WO2003053866A1 - Water clarifying system - Google Patents
Water clarifying system Download PDFInfo
- Publication number
- WO2003053866A1 WO2003053866A1 PCT/JP2001/011175 JP0111175W WO03053866A1 WO 2003053866 A1 WO2003053866 A1 WO 2003053866A1 JP 0111175 W JP0111175 W JP 0111175W WO 03053866 A1 WO03053866 A1 WO 03053866A1
- Authority
- WO
- WIPO (PCT)
- Prior art keywords
- carrier
- conduit
- sewage
- water
- bacteria
- Prior art date
Links
Classifications
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F3/00—Biological treatment of water, waste water, or sewage
- C02F3/02—Aerobic processes
- C02F3/04—Aerobic processes using trickle filters
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F3/00—Biological treatment of water, waste water, or sewage
- C02F3/02—Aerobic processes
- C02F3/06—Aerobic processes using submerged filters
-
- 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
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W10/00—Technologies for wastewater treatment
- Y02W10/10—Biological treatment of water, waste water, or sewage
Definitions
- the present invention relates to a water purification system used to purify sewage containing organic pollutants such as sewage.
- the applicant developed the following water hatching system. That is, the water hatching system according to the present invention is characterized in that a helically arranged conduit is filled with a granular carrier impregnated with bacteria, and the sewage is put in from one end of the conduit and taken out from the other end. There is. In this water purification system, it is desirable to arrange the conduit so that the central axis of the helix is directed vertically.
- the sewage When the sewage is introduced from one end of the conduit, the sewage flows through the gap between the carriers in the conduit to the other end of the conduit. During this time, fixed pollutants mixed in the sewage are filtered off to the support, and pollutants such as organic substances dissolved in the soil are decomposed by Pacteria. Thus, from the other end of the conduit, Is taken out.
- conduits of the required length can be arranged in a narrow space, and the flow of sewage is smooth and stagnation does not occur, so that filtration and decomposition of pollutants are performed well.
- the conduit is arranged so that the central axis of the spiral is in the vertical direction, the waste water will flow through the conduit by its own weight, so no pump is required to flow the waste water.
- FIG. 1 shows the installation of the water purification system.
- FIG. 2 is an enlarged cross-sectional view of a carrier.
- FIG. 1 is a view showing the installation state of the water purification system according to the present invention, in which a spiral conduit '1' is provided with its central axis OO directed vertically, and the upper end opening of the conduit 1 is provided. Sewage water supply pipe 2 is connected to, and drain pipe 3 is connected to the lower end opening.
- Three perforated plates 4 are provided on the inner side of the conduit 1 at substantially equal positions from the upstream side to the downstream side, and the inside of the conduit 1 is divided into four chambers A, B, C and D. ing. Then, each chamber is filled with a granular carrier 5 impregnated with bacteria.
- the particle size of the carrier 5 is the largest in the most upstream room A, and is smaller in the order of the following rooms B, C and D.
- the pore size of each perforated plate 4 is such that water passes but not the carrier 5.
- inlets 6 a, 6 b, 6 c, 6 d for charging the carrier 5 and outlets 7 a, 7 b, 7 c, for taking out the carrier 5 corresponding to the respective chambers A, B, C, D. 7 d are provided respectively. These inlets and outlets are watertight and open. The door is attached.
- Carrier 5 is a fired product such as ceramic, zeolite, etc., which is made of sludge generated at the collection site of waste water to be purified, and has a porous structure as shown in the enlarged cross sectional view of FIG. ing. Therefore, when the carrier 5 is impregnated with the bacterial solution, the bacteria enter the pores 5a of the carrier 5, and the carrier 5 becomes a good growth bed of bacteria.
- the carrier 5 is made of sludge produced at the collection site of the sewage to be purified, and thus is a favorable condition as an environment in which bacteria grow and grow. In addition, the use of sludge helps to reduce the amount of sludge and reduce the treatment of sludge.
- the carrier solution 5 may be impregnated with a bacterial solution immediately before using it to maintain the vitality of the bacteria.
