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
JP7773455B2 - septic tank - Google Patents
[go: Go Back, main page]

JP7773455B2 - septic tank - Google Patents

septic tank

Info

Publication number
JP7773455B2
JP7773455B2 JP2022159519A JP2022159519A JP7773455B2 JP 7773455 B2 JP7773455 B2 JP 7773455B2 JP 2022159519 A JP2022159519 A JP 2022159519A JP 2022159519 A JP2022159519 A JP 2022159519A JP 7773455 B2 JP7773455 B2 JP 7773455B2
Authority
JP
Japan
Prior art keywords
water
baffle
treated
receiving surface
tank
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
JP2022159519A
Other languages
Japanese (ja)
Other versions
JP2024053327A (en
Inventor
信彦 西川
光希 西田
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.)
Kubota Corp
Original Assignee
Kubota Corp
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 Kubota Corp filed Critical Kubota Corp
Priority to JP2022159519A priority Critical patent/JP7773455B2/en
Publication of JP2024053327A publication Critical patent/JP2024053327A/en
Application granted granted Critical
Publication of JP7773455B2 publication Critical patent/JP7773455B2/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Classifications

    • 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

  • Treatment Of Biological Wastes In General (AREA)

Description

本発明は、被処理水の水処理を行う水処理部と、前記水処理部へと被処理水が流入する流入部と、前記流入部に接続されているバッフルと、を備える浄化槽に関する。 The present invention relates to a septic tank equipped with a water treatment unit that treats water to be treated, an inlet through which the water to be treated flows into the water treatment unit, and a baffle connected to the inlet.

従来の浄化槽には、流入部から流れてきた被処理水が浄化槽の水処理部に流入する際、水面に浮上しているスカム(汚泥の塊)が被処理水の勢いで破砕しないように、バッフル部材が設けられている。 Conventional septic tanks are equipped with baffles to prevent the scum (lumps of sludge) floating on the water surface from being crushed by the force of the water being treated when the water flowing from the inlet flows into the water treatment section of the septic tank.

また、バッフル部材を通過した被処理水が勢いよく水処理部の底部に向かうと、底部に堆積した汚泥を撹拌して巻き上げてしまうことになる。そのため、バッフル部材の、流入部と対向する壁面に被処理水を受けるような受け部分を設けて、その受け部分で被処理水の勢いを低減することによって、堆積した汚泥の巻き上げを防ぐようにしている。 Furthermore, if the water to be treated passes through the baffle member and heads toward the bottom of the water treatment unit with force, it will stir up and stir up the sludge that has accumulated at the bottom. For this reason, a receiving section is provided on the wall of the baffle member opposite the inlet section to receive the water to be treated. By reducing the force of the water to be treated in this receiving section, the sludge that has accumulated there is prevented from being stirred up.

特開2004-136187号公報Japanese Patent Application Laid-Open No. 2004-136187

従来の浄化槽では、流入部と、それに対向するバッフル部材の壁面との間に比較的大きな距離が設けられている。そのため、被処理水の流入水量が比較的多い場合は、バッフル部材の受け部分が機能するが、被処理水の流入水量が少ない場合は、被処理水が受け部分を通過し難くなるため、汚泥の巻き上げを防ぐ効果が得られ難くなる。 In conventional septic tanks, there is a relatively large distance between the inlet and the wall of the baffle member facing it. Therefore, when the inflow rate of water to be treated is relatively high, the receiving portion of the baffle member functions properly, but when the inflow rate of water to be treated is low, the water to be treated has difficulty passing through the receiving portion, making it difficult to prevent sludge from being stirred up.

本発明は上記実情に鑑みてなされたものであって、その目的は、被処理水の流入水量によらず被処理水の勢いを低減することのできるバッフルを備える浄化槽を提供することにある。 The present invention was made in consideration of the above-mentioned circumstances, and its purpose is to provide a septic tank equipped with a baffle that can reduce the momentum of the water being treated regardless of the amount of water flowing into it.

