CN107619159A - A kind of method and application system of pollution administration water quality - Google Patents
A kind of method and application system of pollution administration water quality Download PDFInfo
- Publication number
- CN107619159A CN107619159A CN201711084640.5A CN201711084640A CN107619159A CN 107619159 A CN107619159 A CN 107619159A CN 201711084640 A CN201711084640 A CN 201711084640A CN 107619159 A CN107619159 A CN 107619159A
- Authority
- CN
- China
- Prior art keywords
- water
- pond
- sewage
- electron
- connection
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Pending
Links
Landscapes
- Treatment Of Water By Oxidation Or Reduction (AREA)
Abstract
Description
技术领域technical field
本发明涉及一种治理污染水质的方法及应用系统,属环保行业。The invention relates to a method and an application system for controlling polluted water quality, belonging to the environmental protection industry.
背景技术Background technique
城市排污、村镇生活污水排入河道、过度使用化肥以及各种工厂的排污,水资源现状恶化,导致河流和湖泊污染,藻类死亡,使原生态的生物链断裂。自然环境生物链失去平衡后,大量细菌过度繁殖,在分解有机质时,硫化氢等恶臭气体溢出,挥发到空气中,影响周边环境。污水处理厂在处理污水的过程中,常规的生化工艺也有恶臭气体排出,需要进行废气处理,增加了处理成本,浪费资源。Urban sewage, domestic sewage from villages and towns are discharged into rivers, excessive use of chemical fertilizers, and sewage from various factories degrade the status quo of water resources, leading to pollution of rivers and lakes, death of algae, and disruption of the original ecological chain. When the biological chain of the natural environment is out of balance, a large number of bacteria multiply excessively. When decomposing organic matter, malodorous gases such as hydrogen sulfide overflow and volatilize into the air, affecting the surrounding environment. In the process of sewage treatment in the sewage treatment plant, the conventional biochemical process also emits odorous gas, which requires waste gas treatment, which increases the treatment cost and wastes resources.
为解决河流、河道、湖泊的污染问题,为解决污水处理厂恶臭气体的问题,本申请研发了一种治理污染水质的方法及应用系统。In order to solve the pollution problems of rivers, river courses and lakes, and to solve the problem of malodorous gas in sewage treatment plants, this application has developed a method and application system for controlling polluted water quality.
发明内容Contents of the invention
本发明目的在于克服现有技术存在的缺陷,利用核外电子剥离技术并结合生态链而提供一种治理污染水质的方法及应用系统。The purpose of the present invention is to overcome the defects of the prior art, and provide a method and application system for controlling polluted water quality by using the extranuclear electron stripping technology and combining the ecological chain.
本发明由以下技术方案实现:The present invention is realized by the following technical solutions:
一种治理污染水质的方法,包括下列步骤:A method for controlling polluted water, comprising the following steps:
(1)污水排入调节池内,均衡调节水质,使各种污染指标均衡;(1) Sewage is discharged into the adjustment pool to balance the water quality and balance various pollution indicators;
(2)采用核外电子剥离技术,将空气分子电离裂解以及核外电子剥离,产生羟基自由基、臭氧、自由电子;(2) Using extranuclear electron stripping technology to ionize and crack air molecules and strip extranuclear electrons to produce hydroxyl radicals, ozone, and free electrons;
(3)将上述产生的含有臭氧、羟基自由基、自由电子的混合气体输入至装有污水的曝气池内,臭氧和羟基自由基将污水内所含有的有机物质氧化还原,并且破解大分子链,使其成为小分子结构,自由电子补偿重金属离子及其他离子状态的物质缺失的核外电子,使水体内所含有的化学性能不稳定的有害物质失去原有的化学性能,成为稳定状态;(3) Input the above-mentioned mixed gas containing ozone, hydroxyl radicals and free electrons into the aeration tank filled with sewage. Ozone and hydroxyl radicals will oxidize and reduce the organic substances contained in the sewage and break the macromolecular chains. , so that it becomes a small molecular structure, free electrons compensate for the missing extranuclear electrons of heavy metal ions and other ionic substances, so that the harmful substances with unstable chemical properties contained in the water body lose their original chemical properties and become a stable state;
(4)将上述经过处理之后的污水排入含有浮游生物的水池中,利用浮游生物吸收水体中所含的有机无机物质,降解转化水中污染物;(4) Discharge the above-mentioned treated sewage into the pool containing plankton, use the plankton to absorb the organic and inorganic substances contained in the water body, and degrade and transform the pollutants in the water;
(5)将上述经过处理之后的污水排入含有水生植物的水池中,利用水生植物吸收降解水体中污染物;(5) Discharge the above-mentioned treated sewage into the pool containing aquatic plants, and use aquatic plants to absorb and degrade pollutants in the water body;
(6)将上述经过处理之后的水体进行过滤,去除悬浮物,然后排入中水池。(6) Filter the above-mentioned treated water body to remove suspended matter, and then discharge it into the reclaimed water tank.
