JP2004267887A - Method and apparatus for treating water cleaning membrane - Google Patents

Method and apparatus for treating water cleaning membrane Download PDF

Info

Publication number
JP2004267887A
JP2004267887A JP2003061038A JP2003061038A JP2004267887A JP 2004267887 A JP2004267887 A JP 2004267887A JP 2003061038 A JP2003061038 A JP 2003061038A JP 2003061038 A JP2003061038 A JP 2003061038A JP 2004267887 A JP2004267887 A JP 2004267887A
Authority
JP
Japan
Prior art keywords
membrane
treatment device
water
membrane treatment
raw water
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.)
Granted
Application number
JP2003061038A
Other languages
Japanese (ja)
Other versions
JP4071134B2 (en
Inventor
Torataro Minegishi
寅太郎 峯岸
Shoichi Suda
昇一 須田
Yoshihiko Mori
吉彦 森
Takashi Ogawa
高史 小川
Kenzo Sugaya
謙三 菅谷
Hideyoshi Matsubara
秀吉 松原
Yoshinori Masaoka
喜則 正岡
Toshibumi Mukuhashi
俊文 椋橋
Keizo Murata
圭三 村田
Hideji Yamada
秀治 山田
Teruhiro Kitazawa
照啓 北沢
Yoichi Hirose
洋一 広瀬
Yasuhiro Nakamura
康宏 中村
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Sanki Engineering Co Ltd
Ishigaki Co Ltd
JFE Engineering Corp
Asahi Kasei Chemicals Corp
Hitachi Plant Technologies Ltd
Sumitomo Heavy Industries Ltd
Fuso Kensetsu Kogyo KK
Original Assignee
Sanki Engineering Co Ltd
Ishigaki Co Ltd
JFE Engineering Corp
Asahi Kasei Chemicals Corp
Hitachi Plant Technologies Ltd
Sumitomo Heavy Industries Ltd
Fuso Kensetsu Kogyo KK
Priority date (The priority date 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 date listed.)
Filing date
Publication date
Application filed by Sanki Engineering Co Ltd, Ishigaki Co Ltd, JFE Engineering Corp, Asahi Kasei Chemicals Corp, Hitachi Plant Technologies Ltd, Sumitomo Heavy Industries Ltd, Fuso Kensetsu Kogyo KK filed Critical Sanki Engineering Co Ltd
Priority to JP2003061038A priority Critical patent/JP4071134B2/en
Publication of JP2004267887A publication Critical patent/JP2004267887A/en
Application granted granted Critical
Publication of JP4071134B2 publication Critical patent/JP4071134B2/en
Anticipated expiration legal-status Critical
Expired - Lifetime legal-status Critical Current

Links

Images

Landscapes

  • Separation Using Semi-Permeable Membranes (AREA)
  • Treatment Of Sludge (AREA)

Abstract

<P>PROBLEM TO BE SOLVED: To concentrate physical washing wastewater produced from a membrane treatment device until the concentration of sludge becomes almost constant throughout a year without adding a flocculant, to set the cleaned water recovery rate of the whole of a system to 99.9% or above, to increase the dehydration speed in a dehydrator and to reduce the evil related to the effective utilization of dehydrated sludge. <P>SOLUTION: This water cleaning membrane treatment apparatus is equipped with a water arriving well 1 for receiving raw water taken in from rivers or the like, a pretreatment device 2 for pretreating the raw water from the water arriving well 1, a first membrane treatment device 3 for subjecting the raw water pretreated by the pretreatment device 2 to membrane filtering treatment and a second membrane treatment device 4 for further subjecting the physical washing wastewater from the first membrane treatment device 3 to membrane filtering treatment and further equipped with a sterilizing treatment device 7 for sterilizing the membrane filtered water from the first membrane filtering treatment device 3, a concentrator 5 for concentrating the physical washing wastewater from the second membrane filtering treatment device 4 and the dehydrator 6 for dehydrating the sludge concentrated by the concentrator 5. <P>COPYRIGHT: (C)2004,JPO&NCIPI