本発明に係る浄化槽の特徴は、被処理水の水処理を行う水処理部と、前記水処理部へと被処理水が流入する流入部と、前記流入部に接続されているバッフルと、を備える浄化槽において、
前記流入部の正面に位置する前記バッフルの正面壁に、被処理水を受けるための横方向に延びる横方向受け面が形成されており、
被処理水を移送可能な配管が、前記流入部から前記バッフルの正面壁の側に向かって延伸しており、前記配管の開口より排出された被処理水が、前記横方向受け面で受けられた後に前記バッフルの流出口から排出されるように構成される点にある。
The feature of the septic tank according to the present invention is that the septic tank includes a water treatment unit that treats water to be treated, an inlet through which the water to be treated flows into the water treatment unit, and a baffle connected to the inlet.
a lateral receiving surface extending laterally for receiving the water to be treated is formed on a front wall of the baffle located in front of the inlet portion,
A pipe capable of transporting the water to be treated extends from the inlet toward the front wall of the baffle, and the water to be treated discharged from the opening of the pipe is received by the lateral receiving surface and then discharged from the outlet of the baffle.

本発明に係る浄化槽においては、前記バッフルの正面壁が、前記バッフルの底部より立ち上がる縦面と、前記縦面に連設する前記横方向受け面と、前記横方向受け面に連設して縦方向に延びる縦方向受け面とを備えると好適である。 In the septic tank of the present invention, it is preferable that the front wall of the baffle has a vertical surface rising from the bottom of the baffle, a horizontal support surface connected to the vertical surface, and a vertical support surface connected to the horizontal support surface and extending vertically.

本発明に係る浄化槽においては、前記横方向受け面が、前記流入部の側に傾斜していると好適である。 In the septic tank of the present invention, it is preferable that the lateral receiving surface is inclined toward the inlet.

本発明に係る浄化槽においては、前記横方向受け面の水平面に対する傾斜角度が20°~35°であると好適である。 In the septic tank of the present invention, it is preferable that the inclination angle of the lateral receiving surface relative to the horizontal plane be between 20° and 35°.

本発明に係る浄化槽においては、前記配管の開口が、前記バッフルの正面壁の下端部の略真上か、もしくは前記横方向受け面の上方に位置すると好適である。 In the septic tank of the present invention, it is preferable that the opening of the piping be located approximately directly above the lower end of the front wall of the baffle or above the lateral support surface.

本発明に係る浄化槽においては、前記横方向受け面における前記流入部の側の端部と、前記配管の開口との間の水平方向における距離が、10mm~20mmであると好適である。 In the septic tank of the present invention, it is preferable that the horizontal distance between the end of the lateral support surface on the inlet side and the opening of the piping is 10 mm to 20 mm.

被処理水を移送可能な配管が、流入部からバッフルの正面壁の側に向かって延伸している。これにより、配管の開口より排出された被処理水は、バッフルの横方向受け面で受けられた後にバッフルの流出口から排出されるように構成されている。そのため、たとえ被処理水の流入水量が少ない場合であっても、被処理水の勢いを低減することができる。従って、本発明におけるバッフルによれば、被処理水の流入水量によらずその勢いを低減することが可能であり、その結果、固液分離槽の槽底部に堆積した汚泥が撹拌及び巻き上げられることが抑制されるため、次槽以降への汚泥の流出が低減される。さらに、汚泥の静置状態が継続されるため、汚泥の圧密化と濃縮化が進み、汚泥以外の空間が増えることで、次槽以降への汚泥の流出がさらに軽減される。 A pipe capable of transporting untreated water extends from the inlet toward the front wall of the baffle. As a result, untreated water discharged from the opening of the pipe is received by the lateral receiving surface of the baffle before being discharged from the baffle's outlet. This allows the momentum of the untreated water to be reduced even when the inflow rate of the untreated water is small. Therefore, the baffle of the present invention makes it possible to reduce the momentum of the untreated water regardless of the inflow rate of the untreated water. As a result, the sludge accumulated at the bottom of the solid-liquid separation tank is prevented from being stirred up and stirred up, thereby reducing the outflow of sludge to subsequent tanks. Furthermore, because the sludge remains stationary, it becomes more compacted and thickened, increasing the amount of space other than sludge, further reducing the outflow of sludge to subsequent tanks.

