Deprecated: The each() function is deprecated. This message will be suppressed on further calls in /home/zhenxiangba/zhenxiangba.com/public_html/phproxy-improved-master/index.php on line 456
JP7705754B2 - Wastewater treatment device and method for cleaning the same - Google Patents
[go: Go Back, main page]

JP7705754B2 - Wastewater treatment device and method for cleaning the same - Google Patents

Wastewater treatment device and method for cleaning the same Download PDF

Info

Publication number
JP7705754B2
JP7705754B2 JP2021131376A JP2021131376A JP7705754B2 JP 7705754 B2 JP7705754 B2 JP 7705754B2 JP 2021131376 A JP2021131376 A JP 2021131376A JP 2021131376 A JP2021131376 A JP 2021131376A JP 7705754 B2 JP7705754 B2 JP 7705754B2
Authority
JP
Japan
Prior art keywords
wastewater treatment
treatment tanks
anaerobic
anaerobic wastewater
membrane
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Active
Application number
JP2021131376A
Other languages
Japanese (ja)
Other versions
JP2023025922A (en
Inventor
伸一 酒見
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.)
Mitsubishi Kakoki Kaisha Ltd
Original Assignee
Mitsubishi Kakoki Kaisha Ltd
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 Mitsubishi Kakoki Kaisha Ltd filed Critical Mitsubishi Kakoki Kaisha Ltd
Priority to JP2021131376A priority Critical patent/JP7705754B2/en
Priority to TW111128113A priority patent/TWI910376B/en
Priority to KR1020220092907A priority patent/KR20230024204A/en
Priority to CN202210960594.5A priority patent/CN115888403A/en
Publication of JP2023025922A publication Critical patent/JP2023025922A/en
Application granted granted Critical
Publication of JP7705754B2 publication Critical patent/JP7705754B2/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Images

Classifications

    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D65/00Accessories or auxiliary operations, in general, for separation processes or apparatus using semi-permeable membranes
    • B01D65/02Membrane cleaning or sterilisation ; Membrane regeneration
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D61/00Processes of separation using semi-permeable membranes, e.g. dialysis, osmosis or ultrafiltration; Apparatus, accessories or auxiliary operations specially adapted therefor
    • B01D61/14Ultrafiltration; Microfiltration
    • B01D61/18Apparatus therefor
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D61/00Processes of separation using semi-permeable membranes, e.g. dialysis, osmosis or ultrafiltration; Apparatus, accessories or auxiliary operations specially adapted therefor
    • B01D61/14Ultrafiltration; Microfiltration
    • B01D61/20Accessories; Auxiliary operations
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D61/00Processes of separation using semi-permeable membranes, e.g. dialysis, osmosis or ultrafiltration; Apparatus, accessories or auxiliary operations specially adapted therefor
    • B01D61/14Ultrafiltration; Microfiltration
    • B01D61/22Controlling or regulating
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D63/00Apparatus in general for separation processes using semi-permeable membranes
    • B01D63/02Hollow fibre modules
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D69/00Semi-permeable membranes for separation processes or apparatus characterised by their form, structure or properties; Manufacturing processes specially adapted therefor
    • B01D69/08Hollow fibre membranes
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F3/00Biological treatment of water, waste water, or sewage
    • C02F3/02Aerobic processes
    • C02F3/12Activated sludge processes
    • C02F3/1236Particular type of activated sludge installations
    • C02F3/1268Membrane bioreactor systems
    • C02F3/1273Submerged membrane bioreactors
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2321/00Details relating to membrane cleaning, regeneration, sterilization or to the prevention of fouling
    • B01D2321/18Use of gases
    • B01D2321/185Aeration
    • YGENERAL 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
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02EREDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
    • Y02E50/00Technologies for the production of fuel of non-fossil origin
    • Y02E50/30Fuel from waste, e.g. synthetic alcohol or diesel
    • YGENERAL 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
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W10/00Technologies for wastewater treatment
    • Y02W10/10Biological treatment of water, waste water, or sewage

Landscapes

  • Chemical & Material Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Water Supply & Treatment (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Biodiversity & Conservation Biology (AREA)
  • Microbiology (AREA)
  • Hydrology & Water Resources (AREA)
  • Environmental & Geological Engineering (AREA)
  • Organic Chemistry (AREA)
  • Separation Using Semi-Permeable Membranes (AREA)
  • Purification Treatments By Anaerobic Or Anaerobic And Aerobic Bacteria Or Animals (AREA)

Description

本発明は、排水処理装置及び排水処理装置の洗浄方法に関する。 The present invention relates to a wastewater treatment device and a method for cleaning the wastewater treatment device.

産業排水や生活排水等の排水を処理する排水処理技術として、嫌気性膜分離法(嫌気性MBR:Membrane Bio Reactor)が知られている。嫌気性膜分離法は、微生物を用い、分離膜による固液分離を行って、排水中の有機物をメタンと二酸化炭素にまで分解できる優れた排水処理技術である。 Anaerobic membrane separation (anaerobic MBR: Membrane Bio Reactor) is known as a wastewater treatment technology for treating industrial wastewater, domestic wastewater, etc. Anaerobic membrane separation is an excellent wastewater treatment technology that uses microorganisms to perform solid-liquid separation using a separation membrane, and can break down organic matter in wastewater into methane and carbon dioxide.

通常、嫌気性膜分離法を用いた排水処理装置では、継続的な使用に伴い、分離膜の表面や孔中に、し渣や汚れ等の汚濁物質が付着して目詰まり(ファウリング)が生じるため、分離膜の洗浄が必要である。分離膜の汚れは、透過流速(フラックス)を低下させ、排水処理性能に大きな影響を与える。
従来、分離膜の洗浄方法としては、散気管による洗浄や薬液による洗浄等が知られている(例えば、特許文献1,2参照)。
In wastewater treatment equipment using anaerobic membrane separation, contaminants such as sediment and dirt adhere to the surface and pores of the separation membrane with continued use, causing clogging (fouling), and therefore the separation membrane must be cleaned. Membrane fouling reduces the permeation flux and has a significant impact on wastewater treatment performance.
Conventionally, methods for cleaning separation membranes include cleaning with an air diffuser and cleaning with a chemical solution (see, for example, Patent Documents 1 and 2).

散気管による洗浄は、分離膜の下方に散気管を設置して気泡を発生させ、この気泡の上昇によって形成される気泡と排水(被処理水)との気液混合流を分離膜の表面に接触させることで、分離膜の表面に付着した汚濁物質を除去するものである。通常、散気管による洗浄は、排水処理装置の運転中に継続して行われる。一方、薬液による洗浄は、所定濃度の薬液に分離膜を浸漬するものであり、例えば、定期的に行われる。この場合、槽外に分離膜を取り出して薬液に浸漬することも行われている。 Cleaning with an aeration tube involves placing an aeration tube below the separation membrane to generate air bubbles, and then bringing the gas-liquid mixture of the bubbles and wastewater (water to be treated) formed by the rising of the bubbles into contact with the surface of the separation membrane, thereby removing contaminants that have adhered to the surface of the separation membrane. Cleaning with an aeration tube is usually performed continuously while the wastewater treatment device is in operation. On the other hand, cleaning with a chemical solution involves immersing the separation membrane in a chemical solution of a specified concentration, and is performed, for example, periodically. In this case, the separation membrane is sometimes removed from the tank and immersed in the chemical solution.

