JP6583868B2 - Composite membrane separation method applied to desalination and recovery of sewage - Google Patents
Composite membrane separation method applied to desalination and recovery of sewage Download PDFInfo
- Publication number
- JP6583868B2 JP6583868B2 JP2018537775A JP2018537775A JP6583868B2 JP 6583868 B2 JP6583868 B2 JP 6583868B2 JP 2018537775 A JP2018537775 A JP 2018537775A JP 2018537775 A JP2018537775 A JP 2018537775A JP 6583868 B2 JP6583868 B2 JP 6583868B2
- Authority
- JP
- Japan
- Prior art keywords
- composite membrane
- reactor
- membrane
- cathode
- anode
- 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.)
- Active
Links
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
- C02F1/469—Treatment of water, waste water, or sewage by electrochemical methods by electrochemical separation, e.g. by electro-osmosis, electrodialysis, electrophoresis
-
- 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
- C02F1/44—Treatment of water, waste water, or sewage by dialysis, osmosis or reverse osmosis
-
- 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
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02A—TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
- Y02A20/00—Water conservation; Efficient water supply; Efficient water use
- Y02A20/124—Water desalination
- Y02A20/131—Reverse-osmosis
Description
本発明は、膜による濾過と電気吸着のカップリング原理で汚水中のイオンを除去して排水の水質を向上させる、汚水（廃水）の処理分野に属す、汚水の脱塩回収に適用する複合膜分離方法に関する。 The present invention relates to a composite membrane applied to the desalination and recovery of sewage, belonging to the field of sewage (wastewater) treatment, which improves the quality of wastewater by removing ions in the sewage by the coupling principle of filtration and electroadsorption by membrane. It relates to a separation method.
社会経済の高速発展に従って、環境の状況が益々厳しくなり、多くの環境問題には、水資源の不足が益々深刻になり、社会経済の継続的な発展に制限がある問題が存在する。この状況で、僅か用水の節約のみを呼びかけるのは、現在の用水要求を満たせず、苦い塩水の淡水化、工業廃水のリサイクル利用及び市政廃水の再利用等、非常用の水源を開発することが求められているが、ある農村地域の地下水、沿岸都市での海水を混合した生活汚水、及び化工、印刷、食品加工等の産業の工業廃水には、例えばＣｌ-、ＮＯ3 -、ＳＯ4 2-及び各種類の金属イオン等の、濃度が高いイオンが含まれており、それらの処理の不当によって深刻な水汚染問題が発生する恐れがある。また、重金属イオンが水に入ると、居住者の生活飲用水の安全に影響があり、人体の健康に損害を与え、例えば、鉛は貧血を誘発することができ、水銀の濃縮は水俣病を引き起こすことができ、カドミウムは骨の痛みを引く起こすことができ、過度の銅摂取は肝臓を損傷することができ、ヒ素の化合物は非常に毒性が高くて発癌性がある。このため、このような非常用の水源への利用を実現するために、それらを脱塩処理して高標準の排水又は有効的な回収再利用の目的を達成する必要があり、これは、現在の研究課題の一つになる。 With the rapid development of socio-economic conditions, the environmental situation becomes increasingly severe, and for many environmental problems, the shortage of water resources becomes more serious, and there are problems that limit the continuous development of socio-economics. In this situation, the only call to save a small amount of water is to meet the current water requirements, and to develop an emergency water source, such as desalting bitter salt water, recycling industrial wastewater, and reusing municipal wastewater. For example, Cl − , NO 3 − , SO 4 2 may be used for groundwater in a certain rural area, domestic wastewater mixed with seawater in coastal cities, and industrial wastewater in industries such as chemical processing, printing, and food processing. - and the like each type of metal ions, the concentration includes a high ion, there is a possibility that serious water pollution problems due to undue their processing. Also, the entry of heavy metal ions into the water has an impact on the safety of the resident's drinking water and damages the health of the human body.For example, lead can induce anemia, and mercury concentration can cause Minamata disease. Cadmium can cause bone pain, excessive copper intake can damage the liver, and arsenic compounds are very toxic and carcinogenic. Therefore, in order to realize the use for such an emergency water source, it is necessary to desalinate them to achieve the purpose of high standard drainage or effective recovery and reuse. It becomes one of the research subjects.
近年、電気吸着技術は、除去効率および省エネルギー等の点で独特の利点があるため、広く注目されている。外部から低電圧の直流電源を供給することにより、電気吸着技術は汚染イオンを除去し、廃水の浄化を達成することができる。他の水処理技術と比較して、電気吸着技術は、簡単な操作とメンテナンス、長い装置寿命、低いエネルギー消費、二次汚染無しなどの特徴があり、溶解性汚染物質に対する良好な除去効果を有する。しかしながら、伝統的な電気吸着プロセスは、パーティクル状の汚染物質に対してより敏感である。パーティクルの導入は、脱塩効果を減少させるだけでなく、電極を詰め、装置のメンテナンスコストを増加させる。従って、パーティクル汚染物質を含んだ、塩を含有する廃水の処理においては、通常、パーティクルを捕捉するために、電気吸着プロセスの先端にプリ処理工程を設ける必要があり、それによって、電気吸着プロセスの設置面積、設備コストおよび操作工程が増加してしまうことになる。 In recent years, electroadsorption technology has received wide attention because of its unique advantages in terms of removal efficiency and energy saving. By supplying a low-voltage DC power supply from the outside, the electroadsorption technology can remove contaminating ions and achieve purification of wastewater. Compared with other water treatment technologies, electroadsorption technology has features such as easy operation and maintenance, long equipment life, low energy consumption, no secondary pollution and has good removal effect on soluble pollutants . However, traditional electrosorption processes are more sensitive to particulate contaminants. The introduction of particles not only reduces the desalting effect, but also packs the electrodes and increases the maintenance cost of the device. Therefore, in the treatment of wastewater containing salt containing particle contaminants, it is usually necessary to provide a pre-treatment step at the tip of the electroadsorption process in order to capture particles, thereby Installation area, equipment cost, and operation process will increase.
