JP3268876B2 - How to purify river or lake water - Google Patents
How to purify river or lake waterInfo
- Publication number
- JP3268876B2 JP3268876B2 JP6470493A JP6470493A JP3268876B2 JP 3268876 B2 JP3268876 B2 JP 3268876B2 JP 6470493 A JP6470493 A JP 6470493A JP 6470493 A JP6470493 A JP 6470493A JP 3268876 B2 JP3268876 B2 JP 3268876B2
- Authority
- JP
- Japan
- Prior art keywords
- water
- lake
- ultrafiltration membrane
- hollow fiber
- activated carbon
- 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.)
- Expired - Fee Related
Links
Classifications
-
- 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
Description
【0001】[0001]
【産業上の利用分野】本発明は、河川水や湖沼水の浄化
方法に関するものである。さらに詳しくは、中空糸型限
外濾過膜と生物活性炭により処理することを特徴とする
塩素未処理河川水や湖沼水の浄化方法に関する。BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method for purifying river water and lake water. More specifically, the present invention relates to a method for purifying unchlorinated river water and lake water, which is characterized by treating with a hollow fiber type ultrafiltration membrane and biological activated carbon.
【0002】[0002]
【従来の技術】従来、河川水や湖沼水から水道水を得る
ための浄水処理システムとしては、前塩素処理−凝集沈
澱−砂濾過−塩素滅菌工程を経るのが一般的である。こ
のような工程を実現するためには、凝集池、沈澱池、砂
濾過池、塩素滅菌設備等が必要であり、大きな設置スペ
ースを要するという問題点がある。加えて、近年河川等
の水源の汚濁が進んでいるため、これに対する新しい高
度浄水処理システムの開発が求められ、上記工程に活性
炭処理システムやオゾン処理システムを付加することが
提案されている。2. Description of the Related Art Conventionally, a water purification system for obtaining tap water from river water or lake water generally involves a pre-chlorination-coagulation-sedimentation-sand filtration-chlorine sterilization process. In order to realize such a process, a coagulation pond, a sedimentation pond, a sand filtration pond, a chlorine sterilization facility, and the like are required, and there is a problem that a large installation space is required. In addition, since the pollution of water sources such as rivers has been increasing in recent years, development of a new advanced water purification treatment system has been required, and it has been proposed to add an activated carbon treatment system or an ozone treatment system to the above process.
【0003】しかしながら、従来の浄水処理システムに
上述した活性炭処理システムやオゾン処理システムを付
加することは、設置スペースの更なる増加を招き、複雑
な計測制御技術をも必要とする新たな問題点が生ずる。However, the addition of the above-mentioned activated carbon treatment system and ozone treatment system to the conventional water purification treatment system causes a further increase in installation space and a new problem requiring complicated measurement control technology. Occurs.
【0004】また、前記前塩素処理は凝集沈澱工程より
前で行われ、その目的は河川水や湖沼水に含まれる溶解
性の鉄、マンガン、アンモニア等を塩素の作用により酸
化し、さらに凝集沈澱で沈澱させて除去することにあ
る。しかし、河川水や湖沼水に含まれる微量有機物が前
塩素処理の塩素により酸化されて、発ガン性を有するト
リハロメタン等の有害物質が生成するという問題があっ
た。そこで、前塩素処理を行わないで河川水や湖沼水を
浄化する方法が求められていた。[0004] The pre-chlorination is performed before the coagulation sedimentation step. The purpose of the pre-chlorination is to oxidize soluble iron, manganese, ammonia and the like contained in river water or lake water by the action of chlorine, and further to coagulate sedimentation. To remove by precipitation. However, there has been a problem that trace organic substances contained in river water and lake water are oxidized by chlorine in pre-chlorination, and harmful substances such as trihalomethane having carcinogenicity are generated. Therefore, a method of purifying river water and lake water without performing pre-chlorination has been required.
【0005】一方、限外濾過膜と呼ばれる新しい材料の
利用技術が多方面にわたって提案されており、水道水を
得るための前記設備設置スペースや水源の汚濁に対して
の問題に対処できる中空糸型限外濾過膜モジュールを使
用した浄水処理システムの実用化が検討されている。[0005] On the other hand, techniques for utilizing a new material called an ultrafiltration membrane have been proposed in various fields, and a hollow fiber type capable of coping with the problems of the installation space for obtaining tap water and contamination of a water source. Practical application of a water purification system using an ultrafiltration membrane module is being studied.