Description

【0001】
【発明の属する技術分野】
本発明は、浄水膜処理方法および装置、特に、膜利用型浄水場において、膜処理装置から排出される物理洗浄排水を効率的に処理して、浄水回収率を向上させることができる浄水膜処理方法および装置に関するものである。
【0002】
【従来の技術】
膜ろ過処理を利用した従来の浄水処理を、図面を参照しながら説明する。
【0003】
図4は、膜ろ過処理を行っている浄水場における従来処理フローを示す図である。
【0004】
同図の浄水処理では、河川等から取水した原水を着水井20で受水した後、原水中の夾雑物を除去するための前処理装置21へ導き、膜処理装置22にて原水中の懸濁成分、病原性原虫類および細菌類を除去する。膜処理装置22より得られた膜ろ過水は、滅菌処理装置31により塩素消毒を行って、水道水として供給される。その際の浄水回収率は、90〜95%程度である。膜処理装置22において、定期的に物理洗浄操作が実施されており、洗浄によって排出された物理洗浄排水は、排水池23へ送られ、汚泥と上澄水とに分離される。汚泥は、濃縮槽24において重力により沈降濃縮されて脱水機25に供給される。濃縮槽24からの上澄水は、排水池23からの上澄水と共に回収率を向上させる目的により着水井20へ返送される。
【0005】
上記構成の従来方式では、原水濁度が高い場合には、物理洗浄排水中の固形物濃度も高くなるため、濃縮槽24において重力による沈降濃縮を適用することが可能である。しかしながら、原水濁度が低い場合には、物理洗浄排水中の固形物濃度が低くなるため、汚泥の沈降速度が遅くなり、濃縮槽24において重力による沈降濃縮を適用することが困難となる。
【0006】
この問題を解決するために、濃縮槽24において凝集剤としてポリ塩化アルミニウム(PAC)や高分子凝集剤を使用して汚泥の沈降性を向上させる必要がある。
【0007】
また、図5における標準的な膜利用型浄水処理では、河川等から取水した原水を着水井20で受水した後、原水中の夾雑物を除去するために、ポリ塩化アルミニウム(PAC)等の無機系凝集剤26を添加して凝集混和装置27に導き、膜処理装置28に圧入して膜ろ過を行い、原水中の懸濁成分、病原性原虫類および細菌類を除去する。膜処理装置28より得られた膜ろ過水は、滅菌処理装置31によって塩素消毒を行って、水道水として供給される。その際の浄水回収率は、95〜98%程度である。膜処理装置28では、定期的に物理洗浄操作が実施されており、洗浄によって排出された物理洗浄排水はシックナー29へ導かれ、濃縮汚泥と上澄水とに分離される。濃縮汚泥は、脱水機30に供給され、上澄水は、回収率を向上させる目的により着水井20へ返送される。
【0008】
【発明が解決しようとする課題】
以上のように、従来方式の図4および図5において、凝集剤が添加される場合が一般的である。凝集剤を添加した濃縮汚泥が脱水機25、30に投入された場合、脱水機25、30における汚泥の脱水速度が大幅に減少し、脱水機の必要台数が増加するという問題がある。また、脱水汚泥中にアルミニウムを含む場合には、その有効利用が困難であるという問題がある。
【0009】
従って、本発明は、上記のような課題を克服すべく鋭意研究の結果完成されたものであって、凝集剤を添加することなく膜処理装置から発生する物理洗浄排水を年間を通じてほぼ一定した汚泥濃度まで濃縮すると共に、システム全体の浄水回収率を99.9%以上とし、脱水機における脱水速度を向上させ、脱水汚泥の有効利用に係る弊害を少なくすることができる浄水膜処理方法および装置を提供することを目的としている。
【0010】
【課題を解決するための手段】
本発明は、上記課題を解決するためになされたものであり、下記を特徴とするものである。
【0011】
請求項1に記載された発明は、河川等から取水した原水をこれに凝集剤を添加することなく膜ろ過処理して水道水として利用する際に、原水を一次膜ろ過処理し、次いで、一次膜ろ過処理した後の物理洗浄排水を二次膜ろ過処理し、そして、二次膜ろ過処理した後の物理洗浄排水を濃縮することに特徴を有するものである。
【0012】
請求項2に記載された発明は、前記二次膜ろ過処理した後の物理洗浄排水を、汚泥の固形物濃度が1から6%となるまで濃縮することに特徴を有するものである。
【0013】
請求項3に記載された発明は、河川等から取水した原水をこれに凝集剤を添加することなく膜処理装置により膜ろ過処理して水道水として利用する浄水膜処理装置において、原水を一次膜ろ過する第1膜処理装置と、前記第1膜処理装置からの物理洗浄排水を二次膜ろ過する第2膜処理装置とが設けられていることに特徴を有するものである。
【0014】
請求項4に記載された発明は、河川等から取水した原水を受水する着水井と、前記着水井からの原水を前処理する前処理装置と、前記前処理装置により前処理された原水を膜ろ過処理する第1膜処理装置と、前記第1膜処理装置からの物理洗浄排水をさらに膜ろ過する第2膜処理装置と、前記第1膜処理装置からの膜ろ過水を滅菌処理する滅菌処理装置と、前記第2膜処理装置からの物理洗浄排水を濃縮する濃縮装置と、前記濃縮装置により濃縮された汚泥を脱水する脱水機とを備えていることに特徴を有するものである。
【0015】
請求項5に記載された発明は、前記第2膜処理装置からの膜ろ過水は、前記滅菌処理装置に送られ、前記濃縮装置からの処理水は、前記第2膜処理装置に返送されることに特徴を有するものである。
【0016】
請求項6に記載された発明は、前記第2膜処理装置からの膜ろ過水は、前記第1膜処理装置に返送され、前記濃縮装置からの処理水は、前記第2膜処理装置に返送されることに特徴を有するものである。
【0017】
請求項7に記載された発明は、前記濃縮装置は、膜濃縮装置からなり、前記膜濃縮装置からの膜ろ過水は、前記滅菌処理装置に送られ、前記第2膜処理装置からの膜ろ過水は、前記滅菌処理装置に送られることに特徴を有するものである。