一方、膜分離方法は、固液分離の効果に優れているため、汚水処理分野で広く用いられている。膜分離技術は、電気吸着プロセスにおけるパーティクル汚染の問題を効果的に解決する有効な手段である。膜分離プロセスの発展を制限する最も主な問題は、膜の汚染であり、外部から直流電界を与えることにより、膜の表面を負の電荷に帯電させ、汚水中の負の電荷にも帯電したパーティクル汚染を排斥し、膜の汚染の作用を制御できるようになる。電気吸着と膜分離プロセスをカップリングすることにより、新しいタイプの導電性複合膜電気吸着脱塩プロセスを形成し、パーティクルの阻みとイオン除去を同時に実現でき、塩を有する廃水の処理のための新しいアイデアを形成することができる。しかし、既存の研究成果や文献報告は主に電気吸着プロセスの最適化に集中するものであり、且つ、国内特許での脱塩に関する成果は、例えば木内崇文（膜分離装置、膜分離方法、特許文献ＣＮ１０３０５２４３７Ａ）、常▲ツェン▼（電気吸着技術で工業廃水から選択的にＦｅ2+及び／又はＦｅ3+を除去する方法、特許文献ＣＮ１０４６０９５１８Ａ）のように、膜分離と電気吸着の単独に運行する動作条件に集中するものであり、膜分離および電気吸着カップリングのプロセスは滅多に報告されません。両方を組み合わせたいくつかのプロセスに関しては、張▲鴻▼涛（脱塩システムに用いられる膜-電気吸着装置、特許文献ＣＮ１０３６９３７１８Ａ）が電解吸着プロセスと組み合わせてイオン交換膜で廃水を脱塩しており、アノードイオン交換膜とカソードイオン交換膜を増加する目的は、アノードイオンとカソードイオンの透過性を選択的に高めることであり、イオン交換膜は汚水フィルタとして機能することができず、次に、該システムが依然として装置自身に対するパーティクル汚染物質の損傷を解決することができず、且つイオン交換膜のコストが高く、運行やメンテナンスが面倒である。 On the other hand, the membrane separation method is widely used in the sewage treatment field because of its excellent solid-liquid separation effect. Membrane separation technology is an effective means for effectively solving the problem of particle contamination in the electroadsorption process. The main problem that limits the development of the membrane separation process is the contamination of the membrane. By applying a DC electric field from the outside, the surface of the membrane is charged to a negative charge, and the negative charge in the sewage is also charged. It is possible to eliminate particle contamination and control the effect of membrane contamination. By coupling electroadsorption and membrane separation process, a new type of conductive composite membrane electroadsorption desalination process can be formed, which can simultaneously realize particle blockage and ion removal, a new for the treatment of wastewater with salt Ideas can be formed. However, existing research results and literature reports mainly focus on optimizing the electroadsorption process, and the achievements related to desalination in domestic patents are, for example, Takafumi Kiuchi (membrane separation device, membrane separation method, patent (Document CN103052437A), Tsuen (Method of selectively removing Fe 2+ and / or Fe 3+ from industrial wastewater by electroadsorption technology, Patent Document CN10609518A), and operates independently for membrane separation and electroadsorption. The process of membrane separation and electroadsorption coupling is rarely reported. For some processes that combine both, Zhang ▲ 鴻 ▼ 涛 (membrane-electroadsorber used in the desalination system, patent document CN103693718A) combined with the electrolytic adsorption process to desalinate wastewater with ion exchange membranes. The purpose of increasing the anode ion exchange membrane and the cathode ion exchange membrane is to selectively increase the permeability of the anode ion and the cathode ion, and the ion exchange membrane cannot function as a sewage filter. The system still cannot solve the damage of the particle pollutant to the apparatus itself, the cost of the ion exchange membrane is high, and the operation and maintenance are troublesome.
本発明は、膜分離と電気吸着を組合せしながら、汚水の濾過分離と電気吸着によるイオン脱離の機能を同時に実現し、汚水中におけるパーティクルを阻み、それによる吸着材料への損害を避け、同時に汚水中の汚染イオンを除去し、二次汚染を避け、エネルギーを節約し、コストを削減するものである。 While combining membrane separation and electroadsorption, the present invention simultaneously achieves the function of filtration separation of sewage and ion desorption by electroadsorption, prevents particles in the sewage, thereby avoiding damage to the adsorbent material, and at the same time It eliminates contaminating ions in sewage, avoids secondary contamination, saves energy, and reduces costs.
本発明は、その目的が、汚水処理中に固液分離及び脱塩の機能を同時に実現できる膜分離技術を提供することにあり、該技術方法は、膜分離と電気吸着プロセスをカップリングし、同時に汚水の濾過分離と電気吸着によるイオン脱離の機能を同時に実現し、パーティクルを阻み、廃水におけるイオン型汚染物質を吸着し、脱塩の効果を向上させ、二次汚染がなく、且つ操作が簡単で、エネルギー消耗が低く、低濃度の塩を含んだ廃水の処理に適用されるものである。 The object of the present invention is to provide a membrane separation technology capable of simultaneously realizing the functions of solid-liquid separation and desalting during sewage treatment, and this technical method couples membrane separation and electroadsorption process, At the same time, it simultaneously realizes the functions of filtration and separation of sewage and ion desorption by electroadsorption, blocking particles, adsorbing ionic pollutants in wastewater, improving the desalination effect, eliminating secondary contamination, and operating. It is simple, has low energy consumption and is applied to the treatment of wastewater containing low concentrations of salt.
本発明に提出される汚水の脱塩回収に適用する複合膜分離方法は、導電複合膜リアクターで汚水の脱塩を実現し、前記導電複合膜リアクターが給水システム１、電源システム２、膜リアクター３、排水制御システム４及び清浄水タンク５からなり、給水システム１は、給水タンクと給水流量調整装置とからなり、プロセス要求に応じて給水流量を調整し、給水流量調整装置が給水タンクの給水ポートに設置され、給水タンクの排水ポートがパイプを介して膜リアクターと接続され、膜リアクターがリアクタータンク、複合膜アセンブリー６及び攪拌システムからなり、リアクタータンク中に位置する複数の複合膜アセンブリー６がそれぞれ導電性の良い導線７を介して電源システム２の正極と負極に接続される。膜リアクターは、浸水式の配置方式を採用するように構成され、攪拌器がリアクタータンクに設置され、リアクタータンク内のリアクター液体を均一に混合させ、膜リアクターのリアクタータンクの排水ポートがパイプを介して排水システムと接続される。 The composite membrane separation method applied to the desalination and recovery of sewage submitted to the present invention realizes desalination of sewage with a conductive composite membrane reactor, and the conductive composite membrane reactor includes a water supply system 1, a power supply system 2, and a membrane reactor 3. The water supply system 1 is composed of a water supply tank and a water supply flow rate adjusting device, and adjusts the water supply flow rate according to the process request. The water supply flow rate adjusting device is a water supply port of the water supply tank. The drainage port of the water supply tank is connected to the membrane reactor through a pipe, and the membrane reactor is composed of the reactor tank, the composite membrane assembly 6 and the stirring system, and each of the plurality of composite membrane assemblies 6 located in the reactor tank The power supply system 2 is connected to the positive electrode and the negative electrode through a conductive wire 7 having good conductivity. The membrane reactor is constructed so as to adopt a submersible arrangement system, a stirrer is installed in the reactor tank, the reactor liquid in the reactor tank is uniformly mixed, and the drain port of the reactor tank of the membrane reactor is connected via a pipe. Connected to the drainage system.