【0006】なお、水の汚染度が相当に大きく変動する
場合や汚染物質の組成が広範に変化する場合に適する地
下水及び排水の浄化方法として、特開平4−22709
9号公報には被処理水を生物学的処理工程と活性炭吸着
との間で膜分離処理にかける方法が開示されている。As a method of purifying groundwater and wastewater suitable for a case where the degree of contamination of water fluctuates considerably or a case where the composition of pollutants varies widely, Japanese Patent Laid-Open No. 22709/1992 is disclosed.
No. 9 discloses a method of subjecting water to be treated to membrane separation between a biological treatment step and activated carbon adsorption.
【0007】[0007]
【発明が解決しようとする課題】河川水または湖沼水を
中空糸型限外濾過膜を用いて処理する際、前記のトリハ
ロメタンの生成を防ぐ理由から前塩素処理を行わずに限
外濾過膜処理を行うと、前記溶解性の鉄、マンガン、ア
ンモニア等は限外濾過膜により除去されず、また限外瀘
過膜処理では低分子有機物質は十分に除去されないの
で、これらが最終処理段階において殺菌の目的で添加さ
れる塩素や次亜塩素酸ナトリウム等の制御を困難にする
だけでなく、これらの添加により不溶性物質やトリハロ
メタン等を生成し、クロラミンの生成によってカルキ臭
が強まり、水道水としては好ましくないものとなること
がある。When treating river water or lake water using a hollow fiber type ultrafiltration membrane, an ultrafiltration membrane treatment is carried out without pre-chlorination for the purpose of preventing the formation of trihalomethane. In this case, the soluble iron, manganese, ammonia and the like are not removed by the ultrafiltration membrane, and the low molecular weight organic substances are not sufficiently removed by the ultrafiltration membrane treatment. Not only makes it difficult to control chlorine and sodium hypochlorite, etc. added for the purpose of the above, but also produces insoluble substances and trihalomethane, etc., and increases the odor of chlorine due to the production of chloramine. May be undesirable.
【0008】[0008]
【課題を解決するための手段】本発明者らはトリハロメ
タンの生成を防止し、かつ高度浄化が達成できる中空糸
型限外濾過膜による河川水または湖沼水の処理に関する
前記課題について鋭意検討した結果、中空糸型限外濾過
膜と生物活性炭処理を組み合わせることにより、前記課
題が容易に解決できるとの知見を得て、本発明を完成さ
せた。DISCLOSURE OF THE INVENTION The present inventors have conducted intensive studies on the above-mentioned problems relating to the treatment of river water or lake water using a hollow fiber type ultrafiltration membrane capable of preventing the generation of trihalomethane and achieving high purification. The present inventors have found that the above problem can be easily solved by combining a hollow fiber type ultrafiltration membrane with a biological activated carbon treatment, and completed the present invention.
【0009】すなわち、本発明は、塩素未処理の河川水
または湖沼水を中空糸型限外濾過膜を用いて処理し、次
いであらかじめ細菌を含む液または限外濾過膜で処理さ
れていない河川水または湖沼水を流入させた生物活性炭
を用いて処理することを特徴とする河川水または湖沼水
の浄化方法である。That is, the present invention relates to a chlorine-free river water.
Alternatively, treat lake water using a hollow fiber type ultrafiltration membrane ,
Previously treated with bacteria-containing liquid or ultrafiltration membrane
A method for purifying river water or lake water , characterized by treating with untreated river water or lake water using biological activated carbon.
【0010】本発明による浄化方法を採用した河川水ま
たは湖沼水の処理工程図を図1に示す。図1は主要工程
のみを示したものである。図1において1は粗大浮遊物
を除く濾過装置や砂などを除く沈砂池などの前処理工程
であり、2は中空糸型限外濾過膜を用いた処理工程であ
り、3は生物活性炭処理工程であり、4は殺菌工程であ
る。また、図2に示すように生物活性炭処理工程と中空
糸型限外濾過膜を用いた処理工程の位置が入れ替わった
工程を採用することは本発明には含まない。ただし、図
1には示されていないが、あらかじめ一時的に河川水ま
たは湖沼水等の表流水を活性炭処理工程に通して生物を
付着させた後、中空糸型限外濾過膜で処理し、次いで、
処理水を活性炭処理工程に通すことは本発明に含まれ
る。 [0010] River water using the purification method according to the present invention.