【0018】
【発明の実施の形態】
以下、本発明の浄水膜処理方法を実施するための浄水膜処理装置の一実施態様を、図面を参照しながら説明する。
【0019】
図1は、本発明の浄水膜処理装置による処理フローを示す図である。
【0020】
図1において、1は、主として、河川等から取水した原水を受水する着水井、2は、原水中の夾雑物を除去するための前処理装置、3は、原水中の懸濁成分、病原性原虫類および細菌類を除去するための第1膜処理装置、4は、第1膜処理装置3において定期的に実施する物理洗浄操作により排出された物理洗浄排水中の懸濁成分、病原性原虫類および細菌類を除去するための第2膜処理装置、5は、第2膜処理装置4において定期的に実施する物理洗浄操作により排出された物理洗浄排水を濃縮するための濃縮装置、6は、濃縮装置5において濃縮された汚泥を脱水する脱水機、そして、7は、第1膜処理装置3および第2膜処理装置4からの膜ろ過水を滅菌処理するための滅菌処理装置である。
【0021】
前処理装置2は、原水中の夾雑物を除去する目的で、例えばオートストレーナーのような簡易型回転固液分離器を用いることができる。
【0022】
また、第1および第2膜処理装置3および4において使用される分離膜は、有機膜および無機膜の何れでも良く、また、精密ろ過膜および限外ろ過膜の何れでも良い。具体的には、精密ろ過膜としては、公称孔径0.01から0.45μmのものが好ましく、限外ろ過膜としては、公称分画分子量1000から100万ダルトンのものが好ましい。膜モジュールの形状は、中空糸状、スパイラル状、チューブラ状、または、平膜状が用いられる。膜モジュールのろ過方式は、全量ろ過方式およびクロスフローろ過方式の何れの方式としても良く、膜ろ過への通水方式は、外圧型および内圧型の何れでも問題ない。さらに、原水側を加圧する加圧型のケーシングタイプ、あるいはろ過水側を減圧する吸引型の槽浸漬タイプの何れであっても良い。
【0023】
また、濃縮装置5では、第2膜処理装置4からの物理洗浄排水を汚泥の固形物濃度が1から6%となるまで濃縮することができ、濃縮装置の方式は、重力濃縮、膜濃縮、機械濃縮および浮上濃縮の何れであっても良い。
【0024】
上述した、本発明の浄水膜処理装置によれば、以下のようにして、原水を処理する。
【0025】
先ず、河川等から取水した原水を着水井1で受水した後、原水中の夾雑物を除去するための前処理装置2へ導き、第1膜処理装置3にて原水中の懸濁成分、病原性原虫類および細菌類を除去する。第1膜処理装置3において得られた膜ろ過水は、滅菌処理装置7により塩素消毒を行って水道水として供給される。
【0026】
第1膜処理装置3において、定期的に実施する物理洗浄操作により排出された物理洗浄排水は、第2膜処理装置4に送水され、さらに懸濁成分、病原性原虫類および細菌類を除去する。このように、第1膜処理装置3により膜ろ過された後の物理洗浄排水を第2膜処理装置4によりさらに膜ろ過することによって、従来のように、原水に凝集剤を添加する必要がなくなる。
【0027】
第2膜処理装置4において得られた膜ろ過水は、滅菌処理装置7に返送し、塩素消毒を行って水道水として供給される。第2膜処理装置4において、定期的に実施する物理洗浄操作により排出された物理洗浄排水は、濃縮装置5へ送られて処理される。濃縮装置5より得られた処理水は、水路8aから第2膜処理装置4へ送水されることにより、トータルの浄水回収率99.9%以上を得ることができる。一方、濃縮装置5より間欠的、あるいは連続的に得られた濃縮汚泥は、脱水機6へ送られ脱水される。
【0028】
上記浄水膜処理装置において、第2膜処理装置4からの膜ろ過水を滅菌処理装置7に返送する代わりに、図2に示すように、第1膜処理装置3に返送しても良い。
【0029】
次に、本発明の浄水膜処理方法を実施するためのさらに他の浄水膜処理装置について、図面を参照しながら説明する。
【0030】
図3は、本発明のさらに他の浄水膜処理装置による処理フローを示す図である。図3において、図1と同一部分には同一符号が付与されており、同一部分の説明は省略する。
【0031】
図3の浄水膜処理装置では、濃縮装置として膜濃縮装置9を用いており、第2膜処理装置4から定期的に実施する物理洗浄操作により排出された物理洗浄排水を汚泥の固形物濃度が1から6%となるまで濃縮する。図3の浄水膜処理装置においても、第1膜処理装置3により膜ろ過された後の物理洗浄排水を第2膜処理装置4によりさらに膜ろ過することによって、従来のように、原水に凝集剤を添加する必要がなくなる。さらに、膜濃縮装置9より得られた膜ろ過水は、水路8bから滅菌処理装置7により塩素消毒を行って水道水として供給されることにより、トータルの浄水回収率99.9%以上を得ることができる。
【0032】
ここで、膜濃縮装置9において使用される分離膜は、有機膜および無機膜の何れでも良く、また、精密ろ過膜および限外ろ過膜の何れでも良い。膜モジュールの形状は、中空糸状、スパイラル状、チューブラ状、または平膜状が用いられる。膜モジュールのろ過方式は、全量ろ過方式およびクロスフローろ過方式の何れの方式としても良く、膜ろ過への通水方式は、外圧型および内圧型の何れでも問題ない。さらに、原水側を加圧する加圧型のケーシングタイプ、あるいはろ過水側を減圧する吸引型の槽浸漬タイプの何れであっても良い。
【0033】
【実施例】
次に、本発明の浄水膜処理装置を、実施例によりさらに詳細に説明する。なお、以下の実施例によって、本発明を限定するものではない。
【0034】
(実施例1)
図3に示す浄水処理フローに従って原水を処理する。原水の平均濁度は5度であり、前処理装置2には、オートストレーナーを配置して、原水中の夾雑物を除去する。第1および第2膜処理装置3および4の仕様ならびに運転条件は表1に示した通りである。
【0035】
【表1】