各々の複合膜アセンブリーは、フラットフィルムになるよう構成され、カソード複合膜８、アノード複合膜９及び分離層１０からなり、このうち、カソード複合膜は、カソード電極１２とカソード電流コレクタ１１をポリマー材料で張り付けることで形成されるものであり、アノード複合膜は、アノード電極１３とアノード電流コレクタ１４をポリマー材料で張り付けることで形成されるものであり、前記カソード複合膜８とアノード複合膜９とは、短絡を防止するように分離層１０で仕切られ、前記カソード電流コレクタが給水ポート側に位置し、アノード電流コレクタが排水ポート側に位置し、即ち、給水が先にカソード電流コレクタとカソード電極を流れて分離層を流れてから、アノード電流コレクタとアノード電極を流れて、膜から排出するように導電複合膜リアクターに排出される。
具体的には、プロセス要求に合致した給水を給水タンクに入れ、給水流量調整装置で給水流量を調整し、給水タンクの排水が膜リアクターに入り、一定流量又は一定圧力の方式を採用するように運行し、給水が先にカソード電流コレクタとカソード電極を流れて分離層を流れてから、アノード電流コレクタとアノード電極を流れて、膜から排出するように導電複合膜リアクターに排出され、膜フラックスが８〜５０L／（ｍ2ｈ）になるように制御し、膜間差圧が０．４〜２０ｋＰａになり、電源をオンにし、膜リアクターを起動させ、塩を含んだ廃水中のイオン型汚染物を吸着するステップを備える。
Each composite membrane assembly is configured to be a flat film, and includes a cathode composite membrane 8, an anode composite membrane 9, and a separation layer 10, and the cathode composite membrane includes a cathode electrode 12 and a cathode current collector 11 as a polymer material. The anode composite film is formed by attaching the anode electrode 13 and the anode current collector 14 with a polymer material, and the cathode composite film 8 and the anode composite film 9 are formed. Is separated by a separation layer 10 so as to prevent a short circuit, the cathode current collector is located on the water supply port side, the anode current collector is located on the drainage port side, that is, the water supply is first performed on the cathode current collector and the cathode. Flow through the electrode and flow through the separation layer, then flow through the anode current collector and the anode electrode, from the membrane It is discharged to the conductive composite membrane reactor to exit.
Specifically, feed water that meets the process requirements is put into the feed tank, the feed flow rate is adjusted with the feed water flow rate adjustment device, and the waste water from the feed water tank enters the membrane reactor, adopting a method of constant flow rate or constant pressure. The water supply flows through the cathode current collector and the cathode electrode through the separation layer first, then flows through the anode current collector and the anode electrode, and is discharged to the conductive composite membrane reactor so as to be discharged from the membrane. Control to be 8-50 L / (m 2 h), the transmembrane pressure difference becomes 0.4-20 kPa, the power is turned on, the membrane reactor is activated, and ionic contamination in wastewater containing salt A step of adsorbing an object.
本発明において、給水タンクの給水を制御するＴＤＳ濃度が５０００ｍｇ／Ｌを下回る。 In this invention, the TDS density | concentration which controls the water supply of a water supply tank is less than 5000 mg / L.
本発明において、外から与えられた直流電圧範囲が０．４〜２．０Ｖになる。 In the present invention, the DC voltage range given from the outside becomes 0.4 to 2.0V.
本発明において、電源システムは、一定電圧の直流電源から電気吸着過程に給電し、カソード複合膜が電源の負極に接続され、アノード複合膜が電源の正極に接続され、電源システムとカソード又はアノードとが接続される電気回路中に電流検出装置を設けて電流の状況をリアルタイムに検出する。 In the present invention, the power supply system supplies power to the electroadsorption process from a constant voltage DC power supply, the cathode composite membrane is connected to the negative electrode of the power supply, the anode composite membrane is connected to the positive electrode of the power supply, and the power supply system and the cathode or anode A current detection device is provided in the electric circuit to which is connected to detect the current state in real time.
本発明において、カソード電流コレクタ又はアノード電流コレクタは、導電性の良いネット形状材料を採用し、前記材料は、チタン、チタン合金材料又はステンレス鋼材料のうち何れか一つであり、カソード電極又はアノード電極が、カーボンクロス、カーボンナノチューブ、活性炭粉末または繊維、カーボンエアロゲル、グラフェン、カーボンブラックのうち何れか一つである炭素系材料を採用し、ポリマー材料が、高分子ポリマーを採用し、具体的にはポリビニリデンフルオライド、ポリエーテルスルホン、ポリテトラフルオルエチレン、或いはポリアクリロニトリルのうち何れか一つである。 In the present invention, the cathode current collector or the anode current collector employs a net-shaped material having good conductivity, and the material is any one of titanium, a titanium alloy material, and a stainless steel material, and the cathode electrode or the anode The electrode adopts carbon-based material that is any one of carbon cloth, carbon nanotube, activated carbon powder or fiber, carbon aerogel, graphene, carbon black, and the polymer material adopts a polymer polymer, specifically Is any one of polyvinylidene fluoride, polyethersulfone, polytetrafluoroethylene, or polyacrylonitrile.
本発明において、前記分離層は、ナイロンネット、不織布、及びポリプロピレン材料のうち何れか一つである、水透過性の良い材料を採用する。 In the present invention, the separation layer employs a material having good water permeability, which is any one of a nylon net, a nonwoven fabric, and a polypropylene material.
本発明において、前記カソード複合膜とアノード複合膜とは、異なる電極材料と電流コレクタ材料を採用する。 In the present invention, the cathode composite film and the anode composite film employ different electrode materials and current collector materials.
本発明の原理は、フラットフィルムの電極の形式を採用し、膜分離と電気吸着過程をカップリングし、適切な膜フラックスで、分離層がパーティクル汚染物質を阻み、汚水の固液分離を実現し、アノード電極とカソード電極に対して適切な電圧を与え、汚水中におけるイオン型汚染物質を吸着し、汚水の脱塩の目的を実現することである。電極吸着の完了後、脱着は外部からの電源との短絡で始まり、電極を再生する。吸着-脱着の循環で膜アセンブリーのリサイクル利用を実現でき、運行コストを低減できるようになる。 The principle of the present invention adopts the form of flat film electrode, coupling membrane separation and electroadsorption process, with proper membrane flux, separation layer prevents particle pollutants and realizes solid-liquid separation of sewage An appropriate voltage is applied to the anode electrode and the cathode electrode to adsorb ionic pollutants in the sewage, thereby realizing the purpose of desalting the sewage. After completion of electrode adsorption, desorption begins with a short circuit with an external power source to regenerate the electrode. Adsorption-desorption circulation enables the recycling of membrane assemblies and reduces operating costs.