FIG. 1 shows a process diagram of the treatment of lake or lake water . FIG. 1 shows only the main steps. In FIG. 1, reference numeral 1 denotes a pretreatment step for a filtration device for removing coarse suspended matters and a sand basin for removing sand, etc., 2 a treatment step using a hollow fiber type ultrafiltration membrane, and 3 a biological activated carbon treatment step. And 4 is a sterilization step. In addition, the present invention does not include a step in which the positions of the biological activated carbon treatment step and the treatment step using the hollow fiber type ultrafiltration membrane are switched as shown in FIG . However,
Although not shown in Fig. 1, the river water is temporarily
Or surface water such as lake water through an activated carbon treatment process
After being attached, treated with a hollow fiber type ultrafiltration membrane,
Passing the treated water through the activated carbon treatment step is included in the present invention.
You.
【0011】本発明の生物活性炭処理工程に使用される
生物活性炭濾過装置は、公知のものをそのまま採用する
ことができる。細菌類を高濃度に捕捉・固定するため、
活性炭と共にセルロースなどの濾過助剤担体を充填して
もよい。活性炭に吸着固定される細菌類としては特に限
定されないが、代表的なものとしてはアンモニアを酸化
する際に酸素を要求するアンモニア酸化細菌が挙げられ
る。通常有機物の存在する河川水または湖沼水を活性炭
処理することにより、表流水中に存在する細菌類が活性
炭に捕捉・固定化され、活性炭は次第に生物活性炭に変
化する。図1に示す本発明の好ましい態様においては、
中空糸型限外瀘過膜を通過後の河川水または湖沼水を生
物活性炭により処理するので、細菌類の固定が通常進み
にくい。その場合は、別途細菌を含んだ液を活性炭層に
流入させるか、あるいは中空糸型限外瀘過膜で処理して
いない河川水または湖沼水を予め所定時間活性炭濾過装
置に流過させ、細菌が固定された段階で、本発明の処理
工程としての使用を始めることもできる。As the biological activated carbon filtration device used in the biological activated carbon treatment step of the present invention, a known apparatus can be used as it is. To capture and fix bacteria in high concentration,
A filter aid carrier such as cellulose may be filled together with the activated carbon. Bacteria adsorbed and fixed on activated carbon are not particularly limited, but typical examples include ammonia-oxidizing bacteria that require oxygen when oxidizing ammonia. Activated carbon treatment of river water or lake water containing organic matter usually causes bacteria existing in surface water to be captured and immobilized on activated carbon, and the activated carbon is gradually changed to biological activated carbon. In a preferred embodiment of the present invention shown in FIG.
Since the river water or lake water after passing through the hollow fiber type ultrafiltration membrane is treated with biological activated carbon, the fixation of bacteria is usually difficult to proceed. In that case, a liquid containing bacteria is separately flowed into the activated carbon layer, or river water or lake water not treated with the hollow fiber type ultrafiltration membrane is allowed to flow through the activated carbon filtration device for a predetermined time in advance, and the bacteria are removed. When is fixed, use as a processing step of the present invention can be started.
【0012】生物活性炭濾過装置は通常固定床方式の処
理塔であり、上から被処理水を注入し、下部から処理水
を抜き出す。使用を続けるに従い、増殖した細菌や細菌
が分泌する粘性物質等により圧力損失が増すことがある
ので、必要に応じて定期的に洗浄を行うことが望まし
い。The biological activated carbon filtration apparatus is usually a fixed-bed type treatment tower, in which water to be treated is injected from above and treated water is extracted from below. As the use continues, the pressure loss may increase due to the proliferated bacteria and viscous substances secreted by the bacteria. Therefore, it is desirable to periodically wash as necessary.