特開平09-117646号公報Japanese Patent Application Publication No. 09-117646 特開平09-117789号公報Japanese Patent Application Publication No. 09-117789

しかしながら、前記した散気管による洗浄は、気泡の上昇による気液混合流の上向きの流れを利用したものであるため、汚濁物質が分離膜の上部側に蓄積しやすく、蓄積した汚濁物質を除去し難いという課題があった。
また、薬液による洗浄では、洗浄時に槽内の嫌気性細菌類に影響を与えるため、薬液を使用しない分離膜の洗浄技術の実現が期待されている。
However, the above-mentioned cleaning using an aeration tube utilizes the upward flow of the gas-liquid mixture caused by the rising of air bubbles, and therefore has the problem that contaminants tend to accumulate on the upper side of the separation membrane, making it difficult to remove the accumulated contaminants.
In addition, cleaning with chemical solutions affects the anaerobic bacteria in the tank during cleaning, so there are hopes for the development of a separation membrane cleaning technology that does not use chemical solutions.

本発明は、前記した問題を解決し、排水(被処理水)を利用して分離膜を洗浄できるとともに、分離膜の上部側に蓄積した汚濁物質をも好適に除去できる排水処理装置及び排水処理装置の洗浄方法を提供することを課題とする。 The present invention aims to solve the above problems and provide a wastewater treatment device and a method for cleaning the wastewater treatment device that can clean the separation membrane using wastewater (water to be treated) and also effectively remove contaminants that have accumulated on the upper side of the separation membrane.

前記課題を解決するため本発明の排水処理装置は、隣接して設置された少なくとも2つの嫌気性排水処理槽と、前記2つの嫌気性排水処理槽のそれぞれに設置され、排水をろ過する分離膜と、前記両分離膜の下方にそれぞれ配置され、前記両分離膜に向けてガスの気泡を供給する散気管と、前記両分離膜の下方において前記2つの嫌気性排水処理槽同士を連通する連通路と、前記2つの嫌気性排水処理槽の間に圧力差を発生させる圧力差発生手段と、を具備したことを特徴とする。 To solve the above problems, the wastewater treatment device of the present invention is characterized by comprising at least two anaerobic wastewater treatment tanks installed adjacent to each other, a separation membrane installed in each of the two anaerobic wastewater treatment tanks for filtering wastewater, an aeration pipe arranged below each of the separation membranes for supplying gas bubbles toward each of the separation membranes, a communication passage connecting the two anaerobic wastewater treatment tanks below the separation membranes, and a pressure difference generating means for generating a pressure difference between the two anaerobic wastewater treatment tanks.

本発明の排水処理装置では、一方の嫌気性排水処理槽と他方の嫌気性排水処理槽との間に圧力差を発生させることで水位差を形成でき、水頭が高い嫌気性排水処理槽から水頭が低い嫌気性排水処理槽へ連通路を通じて流れる水流を形成できる。この水流により、水頭が高い嫌気性排水処理槽内では、散気管の気泡の上昇による気液混合流の上向きの流れと逆の下向きの水流が勢いよく形成され、分離膜の上部側に蓄積した汚濁物質が下方向に剥ぎ取られる。これにより、分離膜の上部側に蓄積した汚濁物質を、排水(被処理水)を利用して好適に除去できる。
したがって、薬液による洗浄頻度を減少させることができる。
In the wastewater treatment device of the present invention, a water level difference can be created by generating a pressure difference between one anaerobic wastewater treatment tank and the other anaerobic wastewater treatment tank, and a water flow can be formed that flows through a communication passage from the anaerobic wastewater treatment tank with a high hydraulic head to the anaerobic wastewater treatment tank with a low hydraulic head. This water flow creates a powerful downward water flow in the anaerobic wastewater treatment tank with a high hydraulic head, opposite to the upward flow of the gas-liquid mixed flow caused by the rising air bubbles in the aeration pipe, and the pollutants accumulated on the upper side of the separation membrane are peeled off downward. This allows the pollutants accumulated on the upper side of the separation membrane to be suitably removed by using the wastewater (water to be treated).
Therefore, the frequency of cleaning with chemicals can be reduced.

また、前記圧力差発生手段は、前記2つの嫌気性排水処理槽にそれぞれ接続されるガス回収管と、前記ガス回収管に設けられた回収側開閉弁と、前記両散気管にそれぞれ接続されたガス供給管と、前記両ガス供給管に設けられた供給側開閉弁と、前記両回収側開閉弁及び前記両供給側開閉弁の開閉を制御する制御部と、を備えていることが好ましい。 The pressure difference generating means preferably includes a gas recovery pipe connected to each of the two anaerobic wastewater treatment tanks, a recovery side on-off valve provided in the gas recovery pipe, a gas supply pipe connected to each of the two aeration pipes, a supply side on-off valve provided in both of the gas supply pipes, and a control unit that controls the opening and closing of both of the recovery side on-off valves and both of the supply side on-off valves.

この構成では、制御部により両回収側開閉弁及び両供給側開閉弁の開閉を制御することにより、水頭圧を利用した洗浄を容易に行うことができる。例えば、一方の嫌気性排水処理槽を洗浄する場合、その槽の回収側開閉弁を制御部により開くとともに、供給側開閉弁を閉じる。そして他方の嫌気性排水処理槽における回収側開閉弁を制御部により閉じるとともに、供給側開閉弁を開く。そうすると、他方の嫌気性排水処理槽内で気圧が増加し続け、増加したガスにより他方の槽内の水位が低下する。この水位の低下に伴い、他方の嫌気性排水処理槽から一方の嫌気性排水処理槽へ連通路を通じて排水(被処理水)が流れ、一方の嫌気性排水処理槽の水位が上昇する。一方の嫌気性排水処理槽の水位が所定高さに上昇すると、他方の嫌気性排水処理槽における回収側開閉弁が制御部により開かれる。これにより、一方の嫌気性排水処理槽から他方の嫌気性排水処理槽へ連通路を通じて排水(被処理水)が勢いよく流れ、一方の嫌気性排水処理槽の分離膜の上部側に蓄積した汚濁物質が排水(被処理水)により好適に除去される。 In this configuration, cleaning can be easily performed using the head pressure by controlling the opening and closing of both recovery side valves and both supply side valves by the control unit. For example, when cleaning one anaerobic wastewater treatment tank, the control unit opens the recovery side valve of that tank and closes the supply side valve. Then, the control unit closes the recovery side valve in the other anaerobic wastewater treatment tank and opens the supply side valve. Then, the air pressure continues to increase in the other anaerobic wastewater treatment tank, and the water level in the other tank drops due to the increased gas. As the water level drops, wastewater (water to be treated) flows from the other anaerobic wastewater treatment tank through the communication passage to the one anaerobic wastewater treatment tank, and the water level in the one anaerobic wastewater treatment tank rises. When the water level in the one anaerobic wastewater treatment tank rises to a predetermined height, the control unit opens the recovery side valve in the other anaerobic wastewater treatment tank. This allows the wastewater (water to be treated) to flow vigorously from one anaerobic wastewater treatment tank to the other anaerobic wastewater treatment tank through a connecting passage, and contaminants that have accumulated on the upper side of the separation membrane of one anaerobic wastewater treatment tank are effectively removed by the wastewater (water to be treated).

また、前記両ガス回収管で回収されたガスは、ブロア装置を通じて前記両ガス供給管に供給されることが好ましい。 It is also preferable that the gas recovered in both gas recovery pipes is supplied to both gas supply pipes through a blower device.

この構成では、両ガス回収管で回収されたガスが両嫌気性排水処理槽に再び循環供給されるので、効率のよい分離膜の洗浄を実現できる。 In this configuration, the gas recovered in both gas recovery pipes is circulated and supplied again to both anaerobic wastewater treatment tanks, enabling efficient cleaning of the separation membrane.