本発明は、従来技術と比較して以下のメリットを備える。
（１）本発明は、フラットフィルムの膜アセンブリ形式を採用し、膜分離と電気吸着をカップリングする技術方法は、固液分離と同時にイオン型汚染物質を吸着し、既存の膜分離と電気吸着プロセスの限界を破り、脱塩効果を向上させることができ、該技術は、運行エネルギー消耗が低く、運行管理が便利になるようになる。
（２）本発明の導電複合膜は、その外側がパーティクルを阻む機能を有し、無効な吸着を減少する同時に内側の吸着材料への摩耗を減少することができ、電極材料の使用効率を向上させ、装置のメンテナンス費用を低減することできるようになる。
（３）外から与えられた直流電場は、膜の表面を負の電荷に帯電させており、汚水中に負の電荷にも帯電したパーティクル、コロイドなどの汚染物質を排斥し、膜汚染を制御し、膜の洗浄周期および膜の使用寿命を延ばし、膜洗浄によるエネルギー消費を低減し、運行コストを低減することができるようになる。
The present invention has the following advantages over the prior art.
(1) The present invention adopts a flat film membrane assembly format, and the method of coupling membrane separation and electroadsorption is to adsorb ionic contaminants at the same time as solid-liquid separation. Breaking the limits of the process and improving the desalination effect, the technology reduces operating energy consumption and makes operating management more convenient.
(2) The conductive composite film of the present invention has a function of blocking particles on the outer side, can reduce ineffective adsorption, and at the same time can reduce wear on the inner adsorbing material, improving the use efficiency of the electrode material. Therefore, the maintenance cost of the apparatus can be reduced.
(3) The DC electric field applied from the outside charges the surface of the membrane to a negative charge, and removes contaminants such as particles and colloids that are also charged to a negative charge in the sewage to control membrane contamination. In addition, the cleaning cycle of the membrane and the service life of the membrane can be extended, the energy consumption by the membrane cleaning can be reduced, and the operation cost can be reduced.
以下、本発明について、図面を参照しながら詳細に説明する。 Hereinafter, the present invention will be described in detail with reference to the drawings.
［実施例１］
図１に示すプロセス装置を採用することにより、給水システム１は、給水タンクと給水流量調整装置とからなり、プリ処理を介してプロセス要求に合致した、ＮａＣｌを主にする苦い塩水が給水タンクに入り、給水の塩量が１２００ｍｇ／Ｌ（ＴＤＳで計測）になり、給水流量を調整して膜フラックスが１０Ｌ／ｍ2ｈになるように制御する。給水タンクは、その排水ポートが膜リアクターとパイプを介して接続され、その排水が膜リアクターに入り、膜リアクターがリアクタータンク、複合膜アセンブリー６及び攪拌システムからなり、図２に示す複合膜アセンブリーが採用され、このうち、アノード複合膜は、チタンネットとカーボンクロスとがＰＶＤＦで張り付けられることで形成され、カソード複合膜は、ステンレスのシルクネットとカーボンクロスとがＰＶＤＦで張り付けられることで形成され、分離層は、不織布である。カソード複合膜アセンブリーは、導電性が良い導線７を介して電源システム２の負極と接続され、アノード複合膜は、導線を介して電源の正極と接続され、膜リアクターは、浸水式の配置方式を採用するように構成され、攪拌器がリアクタータンク内に設置され、リアクタータンク内のリアクター液体を均一に混合させ、一定流量の方式で運行する。電源がオンになり、運行電圧が２．０Ｖになり、膜リアクターを起動させ、油圧保持時間が１ｈで、６ｈだけ運行し、運行の最中に膜間差圧が０．７ｋＰａになるように安定し、排水制御システム４で排水流量を調整し、システムの脱塩率が６５〜７２％になる。
[Example 1]
By adopting the process device shown in FIG. 1, the water supply system 1 is composed of a water supply tank and a water supply flow rate adjusting device, and the bitter salt water mainly composed of NaCl that matches the process requirements through pre-processing is supplied to the water supply tank. And the salt amount of the feed water is 1200 mg / L (measured by TDS), and the feed water flow rate is adjusted to control the membrane flux to 10 L / m 2 h. The drainage port of the water supply tank is connected to the membrane reactor via a pipe, the wastewater enters the membrane reactor, and the membrane reactor is composed of the reactor tank, the composite membrane assembly 6 and the stirring system. The composite membrane assembly shown in FIG. Among them, the anode composite film is formed by pasting titanium net and carbon cloth with PVDF, and the cathode composite film is formed by pasting stainless silk net and carbon cloth with PVDF. The separation layer is a nonwoven fabric. The cathode composite membrane assembly is connected to the negative electrode of the power supply system 2 through a conductive wire 7 having good conductivity, the anode composite membrane is connected to the positive electrode of the power supply through a conductive wire, and the membrane reactor has a submerged arrangement system. A stirrer is installed in the reactor tank, the reactor liquid in the reactor tank is uniformly mixed, and the system is operated at a constant flow rate. The power is turned on, the operating voltage is 2.0V, the membrane reactor is started, the hydraulic pressure holding time is 1h, it operates for 6h, and the transmembrane pressure difference is 0.7kPa during the operation. The drainage control system 4 adjusts the drainage flow rate, and the desalination rate of the system is 65 to 72%.