一种用于上述治理污染水质方法的应用系统,特点是,包括调节池,调节池的一端与污水排放管道相通,调节池的另一端连通有曝气池,设有核外电子剥离设备,核外电子剥离设备通过管道与曝气池连通,曝气池与浮游生物池连通,浮游生物池与水生植物池连通,水生植物池与砂滤池连接,砂滤池与中水池连通,中水池与直排管道及回用管道连接。An application system for the above-mentioned method of controlling polluted water quality, which is characterized in that it includes a regulating pool, one end of the regulating pool is connected to the sewage discharge pipeline, and the other end of the regulating pool is connected to an aeration pool, and an extra-nuclear electron stripping device is provided. The external electron stripping equipment is connected to the aeration tank through pipelines, the aeration tank is connected to the plankton tank, the plankton tank is connected to the aquatic plant pool, the aquatic plant pool is connected to the sand filter tank, the sand filter tank is connected to the reclaimed water tank, and the reclaimed water tank is connected to the reclaimed water tank. In-line piping and reuse piping connections.
本发明采用了核外电子剥离技术(参见ZL201010586363X,一种剥离原子核外电子的方法及其装置),将空气输入至核外电子剥离的空间内,空气被激发为等离子状态,氧气分子电离裂解为氧原子;在持续高压电能量的作用下,原子的核外电子脱离原子核的束缚,得到自由电子(-e);氧原子和氧分子产生结合,组成臭氧(O3),将空气中含有的水分子裂解为羟基自由基(OH),独立的氢原子和独立的氧原子结合,再次产生羟基自由基(OH)。The present invention adopts extranuclear electron stripping technology (see ZL201010586363X, a method and device for stripping extranuclear electrons), and air is input into the space where extranuclear electrons are stripped, the air is excited into a plasma state, and oxygen molecules are ionized and dissociated into Oxygen atom; under the action of continuous high-voltage electric energy, the extranuclear electrons of the atom break away from the shackles of the nucleus to obtain free electrons (-e); oxygen atoms and oxygen molecules combine to form ozone (O3), which converts the oxygen contained in the air Water molecules are split into hydroxyl radicals (OH), and independent hydrogen atoms combine with independent oxygen atoms to generate hydroxyl radicals (OH) again.
将上述产生的含有臭氧、羟基自由基、自由电子的混合气体输入至被污染的水体内,羟基自由基和臭氧与可氧化的污染物产生化学反应;自由电子补偿重金属离子及其他离子状态的物质缺失的核外电子;通过氧化还原加电子补偿的方法,污染物的分子被打开,大分子链结构成为小分子结构,小分子结构的污染物再次与羟基自由基和臭氧发生化学反应,COD(化学需氧量)持续降低,同时各项污染指数也降低,自由电子补偿小分子结构污染物缺失的电子,使其分子团核内质子数量与核外电子数量均衡,水体内所含有的化学性能不稳定的有害物质失去原有的化学性能,成为稳定状态。Input the above-mentioned mixed gas containing ozone, hydroxyl radicals and free electrons into the polluted water body, and the hydroxyl radicals and ozone will react with oxidizable pollutants; the free electrons will compensate for heavy metal ions and other ionic substances The missing extranuclear electrons; through the method of redox plus electron compensation, the molecules of the pollutants are opened, the macromolecular chain structure becomes a small molecular structure, and the pollutants of the small molecular structure react chemically with hydroxyl radicals and ozone again, COD ( Chemical oxygen demand) continues to decrease, and at the same time, various pollution indexes are also reduced. Free electrons compensate for the electrons missing from small molecular structure pollutants, so that the number of protons in the nucleus of the molecular cluster and the number of electrons outside the nucleus are balanced. The chemical properties contained in the water body Unstable harmful substances lose their original chemical properties and become stable.