Figure 2004267887
【0036】
第2膜処理装置4から排出された固形物濃度0.1%の物理洗浄排水を、表2に示した仕様の膜濃縮装置9に通水して膜ろ過処理した結果、膜ろ過水の回収率95%が得られ、濃縮汚泥の固形物濃度が2%であった。得られた膜ろ過水の水質分析結果を表3に示した。表3より、本実施例において得られた膜ろ過水は、水道水水質基準を満足することが分かり、塩素消毒装置へ送り滅菌処理を実施して水道水として供給した。その結果、システム全体の浄水回収率は99.98%であった。
【0037】
【表2】
Figure 2004267887
【0038】
【表3】
Figure 2004267887
【0039】
【発明の効果】
以上述べたように、本発明の浄水膜処理装置によれば、凝集剤を添加することなくシステム全体の浄水回収率を99.9%以上まで向上させることができる。また、固形物濃度1から6%の汚泥を脱水機へ投入することができ、脱水機における脱水速度の向上を図ることができる。さらに、脱水汚泥にアルミニウムを含まないため、脱水汚泥の有効利用に係る弊害を少なくする等、工業上有用な効果がもたらされる。
【図面の簡単な説明】
【図1】本発明の浄水膜処理装置による処理フローを示す図である。
【図2】本発明の他の浄水膜処理装置による処理フローを示す図である。
【図3】本発明のさらに他の浄水膜処理装置による処理フローを示す図である。
【図4】膜ろ過処理を行っている浄水場における従来処理フローを示す図である。
【図5】膜ろ過処理を行っている浄水場における他の従来処理フローを示す図である。
【符号の説明】
1:着水井
2:前処理装置
3:第1膜処理装置
4:第2膜処理装置
5:濃縮装置
6:脱水機
7:滅菌処理装置
8a、8b:水路
9:膜濃縮装置
20:着水井
21:前処理装置
22:膜処理装置
23:排水池
24:濃縮槽
25:脱水機
26:無機系凝集剤
27:凝集混和装置
28:膜処理装置
29:シックナー
30:脱水機
31:滅菌処理装置[0001]
TECHNICAL FIELD OF THE INVENTION
The present invention relates to a water purification membrane treatment method and apparatus, and in particular, a water purification membrane treatment capable of efficiently treating physical cleaning wastewater discharged from a membrane treatment apparatus in a membrane-based water purification plant and improving a water purification recovery rate. The present invention relates to a method and an apparatus.
[0002]
[Prior art]
A conventional water purification process using a membrane filtration process will be described with reference to the drawings.
[0003]
FIG. 4 is a diagram showing a conventional processing flow in a water purification plant performing a membrane filtration process.
[0004]
In the water purification treatment shown in the figure, raw water taken from a river or the like is received by a landing well 20, then guided to a pretreatment device 21 for removing impurities in the raw water, and suspended in the raw water by a membrane treatment device 22. Removes turbid components, pathogenic protozoa and bacteria. The membrane filtered water obtained from the membrane treatment device 22 is subjected to chlorine disinfection by the sterilization treatment device 31 and supplied as tap water. The purified water recovery rate at that time is about 90 to 95%. In the membrane treatment device 22, a physical cleaning operation is periodically performed, and the physical cleaning wastewater discharged by the cleaning is sent to a drainage pond 23, where it is separated into sludge and supernatant water. The sludge is settled and concentrated by gravity in the concentration tank 24 and supplied to the dehydrator 25. The supernatant water from the concentration tank 24 is returned to the landing well 20 together with the supernatant water from the drainage pond 23 for the purpose of improving the recovery rate.
[0005]
In the conventional method having the above-described configuration, when the raw water turbidity is high, the solid concentration in the physical cleaning wastewater is also high. However, when the raw water turbidity is low, the solids concentration in the physical washing wastewater is low, so that the sedimentation speed of the sludge is slow, and it is difficult to apply sedimentation concentration by gravity in the concentration tank 24.
[0006]
In order to solve this problem, it is necessary to improve the sedimentation of sludge by using polyaluminum chloride (PAC) or a polymer flocculant as a flocculant in the concentration tank 24.
[0007]
In the standard membrane-based water purification treatment shown in FIG. 5, raw water taken from a river or the like is received by the landing well 20, and then, in order to remove impurities in the raw water, polyaluminum chloride (PAC) or the like is used. An inorganic coagulant 26 is added to the mixture, and the mixture is guided to a coagulation mixing device 27. The mixture is press-fitted into a membrane treatment device 28 to perform membrane filtration to remove suspended components, pathogenic protozoa and bacteria in raw water. The membrane filtered water obtained from the membrane treatment device 28 is subjected to chlorine disinfection by the sterilization treatment device 31 and supplied as tap water. The purified water recovery rate at that time is about 95 to 98%. In the membrane treatment device 28, a physical cleaning operation is periodically performed, and the physical cleaning wastewater discharged by the cleaning is guided to the thickener 29 and separated into concentrated sludge and supernatant water. The concentrated sludge is supplied to the dehydrator 30, and the supernatant water is returned to the landing well 20 for the purpose of improving the recovery rate.
[0008]
[Problems to be solved by the invention]
As described above, in FIGS. 4 and 5 of the conventional system, a case where a coagulant is added is generally used. When the concentrated sludge to which the coagulant has been added is introduced into the dewaterers 25 and 30, there is a problem that the dewatering speed of the sludge in the dewaterers 25 and 30 is greatly reduced, and the required number of dewaterers is increased. Further, when aluminum is contained in the dewatered sludge, there is a problem that its effective utilization is difficult.
[0009]
Therefore, the present invention has been completed as a result of earnest research to overcome the above-mentioned problems, and the physical cleaning wastewater generated from the membrane treatment apparatus without adding a coagulant has a substantially constant sludge throughout the year. A water purification membrane treatment method and apparatus capable of concentrating to a concentration, increasing the water purification rate of the entire system to 99.9% or more, improving the dehydration speed in a dehydrator, and reducing the adverse effects associated with the effective use of dewatered sludge. It is intended to provide.
[0010]
[Means for Solving the Problems]
The present invention has been made to solve the above problems, and has the following features.
[0011]
The invention described in claim 1 is that, when raw water taken from a river or the like is used as tap water by membrane filtration without adding a coagulant thereto, the raw water is subjected to a primary membrane filtration treatment, and then the primary water is filtered. The method is characterized in that the physical washing wastewater after the membrane filtration treatment is subjected to a secondary membrane filtration treatment, and the physical washing wastewater after the secondary membrane filtration treatment is concentrated.
[0012]
The invention described in claim 2 is characterized in that the physical washing wastewater after the secondary membrane filtration treatment is concentrated until the solid concentration of sludge becomes 1 to 6%.
[0013]
The invention described in claim 3 is a water purification membrane treatment apparatus that uses raw water taken from a river or the like as tap water by membrane filtration using a membrane treatment apparatus without adding a coagulant thereto, and using the raw water as a primary membrane. It is characterized in that a first membrane treatment device for filtering and a second membrane treatment device for secondary filtration of the physical cleaning wastewater from the first membrane treatment device are provided.
[0014]
The invention described in claim 4 is a water receiving well that receives raw water taken from a river or the like, a pretreatment device that pretreats raw water from the landing well, and a raw water pretreated by the pretreatment device. A first membrane processing device for performing a membrane filtration process, a second membrane processing device for further performing a membrane filtration of the physical washing wastewater from the first membrane processing device, and a sterilization process for sterilizing the membrane filtered water from the first membrane processing device It is characterized by comprising a treatment device, a concentration device for concentrating the physical cleaning wastewater from the second membrane treatment device, and a dehydrator for dewatering the sludge concentrated by the concentration device.
[0015]
In the invention described in claim 5, the membrane filtered water from the second membrane treatment device is sent to the sterilization device, and the treated water from the concentration device is returned to the second membrane treatment device. It is characterized in particular.
[0016]
In the invention described in claim 6, the membrane filtered water from the second membrane treatment device is returned to the first membrane treatment device, and the treated water from the concentration device is returned to the second membrane treatment device. It is characterized by being performed.
[0017]
In the invention described in claim 7, the concentrating device comprises a membrane concentrating device, and membrane filtration water from the membrane concentrating device is sent to the sterilization device, and membrane filtration from the second membrane processing device is performed. Water is characterized in that it is sent to the sterilization apparatus.
[0018]
BEST MODE FOR CARRYING OUT THE INVENTION
Hereinafter, an embodiment of a water purification membrane treatment device for carrying out the water purification membrane treatment method of the present invention will be described with reference to the drawings.
[0019]
FIG. 1 is a diagram showing a processing flow by the water purification membrane processing apparatus of the present invention.
[0020]