［実施例２］
図１に示すプロセス装置を採用することにより、給水システム１は、給水タンクと給水流量調整装置とからなり、プリ処理を介してプロセス要求に合致した、冷間圧延廃水の生物処理排水をタンクに流し、給水の塩量が１０００ｍｇ／Ｌ（ＴＤＳで計測）になり、浮遊固形物の濃度が５０ｍｇ／Ｌになり、給水流量を調整して膜フラックスが４０Ｌ／ｍ2ｈになるように制御する。給水タンクは、その排水ポートが膜リアクターとパイプを介して接続され、その排水が膜リアクターに入り、膜リアクターがリアクタータンク、複合膜アセンブリー６及び攪拌システムからなり、図２に示す複合膜アセンブリーが採用され、このうち、アノード複合膜とカソード複合膜とは、何れもチタンネットとカーボンクロスとがＰＡＮで張り付けられることで形成され、分離層がナイロンネットである。カソード複合膜アセンブリーは、導電性が良い導線７を介して電源システム２の負極と接続され、アノード複合膜アセンブリーは、導線を介して電源の正極と接続され、膜リアクターは、浸水式の配置方式を採用するように構成され、攪拌器がリアクタータンク内に設置され、リアクタータンク内のリアクター液体を均一に混合させ、一定流量の方式で運行する。電源がオンになり、運行電圧が１．６Ｖになり、膜リアクターを起動させ、油圧保持時間が１５ｍｉｎで、４ｈだけ運行し、運行の最中に膜間差圧が２．３ｋＰａになるように安定し、膜リアクターのリアクタータンクの排水ポートがパイプを介して排水システムと接続され、排水制御システム４で排水流量を調整し、システムの脱塩率が６０〜７０％になり、排水の浮遊固形物の濃度が検出の閾値を下回るようになっている。
[Example 2]
By adopting the process device shown in FIG. 1, the water supply system 1 is composed of a water supply tank and a water supply flow rate adjusting device, and the biological treatment wastewater of cold rolling wastewater that meets the process requirements through pre-treatment is stored in the tank. The amount of salt in the feed water is 1000 mg / L (measured with TDS), the concentration of suspended solids is 50 mg / L, and the feed flux is adjusted to control the membrane flux to 40 L / m 2 h. . The drainage port of the water supply tank is connected to the membrane reactor via a pipe, the wastewater enters the membrane reactor, and the membrane reactor is composed of the reactor tank, the composite membrane assembly 6 and the stirring system. The composite membrane assembly shown in FIG. Among them, the anode composite membrane and the cathode composite membrane are both formed by attaching a titanium net and a carbon cloth with PAN, and the separation layer is a nylon net. The cathode composite membrane assembly is connected to the negative electrode of the power supply system 2 through the conductive wire 7 having good conductivity, the anode composite membrane assembly is connected to the positive electrode of the power supply through the conductive wire, and the membrane reactor is a submersible arrangement system. The stirrer is installed in the reactor tank, and the reactor liquid in the reactor tank is uniformly mixed and operated in a constant flow rate manner. The power is turned on, the operation voltage becomes 1.6 V, the membrane reactor is started, the hydraulic pressure holding time is 15 min, it operates for 4 hours, and the transmembrane pressure difference becomes 2.3 kPa during operation. Stable, the drainage port of the reactor tank of the membrane reactor is connected to the drainage system through a pipe, the drainage control system 4 adjusts the drainage flow rate, the system desalination rate becomes 60-70%, and the wastewater solids The concentration of the object falls below the detection threshold.
［実施例３］
図１に示すプロセス装置を採用することにより、給水システム１は、給水タンクと給水流量調整装置とからなり、プリ処理を介してプロセス要求に合致した、硝酸塩を主にするある肥料生産工業廃水が給水タンクに入り、給水の塩量が９００ｍｇ／Ｌ（ＴＤＳで計測）になり、給水流量を調整して膜フラックスが１０Ｌ／ｍ2ｈになるように制御する。給水タンクは、その排水ポートがパイプを介して膜リアクターと接続され、その排水が膜リアクターに入り、膜リアクターがリアクタータンク、複合膜アセンブリー６及び攪拌システムからなり、図２に示す複合膜アセンブリーが採用され、このうち、アノード複合膜とカソード複合膜が何れもチタンネットとカーボンナノチューブとからなり、分離層がナイロンネットであり、カソード複合膜アセンブリーは、導電性が良い導線７を介して電源システム２の負極と接続され、アノード複合膜は、導線を介して電源の正極と接続され、膜リアクターは、浸水式の配置方式を採用するように構成され、攪拌器がリアクタータンクに設置され、リアクタータンク内のリアクター液体を均一に混合させ、一定流量の方式で運行する。電源がオンになり、運行電圧が２．０Ｖになり、膜リアクターを起動させ、油圧保持時間が１ｈで、４ｈだけ運行し、運行の最中に膜間差圧が２．４ｋＰａになるように安定し、膜リアクターのリアクタータンクの排水ポートがパイプを介して排水システムと接続され、排水制御システム４で排水流量を調整し、システムの脱塩率が５７〜６８％になる。
[Example 3]
By adopting the process device shown in FIG. 1, the water supply system 1 is composed of a water supply tank and a water supply flow rate adjusting device, and certain fertilizer-producing industrial wastewater mainly composed of nitrate that meets the process requirements through pre-processing. Entering the water supply tank, the amount of salt in the water supply becomes 900 mg / L (measured by TDS), and the flow rate of the water supply is adjusted to control the membrane flux to 10 L / m 2 h. The drainage port of the water supply tank is connected to the membrane reactor through a pipe, the wastewater enters the membrane reactor, and the membrane reactor is composed of the reactor tank, the composite membrane assembly 6 and the stirring system. The composite membrane assembly shown in FIG. Among them, the anode composite membrane and the cathode composite membrane are both made of titanium net and carbon nanotube, the separation layer is nylon net, and the cathode composite membrane assembly is connected to the power supply system via the conductive wire 7 having good conductivity. The anode composite membrane is connected to the positive electrode of the power source via a conductor, the membrane reactor is configured to adopt a submersible arrangement system, the stirrer is installed in the reactor tank, the reactor The reactor liquid in the tank is evenly mixed and operated with a constant flow rate. The power is turned on, the operation voltage becomes 2.0 V, the membrane reactor is started, the hydraulic pressure holding time is 1 h, the operation is only for 4 h, and the transmembrane pressure difference is 2.4 kPa during operation. The drainage port of the reactor tank of the membrane reactor is connected to the drainage system via a pipe, the drainage flow rate is adjusted by the drainage control system 4, and the desalination rate of the system becomes 57 to 68%.