浄化槽の概略構成を示した縦断側面図である。FIG. 1 is a vertical cross-sectional side view showing the schematic configuration of a septic tank. 浄化槽の概略構成を示した横断平面図である。FIG. 1 is a cross-sectional plan view showing a schematic configuration of a septic tank. バッフルの概略構成を示した縦断側面図である。FIG. 2 is a vertical cross-sectional side view showing a schematic configuration of a baffle. バッフルにおける被処理水の流れを示す説明図である。FIG. 4 is an explanatory diagram showing the flow of water to be treated in a baffle. 別実施形態のバッフルの概略構成を示した縦断側面図である。FIG. 10 is a vertical cross-sectional side view showing a schematic configuration of a baffle according to another embodiment. 別実施形態のバッフルにおける被処理水の流れを示す説明図である。FIG. 10 is an explanatory diagram showing the flow of water to be treated in a baffle according to another embodiment.

以下、図面に基づいて、本発明に係る浄化槽の実施形態を説明する。
〔浄化槽〕
図1及び図2に示すように、本実施形態に係る浄化槽1の本体内部には、固液分離槽2(水処理部の一例)、嫌気ろ床槽3、担体流動槽4、処理水槽5、及び消毒槽6が備えられている。尚、本実施形態においては、浄化槽1の長手方向というときは、浄化槽1における固液分離槽2、嫌気ろ床槽3、及び担体流動槽4が並ぶ方向を指し、浄化槽1の幅方向とは、平面視において長手方向と直交する方向を指すものとする。
Hereinafter, an embodiment of a septic tank according to the present invention will be described with reference to the drawings.
[Septic tank]
1 and 2, the main body of the septic tank 1 according to this embodiment is equipped with a solid-liquid separation tank 2 (an example of a water treatment unit), an anaerobic filter bed tank 3, a carrier fluidized bed tank 4, a treated water tank 5, and a disinfection tank 6. In this embodiment, the longitudinal direction of the septic tank 1 refers to the direction in which the solid-liquid separation tank 2, anaerobic filter bed tank 3, and carrier fluidized bed tank 4 are aligned in the septic tank 1, and the width direction of the septic tank 1 refers to the direction perpendicular to the longitudinal direction in a plan view.

被処理水Wの原水は、流入部7から固液分離槽2に流入し、嫌気ろ床槽3、担体流動槽4、処理水槽5、消毒槽6の順に移送され、各槽において処理が施された後、放流口8から槽外に放流される。 The raw water to be treated (W) flows into the solid-liquid separation tank 2 through the inlet 7, and is then transported through the anaerobic filter bed tank 3, the carrier fluidized bed tank 4, the treated water tank 5, and the disinfection tank 6 in that order. After being treated in each tank, the water is discharged from the discharge port 8.

固液分離槽2は、流入部7から流入した被処理水Wを受けて一時貯留するように構成されている。固液分離槽2によって、被処理水W中に含まれる比較的大きな夾雑物、固形物等が重力沈降により分離されて、槽上部にスカム等の浮遊性の懸濁物質が貯留されると共に、槽底部に汚泥が貯留される。 The solid-liquid separation tank 2 is configured to receive and temporarily store the water to be treated W that flows in from the inlet 7. The solid-liquid separation tank 2 separates relatively large impurities, solids, etc. contained in the water to be treated W by gravitational settling, and floating suspended matter such as scum is stored in the upper part of the tank, while sludge is stored in the bottom of the tank.

嫌気ろ床槽3は、嫌気ろ材30を備えており、被処理水Wが嫌気ろ材30を通過する際に、浮遊物質の分離と嫌気性微生物の働きによる有機物の分解、及び硝酸性・亜硝酸性窒素の脱窒が実施される。 The anaerobic filter bed tank 3 is equipped with anaerobic filter material 30. As the water to be treated W passes through the anaerobic filter material 30, suspended solids are separated, organic matter is decomposed by anaerobic microorganisms, and nitrate and nitrite nitrogen are denitrified.

本実施形態における担体流動槽4は、図示しない流動担体と散気管とを備える。 In this embodiment, the carrier fluidization tank 4 is equipped with a fluidized carrier and an aeration tube (not shown).