前記課題を解決するため本発明の排水処理装置の洗浄方法は、隣接して設置された少なくとも2つの嫌気性排水処理槽と、前記2つの嫌気性排水処理槽のそれぞれに設置され、排水をろ過する分離膜と、前記両分離膜の下方にそれぞれ配置され、前記両分離膜に向けてガスの気泡を供給する散気管と、前記両分離膜の下方において前記2つの嫌気性排水処理槽を連通する連通路と、を備えた排水処理装置の洗浄方法である。前記2つの嫌気性排水処理槽の間に圧力差を発生させることで前記2つの嫌気性排水処理槽の間に水位差を形成する水位差形成工程と、水頭が高い側の前記嫌気性排水処理槽から水頭が低い側の前記嫌気性排水処理槽へ前記連通路を通じて流れる水流を形成する水流形成工程と、を含むことを特徴とする。 In order to solve the above problems, the method for cleaning a wastewater treatment device of the present invention is a method for cleaning a wastewater treatment device that includes at least two anaerobic wastewater treatment tanks installed adjacent to each other, a separation membrane installed in each of the two anaerobic wastewater treatment tanks for filtering wastewater, an aeration pipe arranged below both separation membranes for supplying gas bubbles toward both separation membranes, and a communication passage that connects the two anaerobic wastewater treatment tanks below both separation membranes. The method includes a water level difference forming step of forming a water level difference between the two anaerobic wastewater treatment tanks by generating a pressure difference between the two anaerobic wastewater treatment tanks, and a water flow forming step of forming a water flow that flows through the communication passage from the anaerobic wastewater treatment tank with a higher water head to the anaerobic wastewater treatment tank with a lower water head.

本発明の排水処理装置の洗浄方法では、水位差形成工程により2つの嫌気性排水処理槽の間に水位差を形成でき、水流形成工程により水頭が高い側から低い側に連通路を通じて流れる水流を形成できる。この水流は、散気管の気泡の上昇による気液混合流の上向きの流れと逆の下向きの流れであるので、分離膜の上部側に蓄積した汚濁物質を下方向に剥ぎ取るように作用する。これにより、分離膜の上部側に蓄積した汚濁物質を、排水(被処理水)を利用して好適に除去できる。
したがって、薬液による洗浄頻度を減少させることができる。
In the method for cleaning a wastewater treatment device of the present invention, a water level difference can be created between two anaerobic wastewater treatment tanks by the water level difference creating step, and a water flow can be created through a communication passage from the side with a higher head to the side with a lower head by the water flow creating step. This water flow is a downward flow opposite to the upward flow of the gas-liquid mixed flow caused by the rising of air bubbles in the aeration tube, and therefore acts to scrape off pollutants accumulated on the upper side of the separation membrane in a downward direction. This allows the pollutants accumulated on the upper side of the separation membrane to be suitably removed by using wastewater (water to be treated).
Therefore, the frequency of cleaning with chemicals can be reduced.

本発明の排水処理装置及び排水処理装置の洗浄方法では、排水を利用して分離膜を洗浄できるとともに、分離膜の上部側に蓄積した汚濁物質をも好適に除去できる。 The wastewater treatment device and method for cleaning the wastewater treatment device of the present invention can use wastewater to clean the separation membrane and can also effectively remove contaminants that have accumulated on the upper side of the separation membrane.

本発明の一実施形態に係る排水処理装置を示した構成図である。1 is a configuration diagram showing a wastewater treatment device according to an embodiment of the present invention. 本発明の一実施形態に係る排水処理装置の洗浄方法を示す図であり、水位差形成工程を示した図である。FIG. 1 is a diagram showing a method for cleaning a wastewater treatment device according to an embodiment of the present invention, and is a diagram showing a water level difference forming step. 本発明の一実施形態に係る排水処理装置の洗浄方法を示す図であり、水流形成工程を示した図である。FIG. 1 is a diagram showing a method for cleaning a wastewater treatment device according to an embodiment of the present invention, and is a diagram showing a water flow forming process. 本発明の一実施形態に係る排水処理装置のレイアウト例を示した模式平面図である。1 is a schematic plan view showing an example of the layout of a wastewater treatment device according to an embodiment of the present invention.

本発明の実施形態について、適宜図面を参照しながら詳細に説明する。以下の説明において、上下の方向は、排水処理装置の嫌気性排水処理槽が設置される面に直交する鉛直方向である。 The embodiment of the present invention will be described in detail with reference to the drawings as appropriate. In the following description, the up-down direction refers to the vertical direction perpendicular to the surface on which the anaerobic wastewater treatment tank of the wastewater treatment device is installed.

図1に示すように、排水処理装置1は、嫌気性排水処理槽2A,2Bと、膜ユニット10,10と、散気管11,11とを備えている。また、排水処理装置1は、2つの嫌気性排水処理槽2A,2Bの間に圧力差を発生させる圧力差発生手段6を備えている。圧力差発生手段6の詳細は、後記する。 As shown in FIG. 1, the wastewater treatment device 1 includes anaerobic wastewater treatment tanks 2A and 2B, membrane units 10 and aeration pipes 11. The wastewater treatment device 1 also includes a pressure difference generating means 6 that generates a pressure difference between the two anaerobic wastewater treatment tanks 2A and 2B. Details of the pressure difference generating means 6 will be described later.

嫌気性排水処理槽2A,2B(以下、「処理槽2A,2B」と称す。)は、左右中央部分に形成された隔壁2aを介して隣接配置されている。各処理槽2A,2Bは、密閉されており、被処理水として排水W1がそれぞれ流入するように構成されている。排水W1は、排水供給路の途中に設けられた不図示の送液ポンプにより処理槽2A,2Bに供給される。排水W1としては、工場等から排出される産業排水や生活排水(汚水)等が挙げられる。なお、各処理槽2A,2Bにおいて、排水W1の水位W1aは、膜ユニット10,10の全体が浸漬される高さに設定されている。 Anaerobic wastewater treatment tanks 2A, 2B (hereinafter referred to as "treatment tanks 2A, 2B") are adjacently arranged with a partition wall 2a formed in the center of the left and right. Each treatment tank 2A, 2B is sealed and configured to receive wastewater W1 as the water to be treated. The wastewater W1 is supplied to the treatment tanks 2A, 2B by a liquid delivery pump (not shown) installed midway through the wastewater supply line. Examples of wastewater W1 include industrial wastewater discharged from factories and domestic wastewater (sewage). In each treatment tank 2A, 2B, the water level W1a of the wastewater W1 is set to a height at which the entire membrane unit 10, 10 is immersed.

隔壁2aの下部には、処理槽2A,2B同士を連通する連通路5が形成されている。連通路5は、処理槽2A,2B相互の排水W1の通流を可能にするものであり、処理槽2A,2B相互間の排水W1の通流に抵抗とならない開口面積を有している。連通路5は、各処理槽2A,2Bの膜ユニット10,10よりも下方となる位置に開口形成されている。
なお、処理槽2A,2Bの内空上部には、排水W1の水位の上昇を許容するスペースが形成されている。また、処理槽2A,2Bは、余剰汚泥を排出するための不図示の排出路を備えている。
A communication passage 5 is formed in the lower part of the partition wall 2a to connect the treatment tanks 2A, 2B to each other. The communication passage 5 allows the flow of wastewater W1 between the treatment tanks 2A, 2B, and has an opening area that does not provide resistance to the flow of wastewater W1 between the treatment tanks 2A, 2B. The communication passage 5 is formed at an opening at a position below the membrane units 10, 10 of each treatment tank 2A, 2B.
A space is formed in the upper interior space of the treatment tanks 2A and 2B to allow the water level of the wastewater W1 to rise. The treatment tanks 2A and 2B are also provided with a discharge path (not shown) for discharging excess sludge.

