the reactor into two reaction chambers 4 of equal volume. The reaction chambers 4 are connected through the air distribution and slagging chamber 5 at the lower end of the reaction chamber 4. The air distribution and slagging chamber 5 is designed as a cuboid structure. Each reaction chamber is provided with two vertical and parallel electrode plates 6, and the electrode plates 6 are connected to an external power supply 7 in parallel. The anode electrode plate of the reactor is made of stainless steel, and the cathode is made of stainless steel electrode. The particle electrode 8 adopts particles h matrix activated carbon particles to load copper oxide and iron oxide, and the particle electrode 8 is placed on the porous sieve plate 10 provided at the bottom of the reaction chamber 4 . An aeration plate 11 is installed in the air distribution and slag discharge chamber 5, and an external ozone generator 13 is connected through a gas pipeline 12 to provide compressed ozone into the reactor. The lower end of the reactor is provided with an emptying port 14 for cleaning sludge and emptying sewage. A water inlet 15 is arranged at the front end of the reaction device, and a water outlet 16 is arranged at the rear end. The working process of this embodiment is the same as that of Embodiment 1.
以山东某己内酰胺生产废水处理为例,经过混凝处理后的水质指标为:CODcr8560mg/L,BOD 220 mg/L,Cl- 7849 mg/L,NH3-N 7957 mg/L。经过混凝处理后的废水由进水口15进入实施例4的多段异相三维电化学反应装置,出水从出水口16流出反应装置。连续进出水,水力停留时间240min,电压强度0.33V/cm,连续运行10d后,出水指标为:CODcr 1504mg/L,BOD 431 mg/L,Cl- 863 mg/L,NH3-N 130 mg/L。BOD5/COD由0.03提高至0.29,可生化性明显提高。出水可调节负荷进入后续的生物处理装置以及后续的脱盐装置。Taking a caprolactam production wastewater treatment in Shandong as an example, the water quality indicators after coagulation treatment are: CODcr8560mg/L, BOD 220 mg/L, Cl - 7849 mg/L, NH 3 -N 7957 mg/L. The coagulated waste water enters the multi-stage heterogeneous three-dimensional electrochemical reaction device of Embodiment 4 through the water inlet 15 , and the effluent flows out of the reaction device through the water outlet 16 . Continuous water inflow and outflow, hydraulic retention time 240min, voltage intensity 0.33V/cm, after 10 days of continuous operation, the effluent indicators are: CODcr 1504mg/L, BOD 431 mg/L, Cl - 863 mg/L, NH 3 -N 130 mg/L L. BOD 5 /COD increased from 0.03 to 0.29, and the biodegradability was obviously improved. The effluent can adjust the load to enter the subsequent biological treatment unit and the subsequent desalination unit.
以上所述仅仅是本发明的优选实施方式,本发明的保护范围并不仅局限于上述实施例。凡是属于本发明思路下的技术方案均属于本发明的保护范围。应该指出,对于本技术领域的普通技术人员来说,在不脱离本发明原理的前体下的改进和润饰,这些改进和润饰也应视为本发明的保护范围。The above descriptions are only preferred implementations of the present invention, and the scope of protection of the present invention is not limited to the above examples. All technical solutions under the idea of the present invention belong to the protection scope of the present invention. It should be pointed out that for those skilled in the art, improvements and modifications without departing from the principle of the present invention should also be regarded as the protection scope of the present invention.