- the type of bacteria to be impregnated into the carrier 5 may be selected appropriately according to the type of contaminant contained in the water to be treated. For example, it is effective to combine aerobic bacteria with anaerobic Pacteria. In this case, if the support 5 has a porous structure, aerobic '14 bacteria will inhabit near the entrance of the surface of the support 5 and the entrance of the vacancies 5a, and anaerobic bacteria will be deep in the vacancies 5a. It is convenient because it is possible to get a parting like being inhabited. Also, bacteria that degrade non-organic properties, such as environmental hormones and dioxins, may be used.
- the carrier 5 impregnated with pacter When the carrier 5 impregnated with pacter is filled in the conduit 1 and the sewage is supplied from the sewage supply pipe 2 to the conduit 1, the sewage passes through the room A, the room B, the room C and the room D sequentially, and the sewage in between The fixed contaminants that are mixed in are filtered off to the carrier 5. In addition, contaminants such as organic substances dissolved in sewage are decomposed by bacteria. Thus, the purified water is taken out to the drainage pipe 3. If the carrier 5 filled with the fixed contaminants collected by filtration or the bacterial membrane exfoliated from the surface of the carrier 5 becomes clogged, the inlets 6a, 6b, 6c, 6d and the carrier 5 are removed. The outlet 7a, 7b, 7c, 7d may be used to replace with the new carrier 5.
- the spiral guiding is performed in a posture in which the central axis 1010 is directed in the vertical direction.
- the water purification system can purify sewage only by circulating sewage in one direction through a spiral conduit filled with a carrier impregnated with bacteria. Because of this, the system is simple, can be installed in a narrow space, and has a low maintenance cost. In addition, by using porous granular calcinated material, which uses sludge generated at the collection site of the sewage to be purified, as a carrier for impregnating bacteria, it is an environment for good growth and growth of bacteria. As a result, the purification capacity can be improved and sludge can be used effectively.
Landscapes
- Life Sciences & Earth Sciences (AREA)
- Water Supply & Treatment (AREA)
- Microbiology (AREA)
- Hydrology & Water Resources (AREA)
- Engineering & Computer Science (AREA)
- Environmental & Geological Engineering (AREA)
- Biodiversity & Conservation Biology (AREA)
- Chemical & Material Sciences (AREA)
- Organic Chemistry (AREA)
- Biological Treatment Of Waste Water (AREA)
- Apparatus Associated With Microorganisms And Enzymes (AREA)
- Immobilizing And Processing Of Enzymes And Microorganisms (AREA)
- Purification Treatments By Anaerobic Or Anaerobic And Aerobic Bacteria Or Animals (AREA)
Abstract
A water clarifying system, characterized in that a tube (1) in a spiral shape are packed with particulate carriers (5) impregnated with bacteria, and foul water is introduced into said tube (1) at one end thereof and is withdrawn from the other end of said tube. The tube (1) is preferably arranged so that the central axis O-O of the spiral is vertical. The carrier (5) is preferably prepared by forming a porous fired material originated from the sludge obtained in the field where the foul water to be clarified has been collected. The system allows the clarification of foul water at a reduced cost with a simple device.
Description
明 細 書 Specification
水の浄化システム 技術分野 Water purification system
この発明は、 下水等の有機性の汚濁物質を含む汚水を浄化するために用いられ る水の浄化システムに関する。 The present invention relates to a water purification system used to purify sewage containing organic pollutants such as sewage.
背景技術 Background art
従来、 有機性の汚濁物質を含む汚水の浄化には、 バクテリアによって汚濁物質 を分解させる方法が広く用いられており、 その代表的なものとして活性汚泥法、 生物膜法等がある。 Heretofore, methods for decomposing pollutants by bacteria have been widely used for purification of sewage containing organic pollutants, and the activated sludge method, biofilm method, etc. are representative.