经上述方法处理之后的污水已经符合浮游生物生长环境,排入浮游生物(如藻类)池内,生物链底层的浮游生物会吸收污水中所含有污染物,污染物被降解转化,藻类得以生长繁殖。藻类处理之后的污水被再次排入水生植物池,由水生植物再次吸收水中的污染物,各项污染指标持续降低,处理之后的水体经过沉淀过滤,去除悬浮物,最终实现达标排放。The sewage treated by the above method has met the growth environment of plankton and is discharged into the plankton (such as algae) pool. The plankton at the bottom of the biological chain will absorb the pollutants contained in the sewage, the pollutants are degraded and transformed, and the algae can grow and reproduce. The sewage after algae treatment is discharged into the aquatic plant pool again, and the pollutants in the water are absorbed by the aquatic plants again, and various pollution indicators continue to decrease. After the treatment, the water body is filtered by sedimentation to remove suspended solids, and finally achieve discharge standards.
本发明是一种采用核外电子剥离技术并结合自然生态链的处理污水方法,优点在于运行成本低廉,无二次污染,无恶臭气体排放,排水指标可降低至地表三类水标准,可中水回用,节约水源。The present invention is a sewage treatment method that adopts extra-nuclear electron stripping technology combined with natural ecological chain. It has the advantages of low operating cost, no secondary pollution, no odorous gas discharge, and the drainage index can be reduced to the third-class water standard on the surface. Water reuse, save water.
下面结合附图及实施例对本发明做详细描述。The present invention will be described in detail below in conjunction with the accompanying drawings and embodiments.
附图说明Description of drawings
图1是本发明的一种应用系统的结构原理图。Fig. 1 is a structural principle diagram of an application system of the present invention.
图2是本发明的一种核外电子剥离设备的结构示意图。Fig. 2 is a schematic structural view of an extranuclear electron stripping device of the present invention.
附图图面说明:Description of drawings:
1污水排放管道,2调节池,3曝气池,4浮游生物池,5空气,6核外电子剥离设备,7自由电子,8羟基自由基,9臭氧,10水生植物池,11砂滤池,12中水池,13直排管道,14回用管道,2-2风机,2-4除尘器,2-5温度湿度调节器,2-6主控电柜,2-7核外电子剥离仓,2-8导体电极,2-9介质电极,2-10送风管道。1 sewage discharge pipeline, 2 regulating tank, 3 aeration tank, 4 plankton tank, 5 air, 6 extranuclear electron stripping equipment, 7 free electrons, 8 hydroxyl radical, 9 ozone, 10 aquatic plant tank, 11 sand filter tank , 12 medium pools, 13 straight pipes, 14 return pipes, 2-2 fans, 2-4 dust collectors, 2-5 temperature and humidity regulators, 2-6 main control cabinets, 2-7 nuclear electronic stripping warehouses , 2-8 conductor electrodes, 2-9 dielectric electrodes, 2-10 air supply ducts.
具体实施方式detailed description
参见图1,本发明的一种处理污水的应用系统,它包括调节池2,调节池2的一端与污水排放管道1相通,调节池2的另一端与曝气池3连通;在曝气池3中设有管道连接核外电子剥离设备6,参见图2,核外电子剥离设备6包括核外电子剥离仓2-7,核外电子剥离仓2-7的进气口通过通风管道与风机2-2连接,核外电子剥离仓2-7内设有导体电极2-8及介质电极2-9,核外电子剥离仓2-7另一端的出气口通过送风管道2-10连通曝气池3,在核外电子剥离仓2-7与风机2-2之间还设有除尘器2-4、温度湿度调节器2-5,核外电子剥离设备6由主控电柜2-6控制;在曝气池3的出口连接浮游生物池4,浮游生物池4出口处再连接水生植物池10,水生植物池10连接砂滤池11,砂滤池11与中水池12连接,中水池12与直排管道13及回用管道14连接,用于排放或中水回用。Referring to Fig. 1, a kind of application system of sewage treatment of the present invention, it comprises regulating pond 2, and one end of regulating pond 2 communicates with sewage discharge pipeline 1, and the other end of regulating pond 2 communicates with aeration pond 3; 3 is provided with pipeline connection extra-nuclear electron stripping equipment 6, referring to Fig. 2, the extra-nuclear electron stripping equipment 6 comprises the extra-nuclear electron stripping bin 2-7, and the air inlet of the extra-nuclear electron stripping bin 2-7 passes through the air duct and the blower fan 2-2 connection, the extra-nuclear electronic stripping chamber 2-7 is equipped with a conductor electrode 2-8 and a dielectric electrode 2-9, and the air outlet at the other end of the extra-nuclear electronic stripping chamber 2-7 is connected to the air outlet through the air supply pipe 2-10. The gas pool 3 is also provided with a dust collector 2-4 and a temperature and humidity regulator 2-5 between the outer nuclear electronic stripping warehouse 2-7 and the fan 2-2, and the outer nuclear electronic stripping equipment 6 is controlled by the main control electric cabinet 2- 6 control; the outlet of the aeration tank 3 is connected to the plankton pool 4, and the plankton pool 4 outlet is connected to the aquatic plant pool 10, and the aquatic plant pool 10 is connected to the sand filter tank 11, and the sand filter tank 11 is connected to the reclaimed water pool 12. The water pool 12 is connected with the straight discharge pipeline 13 and the reuse pipeline 14 for discharging or reusing middle water.