担体流動槽4は、微生物を担持した状態で被処理水Wと共に流動可能な複数の流動担体を収容保持する。流動担体の一例としては、例えば、比重約1.01、大きさ20mm×20mmの角形スポンジ状担体が挙げられる。また流動担体の素材としては、例えばポリウレタン(PU)が挙げられる。尚、流動担体の形状、大きさ、素材については上記構成に限定されるものではなく、耐久性や処理性能が同等以上と判断され得るような構成であればどのような構成であっても良い。 The carrier fluidization tank 4 contains and holds multiple fluidized carriers that carry microorganisms and can flow with the water to be treated W. One example of a fluidized carrier is a square sponge-like carrier with a specific gravity of approximately 1.01 and dimensions of 20 mm x 20 mm. The material of the fluidized carrier is, for example, polyurethane (PU). The shape, size, and material of the fluidized carrier are not limited to the above configurations, and any configuration may be used as long as it is deemed to have equivalent or better durability and treatment performance.

散気管は、担体流動槽4の槽底部の近傍に設けられており、槽外に設置された図示しないブロワからの空気供給により、散気管から気泡が放出されるように構成されている。 The air diffuser is located near the bottom of the carrier fluidized bed 4, and is configured so that air bubbles are released from the air diffuser by air supply from a blower (not shown) installed outside the bed.

散気管から気泡が放出されると、気泡が担体流動槽4に供給される。これにより流動担体が担体流動槽4内を旋回流動し、このとき担体流動槽4では、流動担体に付着した微生物の働きによって有機物の好気分解及びアンモニア態窒素の硝化反応が行われる。 When bubbles are released from the aeration pipe, they are supplied to the carrier fluidized bed 4. This causes the fluidized bed to swirl within the carrier fluidized bed 4, where the microorganisms attached to the fluidized bed carry out aerobic decomposition of organic matter and nitrification of ammonia nitrogen.

担体流動槽4で処理された被処理水Wは、担体流動槽4と処理水槽5とを仕切る隔壁の下部に設けられている移流部を介して、処理水槽5に流れる。 The water to be treated W treated in the carrier fluidization tank 4 flows into the treatment tank 5 via a convection section located at the bottom of the partition separating the carrier fluidization tank 4 and the treatment tank 5.

また担体流動槽4における、処理水槽5と隣接する位置には、循環用のエアリフトポンプAPが設けられており、剥離汚泥と被処理水Wの一部が循環水として、循環返送管を介して固液分離槽2におけるバッフル9に常時移送されるように構成されている。尚、エアリフトポンプAPには、槽外に設置された図示しないブロワから空気が供給される。 In addition, a circulation air lift pump AP is installed in the carrier fluidization tank 4 adjacent to the treated water tank 5, and is configured so that the exfoliated sludge and a portion of the water to be treated W are constantly transferred as circulating water to the baffle 9 in the solid-liquid separation tank 2 via the circulation return pipe. Air is supplied to the air lift pump AP from a blower (not shown) installed outside the tank.

処理水槽5は、担体流動槽4で処理された被処理水Wを一時的に貯留すると共に、担体流動槽4で捕捉できなかった剥離汚泥等を分離し、汚泥の流出を防止する。 The treated water tank 5 temporarily stores the water W treated in the carrier fluidization tank 4, and separates any exfoliated sludge that could not be captured in the carrier fluidization tank 4, preventing the sludge from leaking out.

処理水槽5で処理された被処理水Wは、処理水槽5と消毒槽6とを仕切る隔壁の上部に設けられている移流部を通ってオーバーフローにより消毒槽6の消毒装置(図示せず)に流れる。消毒装置で消毒剤と接触して消毒された被処理水Wは、放流口8から槽外方に放流される。 The water to be treated W treated in the treatment tank 5 flows through a convection section installed at the top of the partition separating the treatment tank 5 and the disinfection tank 6 and overflows into the disinfection device (not shown) in the disinfection tank 6. The water to be treated W disinfected by coming into contact with a disinfectant in the disinfection device is then discharged outside the tank from the discharge port 8.

〔バッフル〕
本実施形態におけるバッフル9は、流入部7の正面に位置する正面壁90と、正面壁90の向かい側に位置する背面壁91と、幅方向に対面配置される右側面壁92及び左側面壁93と、底部94とを有する、横断面が略矩形の部材である。
[Baffle]
In this embodiment, the baffle 9 is a member with an approximately rectangular cross section, having a front wall 90 located in front of the inlet section 7, a rear wall 91 located opposite the front wall 90, a right side wall 92 and a left side wall 93 arranged opposite each other in the width direction, and a bottom 94.