これら従来の方法は、 処理槽、 配管等からなる複雑な設備と広いスペースとを 必要とし、 しかも曝気を継続的【'こ行わなければならないのでランニングコストが 高くつくという問題があった。 このような事情から、 簡単な設備で安価に汚水を 浄化できる方法の開発が望まれている。 発明の開示 These conventional methods require complicated facilities consisting of treatment tanks, piping, etc. and a large space, and moreover, there is a problem that the running cost is high because aeration must be continuously performed. Under these circumstances, it is desirable to develop a method that can purify sewage at low cost with simple equipment. Disclosure of the invention
そこで、 本出願人は次のような水の诤化システムを開発した。 すなわち、 本発 明にかかる水の诤化システムは、 螺旋状に配した導管にバクテリアを含浸させた 粒状の担体を充填し、 当該導管の一方端から汚水を入れ他方端から取り出すこと を特徴としている。 この水の浄化システムにおいては、 螺旋の中心軸が鉛直方向 を向くように導管を配置するのが望ましい。 Therefore, the applicant developed the following water hatching system. That is, the water hatching system according to the present invention is characterized in that a helically arranged conduit is filled with a granular carrier impregnated with bacteria, and the sewage is put in from one end of the conduit and taken out from the other end. There is. In this water purification system, it is desirable to arrange the conduit so that the central axis of the helix is directed vertically.
導管の一方端から汚水を入れると、 汚水は導管内の担体と担体の隙間を通って 、 導管の他方端側へ流れる。 この間に、 汚水に混じっている固定の汚濁物質が担 体に濾し取られると共に、 汚永に溶け込んでいる有機物等の汚濁物質はパクテリ ァによって分解される。 これにより、 導管の他方端からは、 诤化された清浄な水
が取り出される。 When the sewage is introduced from one end of the conduit, the sewage flows through the gap between the carriers in the conduit to the other end of the conduit. During this time, fixed pollutants mixed in the sewage are filtered off to the support, and pollutants such as organic substances dissolved in the soil are decomposed by Pacteria. Thus, from the other end of the conduit, Is taken out.
導管が螺旋状であると、 必要長さの導管を狭いスペースに配設することができ 、 しかも汚水の流れが円滑で澱みが生じないので、 汚濁物質の濾過や分解が良好 に行われる。 また、 螺旋の中心軸が鉛直方向を向くように導管を配置すると、 汚 水が自重で導管を流れるので、 汚水を流すためのポンプが不要である。 If the conduits are spiral, conduits of the required length can be arranged in a narrow space, and the flow of sewage is smooth and stagnation does not occur, so that filtration and decomposition of pollutants are performed well. In addition, if the conduit is arranged so that the central axis of the spiral is in the vertical direction, the waste water will flow through the conduit by its own weight, so no pump is required to flow the waste water.
前記担体を、 浄化しょうとする汚水の採取現場で生じた汚泥を原料とする多孔 質の焼成物で成形すると、 パクテリァが成育増殖する環境として好条件が得られ て好ましい。 図面の簡単な説明 It is preferable to form the above-mentioned carrier from a porous baked product using sludge generated at the collection site of waste water to be purified as a raw material, and favorable conditions can be obtained as an environment in which pacteria grow and grow. Brief description of the drawings
第 1図は、 水の浄化システムの設置状態を示す図である。 また、 第 2図は、 担 体の拡大断面図である。 発明を実施するための最良の形態 FIG. 1 shows the installation of the water purification system. FIG. 2 is an enlarged cross-sectional view of a carrier. BEST MODE FOR CARRYING OUT THE INVENTION
以下、 図面に表された実施の形態に基づき、 本発明を具体的に説明する。 第 1図は本発明による水の浄化システムの設置状態を示す図であり、 中心軸〇 ー〇が鉛直方向を向く姿勢で螺旋状の導管' 1が設けられ、 この導管 1の上端開口 ' 部に汚水供給管 2が接続され、 下端開口部に排水管 3が接続されている。 Hereinafter, the present invention will be specifically described based on the embodiments shown in the drawings. FIG. 1 is a view showing the installation state of the water purification system according to the present invention, in which a spiral conduit '1' is provided with its central axis OO directed vertically, and the upper end opening of the conduit 1 is provided. Sewage water supply pipe 2 is connected to, and drain pipe 3 is connected to the lower end opening.