膜ユニット10は、公知の分離膜からなる複数の膜エレメントを備えている。膜ユニット10は、各処理槽2A,2Bで同じ仕様のものを用いている。膜エレメントは集積性の高い平型形状を呈している。なお、円筒形等の形状の異なるものを用いてもよい。
分離膜としては、精密ろ過膜(MF膜)を使用することが好ましい。分離膜の形状としては、中空糸膜、平膜、管状膜、袋状膜等が挙げられ、容積ベースで比較した場合に膜面積の大きい中空糸膜が好ましい。
分離膜の材質としては、有機材料(セルロース、ポリオレフィン、ポリスルフォン、ポリビニルアルコール、ポリメチルメタクリレート、ポリフッ化ビニリデン、ポリ4フッ化エチレン等)が挙げられる。分離膜の材質は、被処理水の性状に応じて適宜選択する。
The membrane unit 10 includes a plurality of membrane elements made of known separation membranes. The membrane units 10 used in each of the treatment tanks 2A and 2B have the same specifications. The membrane elements have a flat shape that allows for high integration. However, membrane elements of different shapes, such as a cylindrical shape, may also be used.
As the separation membrane, it is preferable to use a microfiltration membrane (MF membrane). Examples of the shape of the separation membrane include a hollow fiber membrane, a flat membrane, a tubular membrane, a bag-shaped membrane, etc., and a hollow fiber membrane having a large membrane area when compared on a volume basis is preferable.
Examples of the material for the separation membrane include organic materials (cellulose, polyolefin, polysulfone, polyvinyl alcohol, polymethyl methacrylate, polyvinylidene fluoride, polytetrafluoroethylene, etc.) The material for the separation membrane is appropriately selected depending on the properties of the water to be treated.

膜ユニット10は、例えば、枠状のフレームに複数の膜エレメントが保持されてなる。膜ユニット10の上部には、複数の膜エレメントからの透過水W2を排出するための透過水排出路12が接続されている。各膜ユニット10,10の透過水排出路12,12は、下流側で一つに合流している。その合流路の途中には、不図示の吸引ポンプが設けられている。透過水W2は、吸引ポンプに吸引されて外部に排出され、後段の不図示の高度処理設備(窒素処理方式)またはアナモックス処理装置に送られて窒素が除去される。 The membrane unit 10 is, for example, a frame holding multiple membrane elements. A permeate discharge channel 12 for discharging the permeate W2 from the multiple membrane elements is connected to the top of the membrane unit 10. The permeate discharge channels 12, 12 of each membrane unit 10, 10 merge into one downstream. A suction pump (not shown) is provided in the middle of the merged channel. The permeate W2 is sucked into the suction pump and discharged to the outside, and is sent to a downstream advanced treatment facility (nitrogen treatment method) or anammox treatment device (not shown) to remove nitrogen.

散気管11は、各膜ユニット10,10の下方にそれぞれ配置されている。散気管11は、ブロア装置19から供給されるガスとしてのバイオガスを膜ユニット10の膜エレメントに向けて吐出するものである。散気管11には、ガス吐出用の吐出孔が複数設けられている。各散気管11,11には、ガス供給管13がそれぞれ接続されている。各ガス供給管13,13は、ブロア装置19に接続された主管18にそれぞれ接続され、主管18を通じてガスの供給を受けるように構成されている。散気管11で発生した気泡は、上昇によって気泡と排水W1との気液混合流を形成する。なお、バイオガスは、メタンガス、二酸化炭素、窒素、硫化水素等を含むガスである。 The aeration pipes 11 are disposed below each of the membrane units 10. The aeration pipes 11 discharge biogas, which is supplied from the blower device 19, toward the membrane elements of the membrane unit 10. The aeration pipes 11 are provided with a plurality of discharge holes for discharging gas. A gas supply pipe 13 is connected to each of the aeration pipes 11. Each of the gas supply pipes 13 is connected to a main pipe 18 connected to the blower device 19, and is configured to receive gas supply through the main pipe 18. The bubbles generated in the aeration pipes 11 rise to form a gas-liquid mixed flow of the bubbles and wastewater W1. The biogas is a gas containing methane gas, carbon dioxide, nitrogen, hydrogen sulfide, etc.

圧力差発生手段6は、ガス回収管15,15と、回収側開閉弁16,16と、ガス供給管13,13と、供給側開閉弁14,14と、制御部30とを備えている。
ガス回収管15,15は、処理槽2A,2Bに一端が接続されており、処理槽2A,2Bの内空からバイオガスを回収する。回収側開閉弁16,16は、ガス回収管15,15の途中に設けられており、制御部30の制御により作動する。回収側開閉弁16は、開いているときに、バイオガスが回収されることを許容し、閉じられているときに、バイオガスの回収を阻止する。ガス回収管15,15の各他端は、回収側主管17に接続されている。回収側主管17の下流端は、ガスフォルダ20に接続されている。ガスフォルダ20は、余剰のバイオガスが生じた場合にこれを貯溜する機能を有している。回収側主管17には、主管18の端部が接続されている。
The pressure difference generating means 6 includes gas recovery pipes 15 , recovery side on-off valves 16 , gas supply pipes 13 , supply side on-off valves 14 , and a control unit 30 .
The gas recovery pipes 15, 15 have one end connected to the treatment tanks 2A, 2B, and recover biogas from the interior of the treatment tanks 2A, 2B. The recovery side on-off valves 16, 16 are provided midway through the gas recovery pipes 15, 15, and are operated under the control of the control unit 30. The recovery side on-off valve 16 allows biogas to be recovered when open, and prevents biogas from being recovered when closed. The other end of each of the gas recovery pipes 15, 15 is connected to a recovery side main pipe 17. The downstream end of the recovery side main pipe 17 is connected to a gas folder 20. The gas folder 20 has the function of storing surplus biogas when it is generated. An end of a main pipe 18 is connected to the recovery side main pipe 17.

ガス供給管13,13は、一端が散気管11,11に接続されており、散気管11,11に対してバイオガスを供給する。ガス供給管13,13の各他端は、主管18に接続されている。供給側開閉弁14,14は、ガス供給管13,13の途中に設けられており、制御部30の制御により作動する。供給側開閉弁14は、開いているときに、バイオガスが散気管11に供給されることを許容し、閉じられているときに、散気管11への供給を阻止する。主管18の上流側は、回収側主管17に接続されている。 One end of the gas supply pipes 13, 13 is connected to the aeration pipes 11, 11, and supplies biogas to the aeration pipes 11, 11. The other end of each of the gas supply pipes 13, 13 is connected to a main pipe 18. The supply side opening/closing valves 14, 14 are provided midway through the gas supply pipes 13, 13, and are operated under the control of the control unit 30. When the supply side opening/closing valve 14 is open, it allows biogas to be supplied to the aeration pipe 11, and when it is closed, it prevents the supply to the aeration pipe 11. The upstream side of the main pipe 18 is connected to the recovery side main pipe 17.