工作原理working principle
污水经过污水排放管道1排入调节池2内,均衡调节水质,使各种污染指标均衡,然后排入曝气池3。The sewage is discharged into the adjustment tank 2 through the sewage discharge pipe 1, and the water quality is adjusted in a balanced manner to balance various pollution indicators, and then discharged into the aeration tank 3.
用风机2-2将空气5输入到核外电子剥离设备6,空气置于核外电子剥离仓2-7内,采用3KV以上的高压电输入,使导体电极2-8和介质电极2-9之间产生高压电子束,高压电子束撞击气态分子链,空气被激发为等离子状态,氧气分子电离裂解为氧原子,在持续高压电能量的作用下,原子的核外电子脱离原子核的束缚,得到自由电子7,空气中的水分子被电离裂解成为羟基自由基8,独立的氢原子和独立的氧原子结合,再次产生羟基自由基,氧气被电离合成为臭氧9。Use the fan 2-2 to input the air 5 into the extra-nuclear electron stripping device 6, place the air in the extra-nuclear electron stripping chamber 2-7, and adopt a high-voltage electric input above 3KV to make the conductor electrode 2-8 and the dielectric electrode 2- A high-voltage electron beam is generated between 9, and the high-voltage electron beam hits the gaseous molecular chain, the air is excited into a plasma state, and the oxygen molecule is ionized and dissociated into oxygen atoms. , get free electrons 7, water molecules in the air are ionized and split into hydroxyl radicals 8, independent hydrogen atoms combine with independent oxygen atoms to generate hydroxyl radicals again, and oxygen is ionized to synthesize ozone 9.
将上述产生的含有自由电子、臭氧、羟基自由基的混合气体输入至曝气池3内,羟基自由基和臭氧与可氧化的污染物产生化学反应,自由电子补偿重金属离子及其他离子状态的物质缺失的核外电子,通过氧化还原加电子补偿的方法,污染物分子的被打开,大分子链结构成为小分子结构,小分子结构的污染物再次与羟基自由基和臭氧化学反应,COD(化学需氧量)持续降低,同时各项污染指数也降低,自由电子补偿小分子结构污染物缺失的电子,使其分子团核内质子数量与核外电子数量均衡,水体内所含有的化学性能不稳定的有害物质失去原有的化学性能,成为稳定状态。Input the above-mentioned mixed gas containing free electrons, ozone and hydroxyl radicals into the aeration tank 3, the hydroxyl radicals and ozone will react with oxidizable pollutants, and the free electrons will compensate for heavy metal ions and other ionic substances The missing extranuclear electrons, through the method of redox plus electron compensation, the pollutant molecules are opened, the macromolecular chain structure becomes a small molecular structure, and the pollutants of the small molecular structure chemically react with hydroxyl radicals and ozone again, COD (chemical Oxygen demand) continues to decrease, and at the same time, various pollution indexes are also reduced. Free electrons compensate for the electrons missing from small molecular structure pollutants, so that the number of protons in the nucleus of the molecular cluster is balanced with the number of electrons outside the nucleus. The chemical properties contained in the water body are not Stable harmful substances lose their original chemical properties and become stable.