導管 1の内側には上流側から下流側にかけてほぼ等間隔の位置に 3個の有孔プ レート 4が設けられており、 導管 1の内部は A, B , C , Dの 4室に仕切られて いる。 そして、 各室にバクテリアを含浸させた粒状の担体 5が充填されている。 担体 5の粒径は、 最上流の A室のものが最も大きく、 以下 B室、 C室、 D室の順 に小さくなつている。 各有孔プレート 4の孔径は、 水は通すが担体 5は通さない ようになつている。 また、 各室 A, B , C , Dに対応して、 担体 5を投入する投 入口 6 a , 6 b , 6 c, 6 dと担体 5を取り出す取出口 7 a , 7 b , 7 c , 7 d とがそれぞれ設けられている。 これら投入口及び取出口には、 水密性を有する開
閉扉が付けられている。 Three perforated plates 4 are provided on the inner side of the conduit 1 at substantially equal positions from the upstream side to the downstream side, and the inside of the conduit 1 is divided into four chambers A, B, C and D. ing. Then, each chamber is filled with a granular carrier 5 impregnated with bacteria. The particle size of the carrier 5 is the largest in the most upstream room A, and is smaller in the order of the following rooms B, C and D. The pore size of each perforated plate 4 is such that water passes but not the carrier 5. Also, inlets 6 a, 6 b, 6 c, 6 d for charging the carrier 5 and outlets 7 a, 7 b, 7 c, for taking out the carrier 5 corresponding to the respective chambers A, B, C, D. 7 d are provided respectively. These inlets and outlets are watertight and open. The door is attached.
担体 5は、 浄化しょうとする汚水の採取現場で生じた汚泥を原料とするセラミ ック、 ゼォライト等の焼成物であって、 第 2図の拡大断面図に示すような多孔質 の構造をしている。 このため、 担体 5にバクテリア溶液を含浸させると、 バクテ リアが担体 5の空孔 5 aに入り込んで、 担体 5がバクテリアの良好な増殖床とな る。 担体 5は浄化しょうとする汚水の採取現場で生じた汚泥を原料としているの で、 バクテリアが成育増殖する環境として好条件である。 また、 汚泥を利用する ことで、 汚泥の量を減少させ、 汚泥の処理を軽減させるのにも役立つ。 なお、 担 体 5にバクテリア溶液を含浸するのは、 バクテリアの活力を維持するために、 使 用する直前に行うのがよい。 Carrier 5 is a fired product such as ceramic, zeolite, etc., which is made of sludge generated at the collection site of waste water to be purified, and has a porous structure as shown in the enlarged cross sectional view of FIG. ing. Therefore, when the carrier 5 is impregnated with the bacterial solution, the bacteria enter the pores 5a of the carrier 5, and the carrier 5 becomes a good growth bed of bacteria. The carrier 5 is made of sludge produced at the collection site of the sewage to be purified, and thus is a favorable condition as an environment in which bacteria grow and grow. In addition, the use of sludge helps to reduce the amount of sludge and reduce the treatment of sludge. The carrier solution 5 may be impregnated with a bacterial solution immediately before using it to maintain the vitality of the bacteria.
担体 5に含浸させるバクテリアの種類は、 処理する水に含まれる汚染物質の種 類に応じて適当なものを選択するとよい。 例えば、 好気性のバクテリアと嫌気性 のパクテリアとを併用すると効果的である。 その場合、 担体 5が多孔質の構造で あると、 好気' 14のバクテリアは担体 5の表面部ゃ空孔 5 aの入口付近で生息し、 嫌気性のバクテリアは空孔 5 aの奥深くで生息するというように棲み分けが得ら れるので好都合である。 また、 有機物以外の特性.物質、 例えば環境ホルモンゃダ ィォキシンを分解するバクテリアを使用してもよい。 The type of bacteria to be impregnated into the carrier 5 may be selected appropriately according to the type of contaminant contained in the water to be treated. For example, it is effective to combine aerobic bacteria with anaerobic Pacteria. In this case, if the support 5 has a porous structure, aerobic '14 bacteria will inhabit near the entrance of the surface of the support 5 and the entrance of the vacancies 5a, and anaerobic bacteria will be deep in the vacancies 5a. It is convenient because it is possible to get a parting like being inhabited. Also, bacteria that degrade non-organic properties, such as environmental hormones and dioxins, may be used.