制御部30は、回収側開閉弁16,16及び供給側開閉弁14,14の開閉を制御する装置である。制御部30は、例えば、CPU(Central Processing Unit)、RAM(Random Access Memory)、ROM(Read Only Memory)、入出力回路等を備えて構成されている。制御部30は、入力装置からの入力、ROMに記憶されたプログラム、データなどに基づいて各種処理を行うことによって制御を実行する。 The control unit 30 is a device that controls the opening and closing of the recovery side opening and closing valves 16, 16 and the supply side opening and closing valves 14, 14. The control unit 30 is configured with, for example, a CPU (Central Processing Unit), RAM (Random Access Memory), ROM (Read Only Memory), input/output circuits, etc. The control unit 30 executes control by performing various processes based on inputs from input devices, programs stored in the ROM, data, etc.

次に、制御部30の制御によって実行される排水処理装置の洗浄方法について説明する。図2は排水処理装置の洗浄方法を示す図であり、水位差形成工程を示した図である。図3は、排水処理装置の洗浄方法を示す図であり、水流形成工程を示した図である。 Next, a method for cleaning the wastewater treatment device, which is executed under the control of the control unit 30, will be described. Figure 2 shows the method for cleaning the wastewater treatment device, and is a diagram showing the water level difference formation process. Figure 3 shows the method for cleaning the wastewater treatment device, and is a diagram showing the water flow formation process.

なお、圧力差を付けない通常運転時は、図1に示すように、処理槽2A,2Bにおいて各膜ユニット10,10の全体が浸漬される水位W1a,1aに設定されている。通常運転時では、制御部30の制御により、回収側開閉弁16,16及び供給側開閉弁14,14の全てが開かれており、ブロア装置19から吐出されたバイオガスが主管18及びガス供給管13,13を通じて散気管11,11から処理槽2A,2B内に散気されている。そして、処理槽2A,2B内に散気されたバイオガスは、処理槽2A,2Bの内空に放出された後、ガス回収管15,15で回収されて、回収側主管17から主管18に流入して再びブロア装置19で主管18に吐出される。つまり、通常運転時には、このような循環経路をたどって、バイオガスが循環することにより、処理槽2A,2Bが嫌気性微生物の生息に適した環境に維持されるようになっている。 During normal operation without a pressure difference, as shown in FIG. 1, the water level W1a, 1a is set in the treatment tanks 2A, 2B so that the entire membrane units 10, 10 are immersed. During normal operation, the recovery side opening/closing valves 16, 16 and the supply side opening/closing valves 14, 14 are all opened under the control of the control unit 30, and the biogas discharged from the blower device 19 is diffused into the treatment tanks 2A, 2B from the diffuser pipes 11, 11 through the main pipe 18 and the gas supply pipes 13, 13. The biogas diffused into the treatment tanks 2A, 2B is discharged into the inner space of the treatment tanks 2A, 2B, recovered by the gas recovery pipes 15, 15, flows from the recovery side main pipe 17 into the main pipe 18, and is discharged again into the main pipe 18 by the blower device 19. In other words, during normal operation, the biogas circulates through such a circulation path, thereby maintaining the treatment tanks 2A, 2B in an environment suitable for the habitation of anaerobic microorganisms.

排水処理装置1の洗浄方法は、水位差形成工程と、水流形成工程とを含んでいる。以下では、左側の処理槽2Aを洗浄対象として説明する。
水位差形成工程は、処理槽2Aと処理槽2Bとの間に圧力差を発生させて水位差を形成する工程である。具体的に、処理槽2A側では、回収側開閉弁16を開いた状態にするとともに、供給側開閉弁14を閉じた状態にする。一方、処理槽2B側では、回収側開閉弁16を閉じた状態にするとともに、供給側開閉弁14を開いた状態にする。このようにすると、処理槽2B側では、ガス回収管15が閉じられた状態で散気管11からバイオガスが供給され続けるので、処理槽2Bの内空の容積がバイオガスの滞留で大きくなり、内空の圧力が高くなる。これにより、通常運転時に図1の高さにあった処理槽2Bの水位W1aが、図2に示した低水位W1cまで押し下げられる。
The method for cleaning the wastewater treatment device 1 includes a water level difference forming step and a water flow forming step. In the following, the left treatment tank 2A will be described as the target to be cleaned.
The water level difference forming step is a step of forming a water level difference by generating a pressure difference between the treatment tanks 2A and 2B. Specifically, in the treatment tank 2A, the recovery side on-off valve 16 is opened and the supply side on-off valve 14 is closed. On the other hand, in the treatment tank 2B, the recovery side on-off valve 16 is closed and the supply side on-off valve 14 is opened. In this way, in the treatment tank 2B, biogas continues to be supplied from the aeration pipe 11 with the gas recovery pipe 15 closed, so that the internal volume of the treatment tank 2B increases due to the accumulation of biogas, and the internal pressure increases. As a result, the water level W1a of the treatment tank 2B, which is at the height shown in FIG. 1 during normal operation, is pushed down to the low water level W1c shown in FIG. 2.

そうすると、処理槽2Bに貯留されていた排水W1が連通路5を通じて処理槽2Aに流入し、通常運転時に図1の高さにあった処理槽2Aの水位W1aが、図2に示した高水位W1bまで押し上げられる。
これにより、処理槽2Aと処理槽2Bとの間に水位差が形成される。
As a result, the wastewater W1 stored in the treatment tank 2B flows into the treatment tank 2A through the connecting passage 5, and the water level W1a in the treatment tank 2A, which is at the height shown in Figure 1 during normal operation, is pushed up to the high water level W1b shown in Figure 2.
This creates a water level difference between the treatment tanks 2A and 2B.

水流形成工程は、水位差形成工程により処理槽2Aと処理槽2Bとの間に形成された水位差に基づき、水頭が高い側の処理槽2Aから水頭が低い側の処理槽2Bへ連通路5を通じて流れる水流を形成する工程である。水位差のピークは、例えば処理槽2Aの水位をセンサー等により監視することで検出できる。
水流形成工程では、処理槽2A側の回収側開閉弁16を開いた状態に維持するとともに、供給側開閉弁14を閉じた状態に維持する。一方、処理槽2B側では、回収側開閉弁16を開いた状態に切り換えるとともに、供給側開閉弁14を開いた状態に維持する。このようにすると、処理槽2Bの内空に滞留していたバイオガスがガス回収管15を通じて回収され、処理槽2Bの内空の圧力が急激に低下する。これにより、処理槽2Bの水位が、低水位W1cから通常運転時の水位W1aに上昇する。
The water flow forming step is a step of forming a water flow that flows from the treatment tank 2A with the higher water head to the treatment tank 2B with the lower water head through the communication passage 5 based on the water level difference formed between the treatment tanks 2A and 2B by the water level difference forming step. The peak of the water level difference can be detected, for example, by monitoring the water level of the treatment tank 2A with a sensor or the like.
In the water flow forming process, the recovery side on-off valve 16 on the treatment tank 2A side is kept open, and the supply side on-off valve 14 is kept closed. On the other hand, on the treatment tank 2B side, the recovery side on-off valve 16 is switched to an open state, and the supply side on-off valve 14 is kept open. In this way, the biogas that has been retained in the inner space of the treatment tank 2B is recovered through the gas recovery pipe 15, and the pressure in the inner space of the treatment tank 2B drops suddenly. As a result, the water level in the treatment tank 2B rises from the low water level W1c to the normal operation water level W1a.