［実施例４］
図１に示すプロセス装置を採用することにより、給水システム１は、給水タンクと給水流量調整装置とからなり、プリ処理を介してプロセス要求に合致した、ある銅を含んだ廃水が給水タンクに入り、給水の塩量が５００ｍｇ／Ｌ（ＴＤＳで計測）になり、給水流量を調整して膜フラックスが２５Ｌ／ｍ2ｈになるように制御する。給水タンクは、その排水ポートがパイプを介して膜リアクターと接続され、その排水が膜リアクターに入り、膜リアクターがリアクタータンク、複合膜アセンブリー６及び攪拌システムからなり、図２に示す複合膜アセンブリーが採用され、このうち、アノード複合膜とカソード複合膜が何れもチタンネットとカーボンナノチューブとからなり、分離層がナイロンネットであり、カソード複合膜アセンブリーは、導電性が良い導線７を介して電源システム２の負極と接続され、アノード複合膜は、導線を介して電源の正極と接続され、膜リアクターは、浸水式の配置方式を採用するように構成され、攪拌器がリアクタータンク内に設置され、リアクタータンク内のリアクター液体を均一に混合させ、一定流量の方式で運行する。電源がオンになり、運行電圧が１．６Ｖになり、膜リアクターを起動させ、油圧保持時間が２４ｍｉｎで、３ｈだけ運行し、運行の最中に膜間差圧が１．５ｋＰａになるように安定し、膜リアクターのリアクタータンクの排水ポートがパイプを介して排水システムと接続され、排水制御システム４で排水流量を調整し、システムの脱塩率が４５〜５８％になる。
[Example 4]
By adopting the process device shown in FIG. 1, the water supply system 1 is composed of a water supply tank and a water supply flow rate adjusting device, and waste water containing copper that meets the process requirements through pre-treatment enters the water supply tank. The salt amount of the feed water is 500 mg / L (measured by TDS), and the feed water flow rate is adjusted to control the membrane flux to 25 L / m 2 h. The drainage port of the water supply tank is connected to the membrane reactor through a pipe, the wastewater enters the membrane reactor, and the membrane reactor is composed of the reactor tank, the composite membrane assembly 6 and the stirring system. The composite membrane assembly shown in FIG. Among them, the anode composite membrane and the cathode composite membrane are both made of titanium net and carbon nanotube, the separation layer is nylon net, and the cathode composite membrane assembly is connected to the power supply system via the conductive wire 7 having good conductivity. The anode composite membrane is connected to the positive electrode of the power source via a conductor, the membrane reactor is configured to adopt a submersible arrangement system, the stirrer is installed in the reactor tank, The reactor liquid in the reactor tank is mixed uniformly and operated in a constant flow rate system. The power is turned on, the operation voltage becomes 1.6 V, the membrane reactor is started, the hydraulic pressure holding time is 24 min, it operates for 3 hours, and the transmembrane pressure difference becomes 1.5 kPa during operation. The drainage port of the reactor tank of the membrane reactor is connected to the drainage system via a pipe, and the drainage flow rate is adjusted by the drainage control system 4, so that the desalination rate of the system is 45 to 58%.
１…給水システム、２…電源システム、３…膜リアクター、４…排水制御システム、５…清浄水タンク、６…複合膜アセンブリー、７…導線、８…カソード複合膜、９…アノード複合膜、１０…分離層、１１…カソード電流コレクタ、１２…カソード電極、１３…アノード電極、１４…アノード電流コレクタ DESCRIPTION OF SYMBOLS 1 ... Water supply system, 2 ... Power supply system, 3 ... Membrane reactor, 4 ... Drainage control system, 5 ... Clean water tank, 6 ... Composite membrane assembly, 7 ... Conductor, 8 ... Cathode composite membrane, 9 ... Anode composite membrane, 10 ... separation layer, 11 ... cathode current collector, 12 ... cathode electrode, 13 ... anode electrode, 14 ... anode current collector
Claims (7)
前記給水システム（１）は、給水タンクと給水流量調整装置とからなり、プロセス要求に応じて給水流量を調整し、前記給水流量調整装置が前記給水タンクの給水ポートに設置され、前記給水タンクの排水ポートがパイプを介して前記膜リアクターと接続され、前記膜リアクターがリアクタータンク、複合膜アセンブリー（６）及び攪拌システムからなり、前記リアクタータンク中に位置する複数の前記複合膜アセンブリー（６）がそれぞれ導電性の良い導線（７）を介して前記電源システム（２）の正極と負極に接続され、前記膜リアクターは、浸水式の配置方式を採用するように構成され、攪拌器が前記リアクタータンクに設置され、前記リアクタータンク内のリアクター液体を均一に混合させ、前記膜リアクターの前記リアクタータンクの前記排水ポートがパイプを介して排水システムと接続され、
各々の前記複合膜アセンブリーは、フラットフィルムになるよう構成され、前記カソード複合膜（８）、アノード複合膜（９）及び分離層（１０）からなり、このうち、前記カソード複合膜は、カソード電極（１２）とカソード電流コレクタ（１１）をポリマー材料で張り付けることで形成されるものであり、前記アノード複合膜は、アノード電極（１３）とアノード電流コレクタ（１４）を前記ポリマー材料で張り付けることで形成されるものであり、
前記カソード複合膜（８）と前記アノード複合膜（９）とは、短絡を防止するように前記分離層（１０）で仕切られ、前記カソード電流コレクタが前記給水ポート側に位置し、前記アノード電流コレクタが前記排水ポート側に位置し、即ち、給水が先に前記カソード電流コレクタと前記カソード電極とを順に流れて前記分離層を流れてから、前記アノード電極と前記アノード電流コレクタとを順に流れて、膜から排出するように前記導電複合膜リアクターに排出され、
具体的には、前記プロセス要求に合致した給水を前記給水タンクに入れ、前記給水流量調整装置で前記給水流量を調整し、前記給水タンクの排水が前記膜リアクターに入り、一定流量又は一定圧力の方式を採用するように運行し、給水が先に前記カソード電流コレクタと前記カソード電極とを順に流れて前記分離層を流れてから、前記アノード電極と前記アノード電流コレクタとを順に流れて、膜から排出するように前記導電複合膜リアクターに排出され、膜フラックスが８〜５０Ｌ／（ｍ２ｈ）になるように制御し、膜間差圧が０．４〜２０ｋＰａになり、電源をオンにし、前記膜リアクターを起動させ、塩を含んだ廃水中のイオン型汚染物を吸着するステップを備える、
ことを特徴とする汚水の脱塩回収に適用する複合膜分離方法。 The conductive composite membrane reactor achieves desalination of sewage, and the conductive composite membrane reactor includes a water supply system (1), a power supply system (2), a membrane reactor (3), a drainage control system (4), and a clean water tank (5). Consists of
The water supply system (1) includes a water supply tank and a water supply flow rate adjustment device, adjusts the water supply flow rate according to a process request, the water supply flow rate adjustment device is installed in a water supply port of the water supply tank, A drainage port is connected to the membrane reactor via a pipe, and the membrane reactor includes a reactor tank, a composite membrane assembly (6), and a stirring system, and a plurality of the composite membrane assemblies (6) located in the reactor tank includes Each of the membrane reactors is connected to a positive electrode and a negative electrode of the power supply system (2) via conductive wires (7) having good conductivity, and the membrane reactor is configured to adopt a submersible arrangement system, and a stirrer is provided in the reactor tank. The reactor liquid in the reactor tank is uniformly mixed with the reactor liquid in the reactor tank. The drain port is connected to the drainage system via the pipe,
Each of the composite membrane assemblies is configured to be a flat film, and includes the cathode composite membrane (8), the anode composite membrane (9), and the separation layer (10). Of these, the cathode composite membrane is a cathode electrode. (12) and a cathode current collector (11) are pasted with a polymer material, and the anode composite film is pasted with an anode electrode (13) and an anode current collector (14) with the polymer material. Is formed by
The cathode composite membrane (8) and the anode composite membrane (9) are partitioned by the separation layer (10) so as to prevent a short circuit, the cathode current collector is located on the water supply port side, and the anode current collector positioned in the drainage port side, i.e., the cathode current collector and the said cathode electrode from sequentially flows through the separation layer flow, sequentially flows the said anode electrode and the anode current collector feedwater earlier , Discharged to the conductive composite membrane reactor to discharge from the membrane,
Specifically, feed water that meets the process requirements is put into the feed water tank, the feed water flow rate adjustment device is used to adjust the feed water flow rate, and the waste water from the feed water tank enters the membrane reactor, and the flow rate is constant or pressure is constant. runs to adopt a system, from the water supply to flow the separation layer flows sequentially and said cathode electrode and said cathode current collector above and sequentially flows through said anode current collector and the anode electrode, the film It is discharged to the conductive composite membrane reactor so as to be discharged, the membrane flux is controlled to be 8 to 50 L / (m2h), the transmembrane pressure difference becomes 0.4 to 20 kPa, the power is turned on, and the membrane Activating the reactor and adsorbing ionic contaminants in the wastewater containing salt;
A composite membrane separation method applied to desalination and recovery of sewage.