パクテリァを含浸させた担体 5を導管 1に充填して、 汚水供給管 2より導管 1 に汚水を供給すると、 汚水は A室、 B室、 C室、 D室を順に通過し、 その間に汚 水に混じっている固定の汚濁物質が担体 5に濾し取られる。 また、 汚水に溶け込 んでいる有機物等の汚濁物質はバクテリアによって分解される。 これにより、 排 水管 3には、 浄化された清浄な水が取り出される。 濾し取った固定の汚濁物質や 担体 5の表面から剥離したバクテリアの膜等によって充填されている担体 5が目 詰まりの状態となれば、 投入口 6 a , 6 b , 6 c, 6 d及び取出口 7 a, 7 b , 7 c , 7 dを利用して新しい担体 5と交換すればよい。 When the carrier 5 impregnated with pacter is filled in the conduit 1 and the sewage is supplied from the sewage supply pipe 2 to the conduit 1, the sewage passes through the room A, the room B, the room C and the room D sequentially, and the sewage in between The fixed contaminants that are mixed in are filtered off to the carrier 5. In addition, contaminants such as organic substances dissolved in sewage are decomposed by bacteria. Thus, the purified water is taken out to the drainage pipe 3. If the carrier 5 filled with the fixed contaminants collected by filtration or the bacterial membrane exfoliated from the surface of the carrier 5 becomes clogged, the inlets 6a, 6b, 6c, 6d and the carrier 5 are removed. The outlet 7a, 7b, 7c, 7d may be used to replace with the new carrier 5.
また、 上記実施の形態では、 中心軸〇一〇が鉛直方向を向く姿勢で螺旋状の導
管 1を配置して、 汚水が自重で導管を流れるようにすることで、 汚水を流すため のボンプを不要にしているが、 中心軸〇一〇が水平方向よりも僅かに傾く姿勢で 導管 1を配置してもよく、 この場^は傾斜度合いに応じてゆつくりと汚水の処理 を行うことができる。 産業上の利用可能性 Further, in the above embodiment, the spiral guiding is performed in a posture in which the central axis 1010 is directed in the vertical direction. By arranging the pipe 1 so that the sewage flows through the conduit under its own weight, the pump for making the sewage flow unnecessary, but with the central axis slightly inclined relative to the horizontal direction, the conduit 1 Can be placed, and this place can perform the treatment of sewage and sewage depending on the degree of inclination. Industrial applicability
以上に説明したように、 本発明にかかる水の浄化システムは、 バクテリアを含 浸させた担体が充¾されている螺旋状の導管に汚水を一方向に流通させる けで 汚水を浄化できるものであるから、 設備が簡単で、 狭くスペースに設置すること ができ、 しかも維持費があまりかからないシステムとなった。 また、 バクテリア を含浸させる担体として、 浄化しょうとする汚水の採取現場で生じた汚泥を原料 とする多孔質の粒状焼成物を使用することにより、 バクテリアにとつて良好な成 育増殖するための環境が得られ、 浄化能力を向上させられると共に、 汚泥を有効 利用することができる。
As described above, the water purification system according to the present invention can purify sewage only by circulating sewage in one direction through a spiral conduit filled with a carrier impregnated with bacteria. Because of this, the system is simple, can be installed in a narrow space, and has a low maintenance cost. In addition, by using porous granular calcinated material, which uses sludge generated at the collection site of the sewage to be purified, as a carrier for impregnating bacteria, it is an environment for good growth and growth of bacteria. As a result, the purification capacity can be improved and sludge can be used effectively.
Claims
1 . 螺旋状に配した導管にバクテリアを含浸させた粒状の担体を充填し、 当該導 管の一方端から汚水を入れ他方端から取り出すことを特徴とする水の浄化システ ム。 1. A water purification system characterized in that a spirally arranged conduit is filled with a granular carrier impregnated with bacteria, and sewage is introduced from one end of the conduit and removed from the other end.