经曝气池3内处理之后的污水排入浮游生物池4内,浮游生物(如藻类)吸收水体中所含的有机及无机物质,并快速生长繁殖,水中污染物得到降解转化,处理之后的水排入水生植物池10内,水体中所含有的污染物二次被水生植物吸收转化,水体中所含有的有机质及无机盐类再次被降低,经水生植物池10处理之后的水排入砂滤池11,悬浮物被过滤掉,水质达到排放标准,然后排入中水池12,经直排管道13排放或者排入中水管道14回收利用。The sewage treated in the aeration tank 3 is discharged into the plankton tank 4, and the plankton (such as algae) absorbs the organic and inorganic substances contained in the water body, and grows and reproduces rapidly, and the pollutants in the water are degraded and transformed. The water is discharged into the aquatic plant pool 10, the pollutants contained in the water body are absorbed and transformed by the aquatic plants for the second time, the organic matter and inorganic salts contained in the water body are reduced again, and the water treated by the aquatic plant pool 10 is discharged into the sand In the filter tank 11, the suspended matter is filtered out, and the water quality reaches the discharge standard, and then it is discharged into the reclaimed water tank 12, discharged through the straight discharge pipe 13 or discharged into the reclaimed water pipe 14 for recycling.
本发明利用核外电子剥离技术,采用臭氧、羟基自由基、自由电子,在化学反应和物理作用力的相互作用下,氧化、分解有机质,使其大分子结构转化为小分子结构,改变水体中分子结构不稳定的化学性能,去除水中有害物质,满足后期水处理过程中的浮游植物、水生植物及水生动物的生长生活环境,提高氧化降解性能,增加生化细菌处理污水及浮游生物吸收污染物的效果,结合自然生态链的运行达到污水净化处理的目的,经过处理之后的水体完全能够达到排放标准,可作为中水回收循环使用。The present invention uses extranuclear electron stripping technology, uses ozone, hydroxyl radicals, and free electrons to oxidize and decompose organic matter under the interaction of chemical reaction and physical force, so that its macromolecular structure is converted into a small molecular structure, and the water body is changed. The chemical properties of unstable molecular structure can remove harmful substances in water, meet the growth and living environment of phytoplankton, aquatic plants and aquatic animals in the later water treatment process, improve the performance of oxidation degradation, and increase the ability of biochemical bacteria to treat sewage and plankton to absorb pollutants As a result, combined with the operation of the natural ecological chain to achieve the purpose of sewage purification and treatment, the treated water can fully meet the discharge standards and can be recycled as reclaimed water.
Claims (2)
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201711084640.5A CN107619159A (en) | 2017-11-07 | 2017-11-07 | A kind of method and application system of pollution administration water quality |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201711084640.5A CN107619159A (en) | 2017-11-07 | 2017-11-07 | A kind of method and application system of pollution administration water quality |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| CN107619159A true CN107619159A (en) | 2018-01-23 |
Family
ID=61093476
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| CN201711084640.5A Pending CN107619159A (en) | 2017-11-07 | 2017-11-07 | A kind of method and application system of pollution administration water quality |
Country Status (1)
| Country | Link |
|---|---|
| CN (1) | CN107619159A (en) |
Citations (9)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| US5807491A (en) * | 1996-08-29 | 1998-09-15 | Advanced Oxidation Systems, Inc. | Electron beam process and apparatus for the treatment of an organically contaminated inorganic liquid or gas |
| CN101269902A (en) * | 2008-04-01 | 2008-09-24 | 总装备部工程设计研究总院 | Purification method for wastewater of ammunition disassembly |
| CN201890799U (en) * | 2010-11-20 | 2011-07-06 | 大连海事大学 | An oxygen active particle sewage treatment equipment |
| CN102479653A (en) * | 2010-11-30 | 2012-05-30 | 潘庆智 | Method and device for stripping out-nucleus electrons |
| CN203513429U (en) * | 2013-07-25 | 2014-04-02 | 东华大学 | Compound water purification system of algal-bacterial symbiotic surface flow wetland |
| CN104591473A (en) * | 2013-11-01 | 2015-05-06 | 中国石油化工股份有限公司大连石油化工研究院 | Advanced nitrogen and phosphorus removal technology |
| CN104944711A (en) * | 2015-07-03 | 2015-09-30 | 广州太和水生态科技有限公司 | Water processing method and device based on water ecosystem |
| CN106673257A (en) * | 2016-12-28 | 2017-05-17 | 常州大学 | Micropolluted raw water treatment integrated plant |
| CN207483557U (en) * | 2017-11-07 | 2018-06-12 | 潘庆智 | A kind of application system of pollution administration water quality |