ことを特徴とする請求項１に記載の汚水の脱塩回収に適用する複合膜分離方法。 DC voltage range given from outside becomes 0.4-2.0V,
The composite membrane separation method applied to the desalination and recovery of sewage according to claim 1.
ことを特徴とする請求項１に記載の汚水の脱塩回収に適用する複合膜分離方法。 The power supply system supplies power to an electroadsorption process from a DC power supply having a constant voltage, the cathode composite film is connected to a negative electrode of the DC power supply, the anode composite film is connected to a positive electrode of the DC power supply, and the power supply system A current detection device is provided in the electric circuit connected to the cathode or anode to detect the current state in real time.
The composite membrane separation method applied to the desalination and recovery of sewage according to claim 1.
前記材料は、チタン、チタン合金材料又はステンレス鋼材料のうち何れか一つであり、
前記カソード電極又は前記アノード電極が、カーボンクロス、カーボンナノチューブ、活性炭粉末または繊維、カーボンエアロゲル、グラフェン、カーボンブラックのうち何れか一つである炭素系材料を採用し、
前記ポリマー材料が、高分子ポリマーを採用し、具体的にはポリビニリデンフルオライド、ポリエーテルスルホン、ポリテトラフルオルエチレン、或いはポリアクリロニトリルのうち何れか一つである、
ことを特徴とする請求項１に記載の汚水の脱塩回収に適用する複合膜分離方法。 The cathode current collector or the anode current collector employs a net-shaped material with good conductivity,
The material is any one of titanium, titanium alloy material or stainless steel material,
The cathode electrode or the anode electrode employs a carbon-based material that is any one of carbon cloth, carbon nanotube, activated carbon powder or fiber, carbon aerogel, graphene, carbon black,
The polymer material employs a high molecular polymer, and specifically is any one of polyvinylidene fluoride, polyethersulfone, polytetrafluoroethylene, or polyacrylonitrile.
The composite membrane separation method applied to the desalination and recovery of sewage according to claim 1.
ことを特徴とする請求項５に記載の汚水の脱塩回収に適用する複合膜分離方法。 The cathode composite membrane and the anode composite membrane employ different electrode materials and current collector materials,
A composite membrane separation method applied to the desalination and recovery of sewage according to claim 5.
ことを特徴とする請求項１に記載の汚水の脱塩回収に適用する複合膜分離方法。 The separation layer employs a material having good water permeability, which is any one of nylon net, nonwoven fabric, and polypropylene material.
The composite membrane separation method applied to the desalination and recovery of sewage according to claim 1.
Applications Claiming Priority (3)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201610041958.4A CN105692817B (en) | 2016-01-22 | 2016-01-22 | A kind of compound membrane separating method suitable for sewage desalination reuse |
| CN201610041958.4 | 2016-01-22 | ||
| PCT/CN2016/103464 WO2017124798A1 (en) | 2016-01-22 | 2016-10-27 | Composite membrane separation method applicable to desalting and recycling of sewage |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JP2019506292A JP2019506292A (en) | 2019-03-07 |
| JP6583868B2 true JP6583868B2 (en) | 2019-10-02 |
Family
ID=56228549
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP2018537775A Active JP6583868B2 (en) | 2016-01-22 | 2016-10-27 | Composite membrane separation method applied to desalination and recovery of sewage |
Country Status (4)
| Country | Link |
|---|---|
| JP (1) | JP6583868B2 (en) |
| CN (1) | CN105692817B (en) |
| AU (1) | AU2016388020B2 (en) |
| WO (1) | WO2017124798A1 (en) |
Families Citing this family (10)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN105692817B (en) * | 2016-01-22 | 2018-02-09 | 同济大学 | A kind of compound membrane separating method suitable for sewage desalination reuse |
| CN107441950B (en) * | 2017-08-02 | 2020-05-05 | 同济大学 | Electrochemical coupling ceramic filter membrane and application thereof |
| CN109987755B (en) * | 2017-12-29 | 2024-01-19 | 宁波方太厨具有限公司 | Water filtration system |
| CN110526349A (en) * | 2018-05-24 | 2019-12-03 | 华东理工大学 | A kind of electricity auxiliary membrane separating method |
| CN110182906B (en) * | 2019-07-12 | 2022-01-11 | 山东大学 | Treatment process for degrading organic wastewater by conductive organic membrane coupling filtering system |
| CN110498491B (en) * | 2019-08-28 | 2021-03-16 | 山东大学 | Treatment process for degrading antibiotic wastewater by electrochemical membrane filtration coupling system |
| CN111359449B (en) * | 2020-03-03 | 2021-05-18 | 清华大学 | Electroactive film and method for preparing same |
| CN112358097B (en) * | 2020-11-13 | 2022-10-25 | 昆明理工大学 | Method and device for strengthening high-electrolyte wastewater treatment through multiple physical fields |
| CN114149075B (en) * | 2021-12-09 | 2024-04-09 | 吉林省电力科学研究院有限公司 | Membrane biological reaction system with desalting capability |
| CN116835790B (en) * | 2023-06-15 | 2024-03-08 | 艾培克环保科技(上海)有限公司 | Treatment process of butyl acrylate wastewater |
Family Cites Families (11)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPH03234016A (en) * | 1990-02-09 | 1991-10-18 | Isuzu Motors Ltd | Electric double layer capacitor |
| JPH0688271A (en) * | 1991-07-03 | 1994-03-29 | Konica Corp | Carbonaceous electrode type electrolytic cell |
| US6309532B1 (en) * | 1994-05-20 | 2001-10-30 | Regents Of The University Of California | Method and apparatus for capacitive deionization and electrochemical purification and regeneration of electrodes |
| JP4212856B2 (en) * | 2002-09-06 | 2009-01-21 | 野村マイクロ・サイエンス株式会社 | Electrodesalting method and electrodesalting apparatus |
| US7813106B2 (en) * | 2006-12-19 | 2010-10-12 | General Electric Company | High current efficiency supercapacitor desalination devices and methods of making the same |
| CN101615512B (en) * | 2008-06-24 | 2013-02-06 | 通用电气公司 | Super-capacitor device and manufacturing method thereof |
| WO2010150534A1 (en) * | 2009-06-23 | 2010-12-29 | クラレケミカル株式会社 | Flow-through capacitor, method for producing deionized water, and device for producing deionized water |