In FIG. 1, 1 is a landing well for receiving raw water taken from a river or the like, 2 is a pretreatment device for removing contaminants in the raw water, 3 is a suspension component in the raw water, pathogen. The first membrane treatment device 4 for removing sexual protozoa and bacteria is a suspension component in the physical washing wastewater discharged by the physical washing operation periodically performed in the first membrane treatment device 3, A second membrane treatment device 5 for removing protozoa and bacteria; a concentration device 6 for condensing physical washing wastewater discharged by a physical washing operation periodically performed in the second membrane treatment device 4; Is a dehydrator for dewatering the sludge concentrated in the concentrating device 5, and 7 is a sterilizing device for sterilizing the membrane filtered water from the first membrane processing device 3 and the second membrane processing device 4. .
[0021]
For the purpose of removing impurities in raw water, a simple rotary solid-liquid separator such as an auto strainer can be used as the pretreatment device 2.
[0022]
The separation membrane used in the first and second membrane treatment devices 3 and 4 may be any of an organic membrane and an inorganic membrane, and may be any of a microfiltration membrane and an ultrafiltration membrane. Specifically, the microfiltration membrane preferably has a nominal pore size of 0.01 to 0.45 μm, and the ultrafiltration membrane preferably has a nominal molecular weight cut-off of 1,000 to 1,000,000 daltons. As the shape of the membrane module, a hollow fiber shape, a spiral shape, a tubular shape, or a flat membrane shape is used. The filtration method of the membrane module may be any of a total filtration method and a cross-flow filtration method, and there is no problem with the water passing method to the membrane filtration either of the external pressure type or the internal pressure type. Further, any of a pressurized casing type for pressurizing the raw water side and a suction tank immersion type for depressurizing the filtered water side may be used.
[0023]
In the concentrating device 5, the physical washing wastewater from the second membrane processing device 4 can be concentrated until the solid concentration of the sludge becomes 1 to 6%. Any of mechanical concentration and flotation concentration may be used.
[0024]
According to the water purification membrane treatment apparatus of the present invention described above, raw water is treated as follows.
[0025]
First, after receiving raw water taken from a river or the like at the landing well 1, the raw water is guided to the pretreatment device 2 for removing impurities in the raw water, and suspended components in the raw water are collected by the first membrane treatment device 3, Eliminate pathogenic protozoa and bacteria. The membrane filtered water obtained in the first membrane processing device 3 is subjected to chlorine disinfection by the sterilization device 7 and supplied as tap water.
[0026]
In the first membrane treatment device 3, the physical washing wastewater discharged by the regular physical washing operation is sent to the second membrane treatment device 4 to further remove suspended components, pathogenic protozoa and bacteria. . As described above, the physical washing wastewater after the membrane filtration by the first membrane treatment device 3 is further subjected to membrane filtration by the second membrane treatment device 4, so that it is not necessary to add a coagulant to the raw water as in the related art. .
[0027]
The membrane filtered water obtained in the second membrane treatment device 4 is returned to the sterilization treatment device 7, subjected to chlorination, and supplied as tap water. In the second membrane processing apparatus 4, the physical cleaning wastewater discharged by the periodically performed physical cleaning operation is sent to the concentration apparatus 5 for processing. The treated water obtained from the concentrating device 5 is sent from the water channel 8a to the second membrane processing device 4, so that a total purified water recovery rate of 99.9% or more can be obtained. On the other hand, the concentrated sludge obtained intermittently or continuously from the concentration device 5 is sent to the dehydrator 6 and dewatered.
[0028]
In the above-mentioned water purification membrane treatment device, instead of returning the membrane filtered water from the second membrane treatment device 4 to the sterilization treatment device 7, it may be returned to the first membrane treatment device 3 as shown in FIG.
[0029]
Next, still another water purification membrane processing apparatus for carrying out the water purification membrane processing method of the present invention will be described with reference to the drawings.
[0030]
FIG. 3 is a diagram showing a processing flow by still another water purification membrane processing apparatus of the present invention. 3, the same parts as those in FIG. 1 are denoted by the same reference numerals, and the description of the same parts will be omitted.
[0031]
In the water purification membrane treatment apparatus of FIG. 3, the membrane concentration apparatus 9 is used as a concentration apparatus, and the physical washing wastewater discharged from the second membrane treatment apparatus 4 by the physical washing operation which is periodically performed is used to reduce the solid concentration of sludge. Concentrate to 1-6%. In the water purification membrane treatment apparatus of FIG. 3 as well, the physical washing wastewater after membrane filtration by the first membrane treatment apparatus 3 is further subjected to membrane filtration by the second membrane treatment apparatus 4, so that the raw water has a coagulant as in the prior art. Need not be added. Further, the membrane filtered water obtained from the membrane concentrator 9 is subjected to chlorine disinfection by the sterilization device 7 from the water channel 8b and supplied as tap water to obtain a total purified water recovery rate of 99.9% or more. Can be.
[0032]
Here, the separation membrane used in the membrane concentrator 9 may be any of an organic membrane and an inorganic membrane, and may be any of a microfiltration membrane and an ultrafiltration membrane. As the shape of the membrane module, a hollow fiber shape, a spiral shape, a tubular shape, or a flat membrane shape is used. The filtration method of the membrane module may be any of a total filtration method and a cross-flow filtration method, and there is no problem with the water passing method to the membrane filtration either of the external pressure type or the internal pressure type. Further, any of a pressurized casing type for pressurizing the raw water side and a suction tank immersion type for depressurizing the filtered water side may be used.
[0033]
【Example】
Next, the water purification membrane treatment apparatus of the present invention will be described in more detail with reference to examples. The present invention is not limited by the following examples.
[0034]
(Example 1)
Raw water is treated according to the water purification treatment flow shown in FIG. The average turbidity of the raw water is 5 degrees, and an auto-strainer is disposed in the pretreatment device 2 to remove impurities in the raw water. The specifications and operating conditions of the first and second film processing apparatuses 3 and 4 are as shown in Table 1.
[0035]
[Table 1]
Figure 2004267887
[0036]
The physical washing wastewater having a solid concentration of 0.1% discharged from the second membrane processing apparatus 4 is passed through a membrane concentrating apparatus 9 having the specifications shown in Table 2 to perform membrane filtration processing, and as a result, membrane filtration water is recovered. A rate of 95% was obtained and the solids concentration of the concentrated sludge was 2%. Table 3 shows the results of water quality analysis of the obtained membrane filtered water. From Table 3, it was found that the membrane filtered water obtained in this example satisfies the tap water quality standard, and was sent to a chlorination apparatus and sterilized to be supplied as tap water. As a result, the purified water recovery rate of the entire system was 99.98%.
[0037]
[Table 2]
Figure 2004267887
[0038]
[Table 3]
Figure 2004267887
[0039]
【The invention's effect】
As described above, according to the water purification membrane treatment device of the present invention, the purified water recovery rate of the entire system can be improved to 99.9% or more without adding a flocculant. Further, sludge having a solid concentration of 1 to 6% can be introduced into the dehydrator, and the dehydration speed in the dehydrator can be improved. Furthermore, since aluminum is not contained in the dewatered sludge, industrially useful effects such as reducing adverse effects on the effective use of the dewatered sludge are provided.
[Brief description of the drawings]
FIG. 1 is a diagram showing a processing flow by a water purification membrane processing apparatus of the present invention.
FIG. 2 is a diagram showing a processing flow by another water purification membrane processing apparatus of the present invention.
FIG. 3 is a diagram showing a processing flow by still another water purification membrane processing apparatus of the present invention.
FIG. 4 is a diagram showing a conventional processing flow in a water purification plant performing a membrane filtration process.
FIG. 5 is a diagram showing another conventional processing flow in a water purification plant performing a membrane filtration process.
[Explanation of symbols]
1: Landing well 2: Pretreatment unit 3: First membrane treatment unit 4: Second membrane treatment unit 5: Concentration unit 6: Dehydrator 7: Sterilization treatment units 8a and 8b: Channel 9: Membrane concentration unit 20: Landing well 21: Pretreatment device 22: Membrane treatment device 23: Drain pond 24: Concentration tank 25: Dehydrator 26: Inorganic coagulant 27: Coagulation mixing device 28: Membrane treatment device 29: Thickener 30: Dehydrator 31: Sterilization treatment device