2 . 螺旋の中心軸が鉛直方向を向くように導管が配置されている請求の範囲第 1 項に記載の水の浄化システム。 2. The water purification system according to claim 1, wherein the conduit is disposed such that the central axis of the spiral points in the vertical direction.
3 . 前記担体は、 浄化しょうとする汚水の採取現場で生じた汚泥を原料とする多 孔質の焼成物で成形されている請求の範囲第 1項又は請求の範囲第 2項に記載の 水の浄化システム。
3. The water according to claim 1 or claim 2, wherein the carrier is formed of a porous fired product made of sludge generated at a collection site of waste water to be purified. Purification system.
Priority Applications (3)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP2000238952A JP4019209B2 (en) | 2000-08-07 | 2000-08-07 | Water purification system |
AU2002217462A AU2002217462A1 (en) | 2001-12-20 | 2001-12-20 | Water clarifying system |
PCT/JP2001/011175 WO2003053866A1 (en) | 2000-08-07 | 2001-12-20 | Water clarifying system |
Applications Claiming Priority (2)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP2000238952A JP4019209B2 (en) | 2000-08-07 | 2000-08-07 | Water purification system |
PCT/JP2001/011175 WO2003053866A1 (en) | 2000-08-07 | 2001-12-20 | Water clarifying system |
Publications (1)
Publication Number | Publication Date |
---|---|
WO2003053866A1 true WO2003053866A1 (en) | 2003-07-03 |
Family
ID=28043515
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
PCT/JP2001/011175 WO2003053866A1 (en) | 2000-08-07 | 2001-12-20 | Water clarifying system |
Country Status (2)
Country | Link |
---|---|
JP (1) | JP4019209B2 (en) |
WO (1) | WO2003053866A1 (en) |
Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN104529050A (en) * | 2014-11-25 | 2015-04-22 | 浙江浙牌科技有限公司 | Efficient rural sewage purification apparatus |
Families Citing this family (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP4019209B2 (en) * | 2000-08-07 | 2007-12-12 | 株式会社ソナー | Water purification system |
WO2005019119A1 (en) * | 2003-08-23 | 2005-03-03 | Moo-Won Byun | Pipe type water treatment apparatus and water treatment system using the same |
JP2011050902A (en) * | 2009-09-03 | 2011-03-17 | Toshiba Corp | Water treatment system for sewage |
CN102092839B (en) * | 2010-12-07 | 2012-07-04 | 江苏苏净集团有限公司 | Compact supporting filler |
Citations (6)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPS6325198U (en) * | 1986-07-31 | 1988-02-19 | ||
JPH078978A (en) * | 1993-06-25 | 1995-01-13 | Matsushita Electric Works Ltd | Waste water treatment apparatus |
JPH10137776A (en) * | 1996-11-08 | 1998-05-26 | Yamaguchi Yukio | Sewage treating device and treated water storage tank |
JP2001047077A (en) * | 1999-08-16 | 2001-02-20 | Matsushita Electric Ind Co Ltd | Carbide biological filter bed, its production thereof and biological cleaning treatment apparatus using the carbide biological filter bed |
JP3082931U (en) * | 2001-05-24 | 2002-01-11 | 宗一 前田 | Soil purification material using useful microorganisms and porous sludge fired ceramics |
JP2002045878A (en) * | 2000-08-07 | 2002-02-12 | Sonar:Kk | Water cleaning system |
-
2000
- 2000-08-07 JP JP2000238952A patent/JP4019209B2/en not_active Expired - Lifetime
-
2001
- 2001-12-20 WO PCT/JP2001/011175 patent/WO2003053866A1/en active Application Filing
Patent Citations (6)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPS6325198U (en) * | 1986-07-31 | 1988-02-19 | ||
JPH078978A (en) * | 1993-06-25 | 1995-01-13 | Matsushita Electric Works Ltd | Waste water treatment apparatus |
JPH10137776A (en) * | 1996-11-08 | 1998-05-26 | Yamaguchi Yukio | Sewage treating device and treated water storage tank |
JP2001047077A (en) * | 1999-08-16 | 2001-02-20 | Matsushita Electric Ind Co Ltd | Carbide biological filter bed, its production thereof and biological cleaning treatment apparatus using the carbide biological filter bed |