| US9469554B2 (en) * | 2009-07-29 | 2016-10-18 | General Electric Company | Bipolar electrode and supercapacitor desalination device, and methods of manufacture |
| CN101891286B (en) * | 2010-04-02 | 2012-05-02 | 广州天至环保科技有限公司 | System for purifying and recycling electroplating/chemical plating wastewater on line |
| CN104211141B (en) * | 2014-09-11 | 2016-07-06 | 北京今大禹环保技术有限公司 | The cloth water-bound of a kind of SPE electrolysis bath and water distribution method thereof |
| CN105692817B (en) * | 2016-01-22 | 2018-02-09 | 同济大学 | A kind of compound membrane separating method suitable for sewage desalination reuse |
-
2016
- 2016-01-22 CN CN201610041958.4A patent/CN105692817B/en active Active
- 2016-10-27 AU AU2016388020A patent/AU2016388020B2/en active Active
- 2016-10-27 WO PCT/CN2016/103464 patent/WO2017124798A1/en active Application Filing
- 2016-10-27 JP JP2018537775A patent/JP6583868B2/en active Active
Also Published As
| Publication number | Publication date |
|---|---|
| AU2016388020A1 (en) | 2018-08-09 |
| JP2019506292A (en) | 2019-03-07 |
| AU2016388020B2 (en) | 2019-10-10 |
| CN105692817B (en) | 2018-02-09 |
| WO2017124798A1 (en) | 2017-07-27 |
| CN105692817A (en) | 2016-06-22 |
Similar Documents
| Publication | Publication Date | Title |
|---|---|---|
| JP6583868B2 (en) | Composite membrane separation method applied to desalination and recovery of sewage | |
| CN106044965B (en) | Device and method for recovering heavy metals in electroplating wastewater | |
| JP2008114213A (en) | Method for treating water | |
| CN101891331B (en) | Integrated treatment device for active carbon adsorption and electrochemical regeneration and use method thereof | |
| US20110240472A1 (en) | Capacitive deionization cell with through-flow | |
| KR20120133229A (en) | Capacitive deionization method for drinking water treatment | |
| CN102329029A (en) | Method for removing fluorin ions in water through electrocoagulation-adsorption | |
| CN107840441A (en) | Intelligent suitching type ozone/electric filter collaboration water treatment facilities and the method using its progress water process | |
| CN108328836B (en) | Water inlet control system based on high-salt-content wastewater reduction process | |
| CN109354304A (en) | A kind of sewage treatment and energy recovery method based on three-level membrane separation technique | |
| CN103819036B (en) | Treating method for desulfurization waste water of power plant | |
| CN210065421U (en) | Water treatment system | |
| KR102301795B1 (en) | Household water purifier comprising carbon electrode filter | |
| CN108751480A (en) | A kind of method and system of the industrial high-salt wastewater of processing | |
| CN213357034U (en) | Electro-adsorption desalination device | |
| CN212476408U (en) | Sewage treatment system | |
| JP2004008888A (en) | Oil separation method and oil separation apparatus for oil-containing liquid | |
| CN209866960U (en) | Autonomous controllable soil or sediment pollutant electric acidification dissociation device | |
| CN112321034A (en) | Device and method for synchronously electrolyzing/membrane separating/advanced oxidizing and cooperatively treating ammonium sulfate-containing wastewater and organic wastewater | |
| CN108033524B (en) | Double-layer mixed bed membraneless electrodeionization system and method for heavy metal wastewater treatment | |
| CN206970371U (en) | A kind of casing processes sewage-treatment plant | |
| CN111606397A (en) | Water purifier and method based on dielectrophoresis nano-membrane and electrodialysis | |
| CN104909505A (en) | Treatment system applied to industrial desalination | |
| CN110845059A (en) | Sewage treatment device based on electrochemistry | |
| CN112479447B (en) | Device and method for removing halogen-containing organic matters in water |
Legal Events
| Date | Code | Title | Description |
|---|---|---|---|
| A521 | Request for written amendment filed |
Free format text: JAPANESE INTERMEDIATE CODE: A523 Effective date: 20180718 Free format text: JAPANESE INTERMEDIATE CODE: A821 Effective date: 20180720 |
|
| A621 | Written request for application examination |
Free format text: JAPANESE INTERMEDIATE CODE: A621 Effective date: 20180718 |
|
| A871 | Explanation of circumstances concerning accelerated examination |
Free format text: JAPANESE INTERMEDIATE CODE: A871 Effective date: 20180718 |
|
| A521 | Request for written amendment filed |
Free format text: JAPANESE INTERMEDIATE CODE: A523 Effective date: 20181206 |
|
| RD01 | Notification of change of attorney |
Free format text: JAPANESE INTERMEDIATE CODE: A7426 Effective date: 20181210 |
|
| A975 | Report on accelerated examination |
Free format text: JAPANESE INTERMEDIATE CODE: A971005 Effective date: 20190222 |
|
| A131 | Notification of reasons for refusal |
Free format text: JAPANESE INTERMEDIATE CODE: A131 Effective date: 20190326 |
|
| A521 | Request for written amendment filed |
Free format text: JAPANESE INTERMEDIATE CODE: A523 Effective date: 20190612 |
|
| TRDD | Decision of grant or rejection written | ||
| A01 | Written decision to grant a patent or to grant a registration (utility model) |
Free format text: JAPANESE INTERMEDIATE CODE: A01 Effective date: 20190806 |
|
| A61 | First payment of annual fees (during grant procedure) |
Free format text: JAPANESE INTERMEDIATE CODE: A61 Effective date: 20190827 |
|
| R150 | Certificate of patent or registration of utility model |
Ref document number: 6583868 Country of ref document: JP Free format text: JAPANESE INTERMEDIATE CODE: R150 |
|
| R250 | Receipt of annual fees |
Free format text: JAPANESE INTERMEDIATE CODE: R250 |
|
| R250 | Receipt of annual fees |
Free format text: JAPANESE INTERMEDIATE CODE: R250 |