【0013】本発明に使用する中空糸型限外濾過膜によ
る河川水または湖沼水の処理工程については、特に限定
されない。好ましい工程例を挙げれば、図3に示すよう
な中空糸型濾過膜モジュールを用い、通常運転時はクロ
スフローを行いながら原水を全量濾過し、間欠的に逆洗
を行うものを挙げることができるものであり、原水から
の回収率は90%以上99%以下で運転することが可能
である。図3の工程には逆止弁10、ポンプ11、中空
糸型限外濾過膜モジュール12、透過水自動弁13、洗
浄水排出自動弁14の構成に加えて、透過水を蓄積する
ための透過水タンク17、蓄積された透過水を中空糸型
限外濾過膜モジュール12の出口側に戻して逆洗を行う
ためのポンプ18、逆洗自動弁19、洗浄水排出経路1
5とを設けている。なお洗浄水排出経路15はポンプ1
1と中空糸型限外瀘過膜モジュール12の間に設けても
よい。The process for treating river water or lake water using the hollow fiber type ultrafiltration membrane used in the present invention is not particularly limited. A preferred example of the process includes a process in which a raw fiber is entirely filtered while performing a cross flow during a normal operation using a hollow fiber type filtration membrane module as shown in FIG. 3, and intermittent backwashing is performed. It can be operated at a recovery rate of 90% or more and 99% or less from raw water. In the process of FIG. 3, in addition to the check valve 10, pump 11, hollow fiber type ultrafiltration membrane module 12, automatic permeated water valve 13, and automatic valve 14 for washing water discharge, permeation for accumulating permeated water is performed. A water tank 17, a pump 18 for returning the accumulated permeated water to the outlet side of the hollow fiber type ultrafiltration membrane module 12, and performing backwashing, a backwash automatic valve 19, and a washing water discharge path 1
5 are provided. The washing water discharge path 15 is the pump 1
1 and the hollow fiber type ultrafiltration membrane module 12.
【0014】この中空糸型限外濾過膜処理工程の運転は
次のようにして行われる。通常運転に際しては、透過水
自動弁13を開、濃縮水排出自動弁14、逆洗自動弁1
9は共に閉とし、ポンプ18を停止状態におく。このよ
うにして、逆止弁10を経て導入された河川水または湖
沼水の原水は、ポンプ11により昇圧されて中空糸型限
外濾過膜モジュール12に供給される。中空糸型限外濾
過膜モジュール12では、限外濾過膜の濾過作用により
濁質成分を除去した透過水を、透過水自動弁13を通し
て透過水タンク17に蓄積する。なお、この通常運転の
間、循環経路16を通して原水の流入量に対してゼロを
越え6倍以下程度の量のクロスフローが行われるが、透
過水量は原水量に等しい。The operation of the hollow fiber type ultrafiltration membrane treatment step is performed as follows. During normal operation, the permeated water automatic valve 13 is opened, the concentrated water discharge automatic valve 14, the backwash automatic valve 1
9 are both closed, and the pump 18 is stopped. In this way, the river water or lake introduced through the check valve 10
The raw water of the swamp is pressurized by a pump 11 and supplied to a hollow fiber type ultrafiltration membrane module 12. In the hollow fiber type ultrafiltration membrane module 12, the permeated water from which the turbid components have been removed by the filtration action of the ultrafiltration membrane is accumulated in the permeated water tank 17 through the permeated water automatic valve 13. During the normal operation, a crossflow of more than zero and about six times or less with respect to the inflow amount of the raw water through the circulation path 16 is performed, but the permeated water amount is equal to the raw water amount.
【0015】逆洗は、例えば30分ないし1時間程度の
定時間間隔で30〜60秒の間行われる。この場合、原
水の供給を停止すると共に透過水自動弁13を閉、洗浄
水排出自動弁14、逆洗自動弁19は共に開とし、ポン
プ11を停止状態、ポンプ18を運転する。このように
して、透過水タンク17に蓄積された透過水の一部を利
用して中空糸型限外濾過膜モジュール12に対する逆洗
が行われ、逆洗により中空糸膜の内表面からはぎとられ
た濁質成分は、洗浄水として洗浄水排出経路15により
洗浄水排出自動弁14を通してシステム外に排出され
る。逆洗水量は洗浄水排出水量に等しくなる。The backwashing is performed at regular time intervals of, for example, about 30 minutes to 1 hour for 30 to 60 seconds. In this case, the supply of raw water is stopped, the automatic permeated water valve 13 is closed, the automatic cleaning water discharge valve 14 and the automatic backwash valve 19 are both opened, the pump 11 is stopped, and the pump 18 is operated. In this manner, the hollow fiber ultrafiltration membrane module 12 is backwashed by utilizing a part of the permeated water accumulated in the permeated water tank 17, and is stripped from the inner surface of the hollow fiber membrane by the backwash. The turbid component is discharged out of the system through a cleaning water discharge automatic valve 14 through a cleaning water discharge path 15 as cleaning water. The backwash water amount is equal to the washwater discharge water amount.