JP2002045878A (en) * | 2000-08-07 | 2002-02-12 | Sonar:Kk | Water cleaning system |
JP3082931U (en) * | 2001-05-24 | 2002-01-11 | 宗一 前田 | Soil purification material using useful microorganisms and porous sludge fired ceramics |
Cited By (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN104529050A (en) * | 2014-11-25 | 2015-04-22 | 浙江浙牌科技有限公司 | Efficient rural sewage purification apparatus |
CN104529050B (en) * | 2014-11-25 | 2016-11-30 | 浙江浙牌科技有限公司 | Efficiently country sewage purifier |
Also Published As
Publication number | Publication date |
---|---|
JP4019209B2 (en) | 2007-12-12 |
JP2002045878A (en) | 2002-02-12 |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
JP2875765B2 (en) | High-concentration wastewater treatment equipment | |
CN106277558A (en) | A kind of integrate process for removing nitrogen and phosphor from sewage and the device that physical biochemistry filters | |
CN109574392A (en) | A kind of integrated apparatus and method purifying black-odor riverway sewage | |
KR102170601B1 (en) | Advanced sewage and wastewater separation membrane device using low temperature plasma | |
CN111333271B (en) | Sewage treatment system, application thereof and sewage treatment method | |
JP2004209465A (en) | Wetland type water purification system | |
CN104098179B (en) | Assembly type aerobic-anaerobic immobilized microorganism sewage-treatment plant | |
CN206607128U (en) | A kind of river sewage processing unit based on water treatment agent and ceramic membrane | |
WO2003053866A1 (en) | Water clarifying system | |
CN104085993B (en) | A kind of constructed wetland device | |
KR200328487Y1 (en) | natural purification system using functional ceramic | |
CN104118941A (en) | Efficient nitrogen and phosphorus removal artificial wetland device | |
KR100424289B1 (en) | nature equilibrium vertical flow type artificial swamp facility for purging contaminate matter away contaminated water | |
KR100443314B1 (en) | Structure for artificial marshy land and sewage treatment device using thereof | |
KR100381901B1 (en) | The treatment system of discharging water in the treatment equipment of sewage and serious contaminated rivers water utilizing the contact oxidation method | |
CN104086058A (en) | Aerobiotic/anaerobic artificial wetland system | |
KR100399294B1 (en) | River sewage purification apparatus constructed in the waters edge | |
CN104085999A (en) | Assembled constructed wetland system | |
KR20210048388A (en) | integrated effluent vertical filtering apparatus | |
JP3087366U (en) | Livestock urine and barn wastewater purification equipment | |
CN104086055A (en) | Assembly type sewage treatment device | |
CN110453941B (en) | Toilet system capable of automatically treating dirt and purifying water | |
CN104118942B (en) | A kind of sewage treatment process | |
EP1084083A2 (en) | Filtering plant for waste water | |
CN210764567U (en) | Biochemical treatment device for micro light bed |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
AK | Designated states |
Kind code of ref document: A1 Designated state(s): AE AG AL AM AT AU AZ BA BB BG BR BY BZ CA CH CN CO CR CU CZ DE DK DM DZ EC EE ES FI GB GD GE GH GM HR HU ID IL IN IS KE KG KP KR KZ LC LK LR LS LT LU LV MA MD MG MK MN MW MX MZ NO NZ PH PL PT RO RU SD SE SG SI SK SL TJ TM TR TT TZ UA UG US UZ VN YU ZA ZW |
|
AL | Designated countries for regional patents |
Kind code of ref document: A1 Designated state(s): GH GM KE LS MW MZ SD SL SZ TZ UG ZM ZW AM AZ BY KG KZ MD RU TJ TM AT BE CH CY DE DK ES FI FR GB GR IE IT LU MC NL PT SE TR BF BJ CF CG CI CM GA GN GQ GW ML MR NE SN TD TG |
|
121 | Ep: the epo has been informed by wipo that ep was designated in this application | ||
122 | Ep: pct application non-entry in european phase |