-
2017
- 2017-11-07 CN CN201711084640.5A patent/CN107619159A/en active Pending
Patent Citations (9)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| US5807491A (en) * | 1996-08-29 | 1998-09-15 | Advanced Oxidation Systems, Inc. | Electron beam process and apparatus for the treatment of an organically contaminated inorganic liquid or gas |
| CN101269902A (en) * | 2008-04-01 | 2008-09-24 | 总装备部工程设计研究总院 | Purification method for wastewater of ammunition disassembly |
| CN201890799U (en) * | 2010-11-20 | 2011-07-06 | 大连海事大学 | An oxygen active particle sewage treatment equipment |
| CN102479653A (en) * | 2010-11-30 | 2012-05-30 | 潘庆智 | Method and device for stripping out-nucleus electrons |
| CN203513429U (en) * | 2013-07-25 | 2014-04-02 | 东华大学 | Compound water purification system of algal-bacterial symbiotic surface flow wetland |
| CN104591473A (en) * | 2013-11-01 | 2015-05-06 | 中国石油化工股份有限公司大连石油化工研究院 | Advanced nitrogen and phosphorus removal technology |
| CN104944711A (en) * | 2015-07-03 | 2015-09-30 | 广州太和水生态科技有限公司 | Water processing method and device based on water ecosystem |
| CN106673257A (en) * | 2016-12-28 | 2017-05-17 | 常州大学 | Micropolluted raw water treatment integrated plant |
| CN207483557U (en) * | 2017-11-07 | 2018-06-12 | 潘庆智 | A kind of application system of pollution administration water quality |
Similar Documents
| Publication | Publication Date | Title |
|---|---|---|
| CN100494101C (en) | A photoelectromagnetic integrated wastewater advanced oxidation method and its device | |
| CN203425700U (en) | Waste gas purifier | |
| CN207002487U (en) | A kind of sterilizable sewage-treatment plant | |
| CN206767867U (en) | A kind of persistent organic pollutant wastewater processing system | |
| CN105540992A (en) | Landfill leachate treatment technology | |
| CN108483743A (en) | A kind of coating wastewater processing system and method | |
| CN207108700U (en) | A kind of sewage-treatment plant | |
| Abdykadyrov et al. | Study of the process of cleaning water-containing iron solutions using ozone technology | |
| CN104609649A (en) | Method and device for treating wastewater containing high-concentration phenol | |
| CN103964638A (en) | Integrated sewage treatment equipment for combining MBR (Membrane Biological Reactor) membrane biological reaction technology and ozone technology | |
| CN100575284C (en) | The stench control system of sludge drying engineering | |
| CN107032567B (en) | Method for deodorizing and reducing municipal sludge | |
| CN103466754A (en) | Apparatus for processing sewage through high-pressure dielectric barrier liquid phase discharge plasma, and method thereof | |
| CN204816185U (en) | Ultraviolet ray deodorizing device | |
| CN205055776U (en) | Handle integrated equipment of foul gas | |
| CN103466755A (en) | Apparatus for processing sewage through high-pressure submerged gas jet discharge plasma, and method thereof | |
| CN207483557U (en) | A kind of application system of pollution administration water quality | |
| Gimeno et al. | Ozonation of 4‐chloro‐2‐methylphenoxyacetic acid (MCPA) in an activated sludge system | |
| CN204824256U (en) | Waste water advanced oxidation device | |
| CN107619159A (en) | A kind of method and application system of pollution administration water quality | |
| CN103466744B (en) | Apparatus for processing sewage through high-pressure dielectric barrier point discharge plasma, and method thereof | |
| CN211419933U (en) | Application system for treating sludge | |
| CN202479042U (en) | High-energy ion photolysis oxidization purifying device | |
| CN105289238A (en) | Intelligent compound malodorous gas treatment device with super-high efficiency | |
| Taghavi et al. | The Removal of Heavy Metals from the Leachate of Aged Landfill: The Application of the Fenton Process and Nanosilica Absorbent: 10.32526/ennrj/19/202100051 |
Legal Events
| Date | Code | Title | Description |
|---|---|---|---|
| PB01 | Publication | ||
| PB01 | Publication | ||
| SE01 | Entry into force of request for substantive examination | ||
| SE01 | Entry into force of request for substantive examination | ||
| RJ01 | Rejection of invention patent application after publication | ||
| RJ01 | Rejection of invention patent application after publication |
Application publication date: 20180123 |