Claims (7)

河川等から取水した原水をこれに凝集剤を添加することなく膜ろ過処理して水道水として利用する際に、原水を一次膜ろ過処理し、次いで、一次膜ろ過処理した後の物理洗浄排水を二次膜ろ過処理し、そして、二次膜ろ過処理した後の物理洗浄排水を濃縮することを特徴とする浄水膜処理方法。When raw water taken from rivers and the like is used as tap water by membrane filtration without adding a coagulant thereto, the raw water is subjected to primary membrane filtration, and then the physical washing wastewater after primary membrane filtration is used. A method for treating a water purification membrane, comprising performing a secondary membrane filtration treatment, and concentrating the physical washing wastewater after the secondary membrane filtration treatment. 前記二次膜ろ過処理した後の物理洗浄排水を、汚泥の固形物濃度が1から6%となるまで濃縮することを特徴とする、請求項1に記載された浄水膜処理方法。The method for treating a water purification membrane according to claim 1, wherein the physical washing wastewater after the secondary membrane filtration treatment is concentrated until the solid concentration of sludge becomes 1 to 6%. 河川等から取水した原水をこれに凝集剤を添加することなく膜処理装置により膜ろ過処理して水道水として利用する浄水膜処理装置において、原水を一次膜ろ過する第1膜処理装置と、前記第1膜処理装置からの物理洗浄排水を二次膜ろ過する第2膜処理装置とが設けられていることを特徴とする浄水膜処理装置。In a water purification membrane treatment device using raw water taken from rivers or the like as tap water by membrane filtration treatment using a membrane treatment device without adding a coagulant thereto, a first membrane treatment device for performing primary membrane filtration of the raw water, A second membrane treatment device for performing secondary membrane filtration of the physical cleaning wastewater from the first membrane treatment device. 河川等から取水した原水を受水する着水井と、前記着水井からの原水を前処理する前処理装置と、前記前処理装置により前処理された原水を膜ろ過処理する第1膜処理装置と、前記第1膜処理装置からの物理洗浄排水をさらに膜ろ過する第2膜処理装置と、前記第1膜処理装置からの膜ろ過水を滅菌処理する滅菌処理装置と、前記第2膜処理装置からの物理洗浄排水を濃縮する濃縮装置と、前記濃縮装置により濃縮された汚泥を脱水する脱水機とを備えていることを特徴とする浄水膜処理装置。A landing well for receiving raw water taken from a river or the like, a pretreatment device for pretreating the raw water from the landing well, and a first membrane treatment device for performing membrane filtration of the raw water pretreated by the pretreatment device. A second membrane treatment device for further membrane-filtering the physical washing wastewater from the first membrane treatment device, a sterilization treatment device for sterilizing membrane filtration water from the first membrane treatment device, and the second membrane treatment device 1. A water purification membrane treatment apparatus comprising: a concentrator for concentrating physical washing wastewater from water; and a dehydrator for dewatering sludge concentrated by the concentrator. 前記第2膜処理装置からの膜ろ過水は、前記滅菌処理装置に送られ、前記濃縮装置からの処理水は、前記第2膜処理装置に返送されることを特徴とする、請求項4に記載された浄水膜処理装置。The membrane filtered water from the second membrane treatment device is sent to the sterilization treatment device, and the treated water from the concentration device is returned to the second membrane treatment device, The method according to claim 4, wherein The described water purification membrane treatment device. 前記第2膜処理装置からの膜ろ過水は、前記第1膜処理装置に返送され、前記濃縮装置からの処理水は、前記第2膜処理装置に返送されることを特徴とする、請求項4に記載された浄水膜処理装置。The membrane filtered water from the second membrane treatment device is returned to the first membrane treatment device, and the treated water from the concentration device is returned to the second membrane treatment device. 4. The water purification membrane treatment device according to 4. 前記濃縮装置は、膜濃縮装置からなり、前記膜濃縮装置からの膜ろ過水は、前記滅菌処理装置に送られ、前記第2膜処理装置からの膜ろ過水は、前記滅菌処理装置に送られることを特徴とする、請求項4に記載された浄水膜処理装置。The concentrator comprises a membrane concentrator, membrane filtered water from the membrane concentrator is sent to the sterilization device, and membrane filtered water from the second membrane device is sent to the sterilization device. The water purification membrane treatment device according to claim 4, characterized in that:
JP2003061038A 2003-03-07 2003-03-07 Water purification membrane treatment equipment Expired - Lifetime JP4071134B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP2003061038A JP4071134B2 (en) 2003-03-07 2003-03-07 Water purification membrane treatment equipment