そうすると、処理槽2Aに高水位W1bで貯留されていた排水W1が連通路5を通じて処理槽2Bに戻る。このとき、処理槽2Aで生じる水流は、散気管11の気泡による気液混合流の上向きの流れと逆の下向きの流れであるので、膜ユニット10の上部側に蓄積した汚濁物質を下方向に剥ぎ取るように作用する。これにより、処理槽2Aにおいて、膜ユニット10の上部側及び膜エレメントの上部側に蓄積した汚濁物質を、排水W1(被処理水)を利用して好適に除去できる。 Then, the wastewater W1 stored at the high water level W1b in the treatment tank 2A returns to the treatment tank 2B through the connecting passage 5. At this time, the water flow generated in the treatment tank 2A flows downward, opposite to the upward flow of the gas-liquid mixture flow caused by the air bubbles in the aeration pipe 11, and acts to scrape off the pollutants accumulated on the upper side of the membrane unit 10 in a downward direction. As a result, the pollutants accumulated on the upper side of the membrane unit 10 and the upper side of the membrane element in the treatment tank 2A can be suitably removed using the wastewater W1 (water to be treated).

処理槽2Bの膜ユニット10を洗浄する場合には、前記した洗浄方法と反対に、処理槽2Aの内空の圧力を高くして水位差を形成し、水頭が高い側の処理槽2Bから水頭が低い側の処理槽2Aへ連通路5を通じて流れる水流を形成する。これにより、処理槽2B側において、膜ユニット10の上部側及び膜エレメントの上部側に蓄積した汚濁物質を、排水W1(被処理水)を利用して好適に除去できる。 When cleaning the membrane unit 10 in the treatment tank 2B, the opposite of the cleaning method described above is performed: the pressure inside the treatment tank 2A is increased to create a water level difference, and a water flow is formed that flows from the treatment tank 2B with the higher water head to the treatment tank 2A with the lower water head through the communication passage 5. This allows the pollutants that have accumulated on the upper side of the membrane unit 10 and the upper side of the membrane element on the treatment tank 2B side to be effectively removed using the wastewater W1 (water to be treated).

以上説明した本実施形態の排水処理装置1では、処理槽2Aと処理槽2Bとの間に圧力差を発生させることで水位差を形成でき、例えば、水頭が高い処理槽2Aから水頭が低い処理槽2Bへ連通路5を通じて流れる水流を形成できる。処理槽2Aにおいて、この水流は、散気管11の気泡による気液混合流の上向きの流れと逆の下向きの流れであるので、膜ユニット10や膜エレメントの上部側に蓄積した汚濁物質を下方向に剥ぎ取るように作用する。これにより、膜ユニット10や膜エレメントの上部側に蓄積した汚濁物質を、排水W1(被処理水)を利用して好適に除去できる。
したがって、薬液による洗浄頻度を減少させることができる。
In the wastewater treatment device 1 of the present embodiment described above, a water level difference can be formed by generating a pressure difference between the treatment tanks 2A and 2B, and for example, a water flow can be formed that flows from the treatment tank 2A with a high water head to the treatment tank 2B with a low water head through the communication passage 5. In the treatment tank 2A, this water flow is a downward flow opposite to the upward flow of the gas-liquid mixed flow caused by the air bubbles in the aeration tube 11, and therefore acts to peel off the pollutants accumulated on the upper side of the membrane unit 10 and the membrane elements in a downward direction. This allows the pollutants accumulated on the upper side of the membrane unit 10 and the membrane elements to be suitably removed by using the wastewater W1 (water to be treated).
Therefore, the frequency of cleaning with chemicals can be reduced.

また、制御部30により両回収側開閉弁16,16及び両供給側開閉弁14,14の開閉を制御することにより、水頭圧を利用した洗浄を容易に行うことができる。例えば、制御部30により、1日に1回、一週間に1回等、所定のサイクルで洗浄を実施できる。
なお、吸引ポンプの吸引圧をセンサー等により検出して、吸引圧が所定の値より大きくなった場合に膜ユニット10に汚れが生じていると判断して、制御部30により洗浄を自動的に実施するように構成してもよい。
Furthermore, cleaning utilizing the hydraulic head pressure can be easily performed by controlling the opening and closing of both recovery side on-off valves 16, 16 and both supply side on-off valves 14, 14 by the control unit 30. For example, cleaning can be performed by the control unit 30 in a predetermined cycle, such as once a day or once a week.
In addition, the suction pressure of the suction pump may be detected by a sensor or the like, and when the suction pressure exceeds a predetermined value, it may be determined that the membrane unit 10 is dirty, and cleaning may be automatically performed by the control unit 30.

また、両ガス回収管15,15で回収されたバイオガスは、ブロア装置19を通じて両ガス供給管13,13に供給されるので、効率のよい膜ユニット10の洗浄を実現できる。 In addition, the biogas recovered in both gas recovery pipes 15, 15 is supplied to both gas supply pipes 13, 13 through a blower device 19, enabling efficient cleaning of the membrane unit 10.

また、本実施形態の排水処理装置1の洗浄方法では、水位差形成工程により処理槽2A,2Bの間に水位差を形成でき、水流形成工程により水頭が高い側から低い側に連通路5を通じて流れる水流を形成できる。この水流は、散気管11の気泡による気液混合流の上向きの流れと逆の下向きの流れであるので、膜ユニット10や膜エレメントの上部側に蓄積した汚濁物質を下方向に剥ぎ取るように作用する。これにより、膜ユニット10や膜エレメントの上部側に蓄積した汚濁物質を、排水W1(被処理水)を利用して好適に除去できる。
したがって、薬液による洗浄頻度を減少させることができる。
In the method for cleaning the wastewater treatment device 1 of this embodiment, a water level difference can be formed between the treatment tanks 2A, 2B in the water level difference forming step, and a water flow can be formed through the communication passage 5 from the side with a higher water head to the side with a lower water head in the water flow forming step. This water flow is a downward flow opposite to the upward flow of the gas-liquid mixed flow caused by the air bubbles in the aeration pipe 11, and therefore acts to peel off pollutants accumulated on the upper side of the membrane unit 10 and the membrane elements in a downward direction. This allows the pollutants accumulated on the upper side of the membrane unit 10 and the membrane elements to be suitably removed by using the wastewater W1 (water to be treated).
Therefore, the frequency of cleaning with chemicals can be reduced.

以上、本発明の実施形態について説明したが、本発明は前記実施形態に限定されることなく、その趣旨を逸脱しない範囲で適宜に変更が可能である。
例えば、前記実施形態では、ブロア装置19により散気管11に送られるバイオガスにより処理槽2Aと処理槽2Bとの間に水位差を形成する構成としたが、これに限られることはなく、ブロア装置19を用いずに、貯溜された排水W1から自然に発生するバイオガスを溜めることによって、内空の圧力を高めるように構成してもよい。
Although the embodiment of the present invention has been described above, the present invention is not limited to the above embodiment, and can be appropriately modified without departing from the spirit of the present invention.
For example, in the above embodiment, a water level difference is created between the treatment tanks 2A and 2B by the biogas sent to the aeration pipe 11 by the blower device 19. However, this is not limited to this, and the pressure in the interior may be increased by storing biogas that is naturally generated from the stored wastewater W1 without using the blower device 19.

また、前記実施形態では、隣り合う2つの処理槽2A,2Bの間に水位差を形成して洗浄を行うものについて説明したが、これに限られることはなく、図4に示すような3つの処理槽61~63と予備槽55とを有する排水処理装置60においても水位差を利用して膜ユニット10の洗浄を好適に行うことができる。
図4に示した処理槽61~63は、膜ユニット10をそれぞれ備えているとともに、2つの隔壁2a,2aに連通路5をそれぞれ備えている。そして、処理槽61~63には、同様に、ガス回収管15、回収側開閉弁16、ガス供給管13及び供給側開閉弁14がそれぞれ備わり、これらの開閉を制御する制御部30が備わる。
In the above embodiment, a water level difference is created between two adjacent treatment tanks 2A, 2B to perform cleaning. However, this is not limited to this. The membrane unit 10 can also be suitably cleaned by utilizing the water level difference in a wastewater treatment device 60 having three treatment tanks 61-63 and a reserve tank 55 as shown in FIG. 4.
4 includes a membrane unit 10, and each of the two partition walls 2a, 2a includes a communication passage 5. Similarly, each of the treatment tanks 61 to 63 includes a gas recovery pipe 15, a recovery side on-off valve 16, a gas supply pipe 13, and a supply side on-off valve 14, and a control unit 30 for controlling the opening and closing of these.