【0016】なお、前記濾過膜モジュールはその膜材質
が酢酸セルロースであるのが最適であり、また中空糸膜
の内側に原水を供給する内圧方式が好ましい。The filtration membrane module is most preferably made of cellulose acetate, and an internal pressure system for supplying raw water to the inside of the hollow fiber membrane is preferred.
【0017】また、前記逆洗時の前記所定圧は,前記通
常運転時の運転圧の実質上1.0倍以上3倍以下とする
ことが望ましい。さらに好ましくは、1.3倍以上であ
る。Preferably, the predetermined pressure at the time of the backwash is substantially 1.0 to 3 times the operating pressure at the time of the normal operation. More preferably, it is 1.3 times or more.
【0018】逆洗に用いられる水は、膜透過水であって
もよく、あるいはまた最終的に得られる水道水等の清浄
水を別途供給してもよいが、前者であることが好まし
い。逆洗はあらかじめ定められた周期による時間制御で
も圧力制御であってもよく、圧力制御の場合は運転圧の
実質上1.3倍以上で動作する様にすればよい。前記の
処理工程によれば透過水の流量をP、濃縮泥とともに排
出される水量をCとすると、回収率は100×P/(P
+C)(%)で表され、回収率95%以上99%以下で
運転することが可能である。The water used for backwashing may be membrane permeated water, or purified water such as tap water finally obtained may be separately supplied, but the former is preferred. The backwashing may be time control or pressure control at a predetermined cycle. In the case of pressure control, the backwash may be operated at substantially 1.3 times or more the operating pressure. Assuming that the flow rate of the permeated water is P and the amount of water discharged together with the thickened mud is C according to the above-mentioned treatment step, the recovery rate is 100 × P / (P
+ C) (%), and can be operated at a recovery rate of 95% or more and 99% or less.
【0019】図1に示す本発明の処理方法においては、
塩素未処理河川水または湖沼水中の溶解性の鉄、マンガ
ン、アンモニア、更には分子量1,000以下の有機物
等は中空糸型限外瀘過膜によって除去されないが、生物
活性炭処理工程で除去されることとなる。これにより、
従来前塩素処理により不溶性とし、沈澱凝集工程で除去
していたこれらの成分を前塩素処理すること無く効果的
に除去することが可能となった。本発明の浄化方法によ
れば、得られる浄化水は濁度、TOC(全有機炭素)、
色度にも優れる。しかも、有機物が比較的多量に存在す
る過程で塩素処理をしないので、従来から水道水に混入
するとして問題化していたトリハロメタンの発生も防止
できる。In the processing method of the present invention shown in FIG.
Soluble iron chlorine untreated river water or lake in water, manganese, ammonia, even in such a molecular weight of 1,000 or less organic matter is not removed by hollow fiber ultrafiltration membrane is removed by the biological activated carbon treatment process The Rukoto. This allows
These components, which were conventionally rendered insoluble by pre-chlorination and removed in the precipitation and aggregation step, can now be effectively removed without pre-chlorination. According to the purification method of the present invention, the obtained purified water has turbidity, TOC (total organic carbon),
Excellent chromaticity. In addition, since chlorination is not performed in the course of the presence of a relatively large amount of organic substances, the generation of trihalomethane, which has conventionally been considered as a problem when mixed into tap water, can be prevented.
【0020】[0020]
【発明の効果】以上説明したように、本発明による浄化
方法により、中空糸型限外瀘過膜と生物活性炭処理を用
いる処理により、前塩素処理を行うことなく有効に河川
水または湖沼水中の濁物および溶解性の成分を除去する
ことが可能となった。しかも前塩素処理をしないので、
発ガン性のトリハロメタンなどの発生も少なく、水道水
などに適する高度に浄化された処理水が得られる。As described above, according to the present invention, the purification method according to the present invention, by treatment with hollow fiber type ultrafiltration membrane and biological activated carbon treatment, effectively river without performing prechlorination
Pollution product and solubility of the components in water or lake in water it becomes possible to remove. And because it doesn't do pre-chlorination,
Highly purified treated water suitable for tap water and the like is obtained with little generation of carcinogenic trihalomethane.
【図1】 本発明による浄化方法を採用した河川水また
は湖沼水の処理工程の一例を示す図である。FIG. 1 shows a river water or a river which adopts the purification method according to the present invention.