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP2003061038A JP4071134B2 (en) 2003-03-07 2003-03-07 Water purification membrane treatment equipment

Publications (2)

Publication Number Publication Date
JP2004267887A true JP2004267887A (en) 2004-09-30
JP4071134B2 JP4071134B2 (en) 2008-04-02

Family

ID=33123358

Family Applications (1)

Application Number Title Priority Date Filing Date
JP2003061038A Expired - Lifetime JP4071134B2 (en) 2003-03-07 2003-03-07 Water purification membrane treatment equipment

Country Status (1)

Country Link
JP (1) JP4071134B2 (en)

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2006272218A (en) * 2005-03-30 2006-10-12 Toray Ind Inc Two-stage membrane filtration system and operation method of two-stage membrane filtration system
JP2006326471A (en) * 2005-05-25 2006-12-07 Jfe Engineering Kk Membrane separation apparatus and its operation method
JP2010167367A (en) * 2009-01-22 2010-08-05 Asahi Kasei Chemicals Corp Water purification membrane treatment apparatus
CN106039819A (en) * 2016-07-14 2016-10-26 宁波威博环保科技有限公司 Wastewater sludge treatment system

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2006272218A (en) * 2005-03-30 2006-10-12 Toray Ind Inc Two-stage membrane filtration system and operation method of two-stage membrane filtration system
JP2006326471A (en) * 2005-05-25 2006-12-07 Jfe Engineering Kk Membrane separation apparatus and its operation method
JP2010167367A (en) * 2009-01-22 2010-08-05 Asahi Kasei Chemicals Corp Water purification membrane treatment apparatus
CN106039819A (en) * 2016-07-14 2016-10-26 宁波威博环保科技有限公司 Wastewater sludge treatment system