このような排水処理装置60において、例えば、処理槽61の膜ユニット10を洗浄する場合には、水位差形成工程により、処理槽61の供給側開閉弁14を閉じるとともに、処理槽62,63の各回収側開閉弁16を閉じて処理槽62,63の各内空の圧力を高くする。これにより、処理槽62,63の水位がそれぞれ下がり、代わりに処理槽61の水位が上がって処理槽61と処理槽62,63との間に水位差が形成される。 In such a wastewater treatment device 60, for example, when cleaning the membrane unit 10 of the treatment tank 61, the supply side opening/closing valve 14 of the treatment tank 61 is closed and the recovery side opening/closing valves 16 of the treatment tanks 62 and 63 are closed in the water level difference formation process to increase the pressure inside the treatment tanks 62 and 63. As a result, the water levels of the treatment tanks 62 and 63 are lowered, and instead the water level of the treatment tank 61 is raised, forming a water level difference between the treatment tank 61 and the treatment tanks 62 and 63.

水位差が形成されたら、水流形成工程により、処理槽61側において、回収側開閉弁16を開いた状態に維持するとともに、供給側開閉弁14を閉じた状態に維持する。一方、処理槽62,63側において、各回収側開閉弁16を開いた状態に切り換えるとともに、各供給側開閉弁14を開いた状態に維持する。これにより、処理槽62,63の内空の圧力がそれぞれ低下し、処理槽62,63の各水位が低水位から通常運転時の水位に上昇する。この上昇により、処理槽61から連通路5を通じて処理槽62,63に排水W1が勢いよく流入する。このときに処理槽61で生じる水流は、散気管11の気泡による気液混合流の上向きの流れと逆の下向きの流れであるので、膜ユニット10の上部側に蓄積した汚濁物質を下方向に剥ぎ取るように作用する。これにより、処理槽61において、膜ユニット10の上部側及び膜エレメントの上部側に蓄積した汚濁物質を、排水W1(被処理水)を利用して好適に除去できる。
なお、処理槽62,63の各膜ユニット10,10の洗浄についても、水位差を同様に形成することにより、汚濁物質を好適に除去できる。
以上のように、3つの処理槽61~63と予備槽55とを有する排水処理装置60について説明したが、これに限られることはなく、4つ以上の処理槽や予備槽を有する排水処理装置についても水位差を利用して膜ユニット10の洗浄を好適に行うことができる。
When the water level difference is formed, the water flow forming process maintains the recovery side on-off valve 16 in the treatment tank 61 in an open state and the supply side on-off valve 14 in a closed state. On the other hand, in the treatment tanks 62 and 63, the recovery side on-off valves 16 are switched to an open state and the supply side on-off valves 14 are maintained in an open state. As a result, the pressure in the treatment tanks 62 and 63 drops, and the water levels of the treatment tanks 62 and 63 rise from the low water level to the water level during normal operation. This rise causes the wastewater W1 to flow vigorously from the treatment tank 61 through the communication passage 5 into the treatment tanks 62 and 63. The water flow generated in the treatment tank 61 at this time is a downward flow opposite to the upward flow of the gas-liquid mixed flow caused by the air bubbles in the air diffuser 11, so it acts to strip off the polluted materials accumulated on the upper side of the membrane unit 10 in a downward direction. This allows the pollutants accumulated on the upper side of the membrane unit 10 and on the upper side of the membrane elements in the treatment tank 61 to be suitably removed by using the wastewater W1 (water to be treated).
In addition, when cleaning each of the membrane units 10, 10 in the treatment tanks 62, 63, a water level difference is similarly created, so that contaminants can be suitably removed.
As described above, the wastewater treatment device 60 having three treatment tanks 61-63 and a reserve tank 55 has been described. However, this is not limited to this, and the membrane unit 10 can also be suitably cleaned by utilizing the water level difference in wastewater treatment devices having four or more treatment tanks or reserve tanks.

1 排水処理装置
2A,2B 嫌気性排水処理槽(処理槽)
5 連通路
6 圧力差発生手段
10 膜ユニット
11 散気管
13 ガス供給管
14 供給側開閉弁
15 ガス回収管
16 回収側開閉弁
30 制御部
60 排水処理装置
61~63 処理槽
W1 排水
1 Wastewater treatment device 2A, 2B Anaerobic wastewater treatment tank (treatment tank)
5 Communication passage 6 Pressure difference generating means 10 Membrane unit 11 Aeration pipe 13 Gas supply pipe 14 Supply side opening/closing valve 15 Gas recovery pipe 16 Recovery side opening/closing valve 30 Control unit 60 Wastewater treatment device 61 to 63 Treatment tank W1 Wastewater

Claims (4)

隣接して設置された少なくとも2つの嫌気性排水処理槽と、
前記2つの嫌気性排水処理槽のそれぞれに設置され、排水をろ過する分離膜と、
前記両分離膜の下方にそれぞれ配置され、前記両分離膜に向けてガスの気泡を供給する散気管と、
前記両分離膜の下方において前記2つの嫌気性排水処理槽同士を連通する連通路と、
前記2つの嫌気性排水処理槽の間に圧力差を発生させる圧力差発生手段と、を具備したことを特徴とする排水処理装置。
At least two anaerobic wastewater treatment tanks installed adjacent to each other;
A separation membrane is installed in each of the two anaerobic wastewater treatment tanks and filters the wastewater;
an aeration tube disposed below each of the separation membranes and configured to supply gas bubbles toward each of the separation membranes;
a communication passage below the two separation membranes that communicates between the two anaerobic wastewater treatment tanks;
and a pressure difference generating means for generating a pressure difference between the two anaerobic wastewater treatment tanks.
前記圧力差発生手段は、前記2つの嫌気性排水処理槽にそれぞれ接続されるガス回収管と、前記ガス回収管に設けられた回収側開閉弁と、前記両散気管にそれぞれ接続されたガス供給管と、前記両ガス供給管に設けられた供給側開閉弁と、前記両回収側開閉弁及び前記両供給側開閉弁の開閉を制御する制御部と、を備えていることを特徴とする請求項1に記載の排水処理装置。 The wastewater treatment device according to claim 1, characterized in that the pressure difference generating means comprises a gas recovery pipe connected to each of the two anaerobic wastewater treatment tanks, a recovery side on-off valve provided in the gas recovery pipe, a gas supply pipe connected to each of the two aeration pipes, a supply side on-off valve provided in both of the gas supply pipes, and a control unit that controls the opening and closing of both of the recovery side on-off valves and both of the supply side on-off valves. 前記両ガス回収管は、ブロア装置を通じて前記両ガス供給管に接続されていることを特徴とする請求項2に記載の排水処理装置。 3. The wastewater treatment apparatus according to claim 2 , wherein the gas recovery pipes are connected to the gas supply pipes through a blower device. 隣接して設置された少なくとも2つの嫌気性排水処理槽と、前記2つの嫌気性排水処理槽のそれぞれに設置され、排水をろ過する分離膜と、前記両分離膜の下方にそれぞれ配置され、前記両分離膜に向けてガスの気泡を供給する散気管と、前記両分離膜の下方において前記2つの嫌気性排水処理槽を連通する連通路と、を備えた排水処理装置の洗浄方法であって、
前記2つの嫌気性排水処理槽の間に圧力差を発生させることで前記2つの嫌気性排水処理槽の間に水位差を形成する水位差形成工程と、
水頭が高い側の前記嫌気性排水処理槽から水頭が低い側の前記嫌気性排水処理槽へ前記連通路を通じて流れる水流を形成する水流形成工程と、を含むことを特徴とする排水処理装置の洗浄方法。
A method for cleaning a wastewater treatment device comprising at least two anaerobic wastewater treatment tanks installed adjacent to each other, a separation membrane installed in each of the two anaerobic wastewater treatment tanks for filtering wastewater, an aeration pipe disposed below each of the two separation membranes for supplying gas bubbles toward each of the two separation membranes, and a communication passage connecting the two anaerobic wastewater treatment tanks below the two separation membranes, comprising:
a water level difference generating step of generating a pressure difference between the two anaerobic wastewater treatment tanks to generate a water level difference between the two anaerobic wastewater treatment tanks;
a water flow forming step of forming a water flow that flows through the communicating passage from the anaerobic wastewater treatment tank with a higher water head to the anaerobic wastewater treatment tank with a lower water head.
JP2021131376A 2021-08-11 2021-08-11 Wastewater treatment device and method for cleaning the same Active JP7705754B2 (en)