FIG. 3 is a diagram showing an example of a lake water treatment process.
【図2】 本発明による浄化方法には含まれない処理工
程の例を示す図である。FIG. 2 is a processing step not included in the purification method according to the present invention.
Is a diagram illustrating an example of a degree.
【図3】 本発明で使用する中空糸型限外濾過膜モジュ
ールの構成・運転方法を説明する工程図である。FIG. 3 is a process diagram illustrating a configuration and an operation method of a hollow fiber type ultrafiltration membrane module used in the present invention.
───────────────────────────────────────────────────── フロントページの続き (51)Int.Cl.7 識別記号 FI C02F 1/44 C02F 1/44 H ──────────────────────────────────────────────────続 き Continued on the front page (51) Int.Cl. 7 Identification code FI C02F 1/44 C02F 1/44 H
Claims (4)
糸型限外濾過膜を用いて処理し、次いであらかじめ細菌
を含む液または限外濾過膜で処理されていない河川水ま
たは湖沼水を流入させた生物活性炭を用いて処理するこ
とを特徴とする河川水または湖沼水の浄化方法。Claims 1. A chlorine-free river water or lake water is treated using a hollow fiber type ultrafiltration membrane.
Or river water not treated with an ultrafiltration membrane
Or a method for purifying river water or lake water , wherein the treatment is performed using biological activated carbon into which lake water or lake water has flowed .
化方法において、前記中空糸型限外濾過膜を用いる処理
が酢酸セルロースを膜材質とする内圧方式中空糸型限外
濾過膜モジュールを用いる処理である河川水または湖沼
水の浄化方法。2. The method of purifying river water or lake water according to claim 1 , wherein the treatment using the hollow fiber type ultrafiltration membrane includes an internal pressure type hollow fiber type ultrafiltration membrane module using cellulose acetate as a membrane material. The river water or lake that is the treatment used
Water purification method.
化方法において、前記生物活性炭を用いる処理がアンモ
ニア酸化細菌を固定化した生物活性炭濾過装置を用いる
処理である河川水または湖沼水の浄化方法。3. A method of purifying river water or lake water according to claim 1, purifying river water or lake water treatment using the biological activated carbon is a treatment with biological activated carbon filtration device immobilized with ammonium oxidizing bacteria Method.
3のいずれかに記載の河川水または湖沼水の浄化方法。 4. The method according to claim 1, further comprising treating in a sterilization step.
3. The method for purifying river water or lake water according to any one of 3.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP6470493A JP3268876B2 (en) | 1993-03-01 | 1993-03-01 | How to purify river or lake water |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP6470493A JP3268876B2 (en) | 1993-03-01 | 1993-03-01 | How to purify river or lake water |
Publications (2)
Publication Number | Publication Date |
---|---|
JPH06254595A JPH06254595A (en) | 1994-09-13 |
JP3268876B2 true JP3268876B2 (en) | 2002-03-25 |
Family
ID=13265806
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP6470493A Expired - Fee Related JP3268876B2 (en) | 1993-03-01 | 1993-03-01 | How to purify river or lake water |
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Country | Link |
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JP (1) | JP3268876B2 (en) |
Families Citing this family (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP4804149B2 (en) * | 2006-01-06 | 2011-11-02 | ダイセン・メンブレン・システムズ株式会社 | Filtration treatment method for washing waste water of plants containing vegetables and / or fruits |
JP6861478B2 (en) * | 2015-08-17 | 2021-04-21 | 三菱ケミカルアクア・ソリューションズ株式会社 | Treatment method and treatment equipment for humic acid-containing wastewater |
CN106045135A (en) * | 2016-08-11 | 2016-10-26 | 太平洋水处理工程有限公司 | High-efficiency emergency safe water treatment apparatus and technology thereof |
Family Cites Families (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPS6068006A (en) * | 1983-09-24 | 1985-04-18 | Kuraray Co Ltd | Filtration apparatus |
JPH01242189A (en) * | 1988-03-22 | 1989-09-27 | Mitsubishi Heavy Ind Ltd | Waste water treating apparatus |
JP3128249B2 (en) * | 1991-01-28 | 2001-01-29 | 旭化成工業株式会社 | Wash water treatment method |
-
1993
- 1993-03-01 JP JP6470493A patent/JP3268876B2/en not_active Expired - Fee Related
Also Published As
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JPH06254595A (en) | 1994-09-13 |
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