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Cited By (9)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN108502988A (en) * | 2018-04-24 | 2018-09-07 | 浙江奇彩环境科技股份有限公司 | A kind of electrolytic method for improving treatment of Organic Wastewater effect |
CN108558084A (en) * | 2018-06-13 | 2018-09-21 | 江苏湖大化工科技有限公司 | The processing method and processing device of organic matter electrolytic catalysis coupling advanced oxidation in a kind of high-salt wastewater |
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Citations (8)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN101028944A (en) * | 2007-01-12 | 2007-09-05 | 华南理工大学 | Composite electrolytic bath and method for electrolyzing and decoloring pulp-making effluent |
CN101423269A (en) * | 2008-11-14 | 2009-05-06 | 浙江大学 | Method and apparatus for treating electroplating waste water |
CN201390683Y (en) * | 2009-04-17 | 2010-01-27 | 湖州森蓝环境工程有限公司 | Multistage electrolysis device for treating cyanide containing wastewater |
CN103408106A (en) * | 2013-08-22 | 2013-11-27 | 吉林大学 | Overturning flow-type electrochemical reactor |
CN103466758A (en) * | 2013-09-24 | 2013-12-25 | 杨作红 | Composite cathode and electrochemical multiple-stage water treatment equipment utilizing same |
CN204529408U (en) * | 2015-03-25 | 2015-08-05 | 西安石油大学 | For the treatment of the Electrochemical oxidation device of oil field polymer-containing wastewater |
CN206417892U (en) * | 2017-01-13 | 2017-08-18 | 丽中环境工程科技(上海)有限公司 | Catalytic electrochemical wastewater treatment equipment |
CN207861965U (en) * | 2017-09-19 | 2018-09-14 | 华东师范大学 | A kind of multistage out-phase three-dimensional electrochemical reaction unit for waste water treatment |
-
2017
- 2017-09-19 CN CN201710846679.XA patent/CN107522267A/en active Pending
Patent Citations (8)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN101028944A (en) * | 2007-01-12 | 2007-09-05 | 华南理工大学 | Composite electrolytic bath and method for electrolyzing and decoloring pulp-making effluent |
CN101423269A (en) * | 2008-11-14 | 2009-05-06 | 浙江大学 | Method and apparatus for treating electroplating waste water |
CN201390683Y (en) * | 2009-04-17 | 2010-01-27 | 湖州森蓝环境工程有限公司 | Multistage electrolysis device for treating cyanide containing wastewater |
CN103408106A (en) * | 2013-08-22 | 2013-11-27 | 吉林大学 | Overturning flow-type electrochemical reactor |
CN103466758A (en) * | 2013-09-24 | 2013-12-25 | 杨作红 | Composite cathode and electrochemical multiple-stage water treatment equipment utilizing same |
CN204529408U (en) * | 2015-03-25 | 2015-08-05 | 西安石油大学 | For the treatment of the Electrochemical oxidation device of oil field polymer-containing wastewater |
CN206417892U (en) * | 2017-01-13 | 2017-08-18 | 丽中环境工程科技(上海)有限公司 | Catalytic electrochemical wastewater treatment equipment |
CN207861965U (en) * | 2017-09-19 | 2018-09-14 | 华东师范大学 | A kind of multistage out-phase three-dimensional electrochemical reaction unit for waste water treatment |
Cited By (12)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN108502988A (en) * | 2018-04-24 | 2018-09-07 | 浙江奇彩环境科技股份有限公司 | A kind of electrolytic method for improving treatment of Organic Wastewater effect |
CN108558084A (en) * | 2018-06-13 | 2018-09-21 | 江苏湖大化工科技有限公司 | The processing method and processing device of organic matter electrolytic catalysis coupling advanced oxidation in a kind of high-salt wastewater |
CN108558084B (en) * | 2018-06-13 | 2024-01-23 | 江苏湖大化工科技有限公司 | Treatment method and device for electrolytic catalysis coupling advanced oxidation of organic matters in high-salt wastewater |
CN109650496A (en) * | 2019-01-28 | 2019-04-19 | 江苏融汇环境工程有限公司 | The method of electrocatalytic oxidation processing rubber and plastic waste water |
CN110204013A (en) * | 2019-06-10 | 2019-09-06 | 宁波瑞岩环保科技有限公司 | A kind of Modular electrical catalysis oxidation sewage disposal system |
CN110204013B (en) * | 2019-06-10 | 2024-12-27 | 宁波瑞岩环保科技有限公司 | A modular electrocatalytic oxidation wastewater treatment system |
CN110627267A (en) * | 2019-09-24 | 2019-12-31 | 利民化学有限责任公司 | System and method for degrading biotoxicity in wastewater |
CN112723657A (en) * | 2020-12-11 | 2021-04-30 | 湖南军信环保股份有限公司 | Device and method for treating aged landfill leachate and membrane filtration concentrated solution thereof |
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CN113896294B (en) * | 2021-11-08 | 2022-11-11 | 中机国际工程设计研究院有限责任公司 | Vertical baffling type electro-catalytic reaction device |
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