Priority Applications (4)

Application Number Priority Date Filing Date Title
JP2021131376A JP7705754B2 (en) 2021-08-11 2021-08-11 Wastewater treatment device and method for cleaning the same
TW111128113A TWI910376B (en) 2021-08-11 2022-07-27 Drainage treatment device and cleaning method for drainage treatment device
KR1020220092907A KR20230024204A (en) 2021-08-11 2022-07-27 Wastewater treatment apparatus and method of washing wastewater treatment apparatus
CN202210960594.5A CN115888403A (en) 2021-08-11 2022-08-11 Wastewater treatment apparatus and cleaning method for wastewater treatment apparatus

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP2021131376A JP7705754B2 (en) 2021-08-11 2021-08-11 Wastewater treatment device and method for cleaning the same

Publications (2)

Publication Number Publication Date
JP2023025922A JP2023025922A (en) 2023-02-24
JP7705754B2 true JP7705754B2 (en) 2025-07-10

Family

ID=85252483

Family Applications (1)

Application Number Title Priority Date Filing Date
JP2021131376A Active JP7705754B2 (en) 2021-08-11 2021-08-11 Wastewater treatment device and method for cleaning the same

Country Status (4)

Country Link
JP (1) JP7705754B2 (en)
KR (1) KR20230024204A (en)
CN (1) CN115888403A (en)
TW (1) TWI910376B (en)

Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2006272105A (en) 2005-03-29 2006-10-12 Kubota Corp Membrane separation tank for methane fermentation treatment and method for operating the membrane separation tank
JP2010207762A (en) 2009-03-12 2010-09-24 Kubota Corp Membrane type methane fermentation treatment apparatus and method for methane fermentation treatment

Family Cites Families (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH02164498A (en) * 1988-12-15 1990-06-25 Kubota Ltd Fermentation tanks in water treatment equipment
JP3282445B2 (en) * 1995-04-28 2002-05-13 栗田工業株式会社 Biological treatment equipment
JP3234139B2 (en) 1995-10-24 2001-12-04 株式会社荏原製作所 Biological treatment method and equipment for sewage
JPH09117646A (en) 1995-10-26 1997-05-06 Hitachi Plant Eng & Constr Co Ltd Anaerobic digestion method for cleaning liquid for filter membrane and sludge containing organic matter
JP3370864B2 (en) * 1996-10-25 2003-01-27 松下電工株式会社 Septic tank
US6592751B2 (en) * 2001-09-26 2003-07-15 Council Of Scientific And Industrial Research Device for treatment of wastewater
CN202465377U (en) * 2012-01-17 2012-10-03 张华� Baffling type anaerobic bioreactor
JP7105162B2 (en) * 2018-10-04 2022-07-22 株式会社クボタ Organic wastewater treatment equipment

Patent Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2006272105A (en) 2005-03-29 2006-10-12 Kubota Corp Membrane separation tank for methane fermentation treatment and method for operating the membrane separation tank
JP2010207762A (en) 2009-03-12 2010-09-24 Kubota Corp Membrane type methane fermentation treatment apparatus and method for methane fermentation treatment

Also Published As

Publication number Publication date
JP2023025922A (en) 2023-02-24
KR20230024204A (en) 2023-02-20
TWI910376B (en) 2026-01-01
CN115888403A (en) 2023-04-04
TW202313186A (en) 2023-04-01

Similar Documents

Publication Publication Date Title
KR101115173B1 (en) Backwash
US6878282B2 (en) System and method for withdrawing permeate through a filter and for cleaning the filter in situ
US7585411B2 (en) Low pressure filtration
JP2010501340A (en) Low pressure backwash
JP5182413B2 (en) Immersion type membrane separator, method of cleaning a diffuser and membrane separation method
JP6271109B1 (en) Water treatment membrane cleaning apparatus and method, and water treatment system
CN113966249B (en) Filter membrane cleaning device, filter membrane cleaning method and water treatment system
JP5181987B2 (en) Cleaning method for submerged membrane module
JP6411051B2 (en) Immersion membrane separator and method for operating the same
JP7705754B2 (en) Wastewater treatment device and method for cleaning the same
CN101472670A (en) Running method of membrane separation device
JP2012061432A (en) Air diffuser and method of operating membrane separation device
JP7325694B1 (en) Filtration membrane cleaning device
JP5423184B2 (en) Filtration membrane module cleaning method and cleaning apparatus
JP2006081979A (en) Membrane cleaning method
JP2009214062A (en) Operation method of immersion type membrane module
JP2011041907A (en) Water treatment system
JP2006263716A (en) Immersion type membrane separator, method of cleaning a diffuser and membrane separation method
JP5251472B2 (en) Membrane module cleaning method
JP2016137469A (en) Method and device for cleaning air diffusion pipe, and activated sludge treatment method and activated sludge treatment system
JP7067678B1 (en) Filtration membrane cleaning equipment, water treatment equipment and filtration membrane cleaning method
JP2007209949A (en) Filtrate recovery device for solid-liquid mixed processing liquid
JP2003305313A (en) Solid-liquid separation method and apparatus therefor
KR101263561B1 (en) 2-phase flow inducing type MBR system having submerged membrane module
JPH11114563A (en) Water treatment equipment

Legal Events

Date Code Title Description
A621 Written request for application examination

Free format text: JAPANESE INTERMEDIATE CODE: A621

Effective date: 20240314

A977 Report on retrieval

Free format text: JAPANESE INTERMEDIATE CODE: A971007

Effective date: 20241118

A131 Notification of reasons for refusal

Free format text: JAPANESE INTERMEDIATE CODE: A131

Effective date: 20250107

A521 Request for written amendment filed

Free format text: JAPANESE INTERMEDIATE CODE: A523

Effective date: 20250310

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: 20250624

A61 First payment of annual fees (during grant procedure)

Free format text: JAPANESE INTERMEDIATE CODE: A61

Effective date: 20250630

R150 Certificate of patent or registration of utility model

Ref document number: 7705754

Country of ref document: JP

Free format text: JAPANESE INTERMEDIATE CODE: R150