Also Published As

Publication number Publication date
JP4071134B2 (en) 2008-04-02

Similar Documents

Publication Publication Date Title
CA2660610C (en) Method of improving performance of ultrafiltration or microfiltration membrane process in landfill leachate treatment
JP3909793B2 (en) Method and apparatus for treating organic wastewater containing high-concentration salts
WO2013054810A1 (en) Organic sewage collection processing device and collection processing method
JP3800449B2 (en) Method and apparatus for treating organic wastewater containing high concentrations of salts
JP2012200652A (en) Biological treatment apparatus
CN106477762A (en) Industrial concentrated water sofening treatment technique based on DF tubular membrane and system
JP4071134B2 (en) Water purification membrane treatment equipment
JP5854591B2 (en) Sewage purification apparatus and sewage purification method
JP2003236558A (en) Water cleaning system
KR20030089219A (en) Discharged water treatment method
KR20120046838A (en) Apparatus and method for water treatment using two stage membrane filtration
JP2010046562A (en) Resource recovery type water treatment method and system
JPH06328069A (en) Water purification device
JPH1119696A (en) Treatment of sludge waste water and water purifier
CN111573945A (en) System and method for resourceful treatment of heparin sodium wastewater
JPH11347595A (en) Water purifying treatment equipment and concentration sludge thereof
JP2002346347A (en) Method and apparatus for filtration
JP3951373B2 (en) Waste water treatment apparatus and method, water purification treatment facility
JP3697529B2 (en) Membrane-based wastewater treatment method and water purification apparatus
JP3185398B2 (en) Water purification equipment
RU2004134490A (en) METHOD FOR PRODUCING BLEATED WATER
JPS5918088B2 (en) Method for purifying valuable substances in liquid
JP5044578B2 (en) Water purification membrane treatment equipment
JP3079604B2 (en) Water treatment equipment
JP2004074146A (en) Method and equipment for treating impurity-containing liquid

Legal Events

Date Code Title Description
A621 Written request for application examination

Free format text: JAPANESE INTERMEDIATE CODE: A621

Effective date: 20051109

A711 Notification of change in applicant

Free format text: JAPANESE INTERMEDIATE CODE: A712

Effective date: 20070628

A977 Report on retrieval

Free format text: JAPANESE INTERMEDIATE CODE: A971007

Effective date: 20070823

A131 Notification of reasons for refusal

Free format text: JAPANESE INTERMEDIATE CODE: A131

Effective date: 20070904

A521 Request for written amendment filed

Free format text: JAPANESE INTERMEDIATE CODE: A523

Effective date: 20071102

RD02 Notification of acceptance of power of attorney

Free format text: JAPANESE INTERMEDIATE CODE: A7422

Effective date: 20071102

A521 Request for written amendment filed

Free format text: JAPANESE INTERMEDIATE CODE: A821

Effective date: 20071102

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: 20071225

A61 First payment of annual fees (during grant procedure)

Free format text: JAPANESE INTERMEDIATE CODE: A61

Effective date: 20080116

R150 Certificate of patent or registration of utility model

Ref document number: 4071134

Country of ref document: JP

Free format text: JAPANESE INTERMEDIATE CODE: R150

Free format text: JAPANESE INTERMEDIATE CODE: R150

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20110125

Year of fee payment: 3

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20110125

Year of fee payment: 3

S531 Written request for registration of change of domicile

Free format text: JAPANESE INTERMEDIATE CODE: R313531

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20110125

Year of fee payment: 3

R350 Written notification of registration of transfer

Free format text: JAPANESE INTERMEDIATE CODE: R350

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20110125

Year of fee payment: 3

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20120125

Year of fee payment: 4

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20120125

Year of fee payment: 4

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20130125

Year of fee payment: 5

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20130125

Year of fee payment: 5

S531 Written request for registration of change of domicile

Free format text: JAPANESE INTERMEDIATE CODE: R313531

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20130125

Year of fee payment: 5

R350 Written notification of registration of transfer

Free format text: JAPANESE INTERMEDIATE CODE: R350

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20140125

Year of fee payment: 6

S111 Request for change of ownership or part of ownership

Free format text: JAPANESE INTERMEDIATE CODE: R313115

R350 Written notification of registration of transfer

Free format text: JAPANESE INTERMEDIATE CODE: R350

S111 Request for change of ownership or part of ownership

Free format text: JAPANESE INTERMEDIATE CODE: R313115

R350 Written notification of registration of transfer

Free format text: JAPANESE INTERMEDIATE CODE: R350

S531 Written request for registration of change of domicile

Free format text: JAPANESE INTERMEDIATE CODE: R313531

R350 Written notification of registration of transfer

Free format text: JAPANESE INTERMEDIATE CODE: R350

S531 Written request for registration of change of domicile

Free format text: JAPANESE INTERMEDIATE CODE: R313531

R350 Written notification of registration of transfer

Free format text: JAPANESE INTERMEDIATE CODE: R350

S531 Written request for registration of change of domicile

Free format text: JAPANESE INTERMEDIATE CODE: R313531

R350 Written notification of registration of transfer

Free format text: JAPANESE INTERMEDIATE CODE: R350

S531 Written request for registration of change of domicile

Free format text: JAPANESE INTERMEDIATE CODE: R313531

R370 Written measure of declining of transfer procedure

Free format text: JAPANESE INTERMEDIATE CODE: R370

R370 Written measure of declining of transfer procedure

Free format text: JAPANESE INTERMEDIATE CODE: R370

S531 Written request for registration of change of domicile

Free format text: JAPANESE INTERMEDIATE CODE: R313531

R371 Transfer withdrawn

Free format text: JAPANESE INTERMEDIATE CODE: R371

S531 Written request for registration of change of domicile

Free format text: JAPANESE INTERMEDIATE CODE: R313531

R350 Written notification of registration of transfer

Free format text: JAPANESE INTERMEDIATE CODE: R350

EXPY Cancellation because of completion of term