バッフル9は、背面壁91を介して流入部7に接続されている。そして、被処理水Wを移送可能な配管70が、流入部7に嵌め込まれている。尚、配管70については、流入部7と一体に構成してあっても良い。 The baffle 9 is connected to the inlet section 7 via the rear wall 91. A pipe 70 capable of transporting the water to be treated W is fitted into the inlet section 7. Note that the pipe 70 may be configured integrally with the inlet section 7.

バッフル9の正面壁90には、被処理水Wを受けるための横方向に延びる横方向受け面902が形成されている。横方向受け面902は、被処理水Wの水位WLよりも常に下にある位置に設けられている。 A lateral receiving surface 902 extending laterally is formed on the front wall 90 of the baffle 9 to receive the water to be treated W. The lateral receiving surface 902 is located at a position that is always below the water level WL of the water to be treated W.

本実施形態においては、被処理水Wが流出する流出口95は、バッフル9の底部94に形成されている。 In this embodiment, the outlet 95 through which the treated water W flows out is formed in the bottom 94 of the baffle 9.

被処理水Wを移送可能な配管70が、流入部7からバッフル9の正面壁90の側に向かって延伸している。これにより、配管70の開口71より排出された被処理水Wは、バッフル9の横方向受け面902で受けられた後にバッフル9の流出口95から排出されるように構成されている。 A pipe 70 capable of transporting the water to be treated W extends from the inlet 7 toward the front wall 90 of the baffle 9. As a result, the water to be treated W discharged from the opening 71 of the pipe 70 is received by the lateral receiving surface 902 of the baffle 9 and then discharged from the outlet 95 of the baffle 9.

そのため、たとえ被処理水Wの流入水量が少ない場合であっても、被処理水Wの勢いを低減することができる。従って、本実施形態におけるバッフル9によれば、被処理水Wの流入水量によらずその勢いを低減することが可能であり、その結果、固液分離槽2の槽底部に堆積した汚泥が撹拌及び巻き上げられることが抑制されるため、次槽(本実施形態では嫌気ろ床槽3)以降への汚泥の流出が低減される。さらに、汚泥の静置状態が継続されるため、汚泥の圧密化と濃縮化が進み、汚泥以外の空間が増えることで、次槽以降への汚泥の流出がさらに軽減される。 As a result, even if the inflow volume of the water to be treated W is small, the momentum of the water to be treated W can be reduced. Therefore, the baffle 9 in this embodiment makes it possible to reduce the momentum of the water to be treated W regardless of the inflow volume of the water to be treated W. As a result, the sludge accumulated at the bottom of the solid-liquid separation tank 2 is prevented from being stirred up and stirred up, thereby reducing the outflow of sludge to the next tank (anaerobic filter bed tank 3 in this embodiment) and beyond. Furthermore, because the sludge continues to remain stationary, the sludge becomes more compacted and thickened, and the space other than the sludge increases, further reducing the outflow of sludge to the next tank and beyond.

また本実施形態においては、バッフル9の正面壁90には、バッフル9の底部94より立ち上がる縦面901と、縦面901に連設する横方向受け面902と、横方向受け面902に連設して縦方向に延びる縦方向受け面903とが形成されている。 In this embodiment, the front wall 90 of the baffle 9 is formed with a vertical surface 901 rising from the bottom 94 of the baffle 9, a horizontal receiving surface 902 connected to the vertical surface 901, and a vertical receiving surface 903 connected to the horizontal receiving surface 902 and extending vertically.

本実施形態における配管70の開口71は、バッフル9の正面壁90の下端部の略真上に位置する。尚、配管70の開口71の位置については、これに限らず、横方向受け面902の上方に位置するようにしても良い。 In this embodiment, the opening 71 of the piping 70 is located approximately directly above the lower end of the front wall 90 of the baffle 9. However, the position of the opening 71 of the piping 70 is not limited to this, and it may also be located above the lateral receiving surface 902.

本実施形態に示されるように、横方向受け面902は、流入部7の側に傾斜していると良い。その際、横方向受け面902の水平面に対する傾斜角度θは20°~35°であることが望ましい。 As shown in this embodiment, the lateral receiving surface 902 is preferably inclined toward the inlet 7. In this case, the inclination angle θ of the lateral receiving surface 902 relative to the horizontal plane is preferably between 20° and 35°.

これにより、図4に示すように、配管70の開口71より排出された被処理水Wは、バッフル9の横方向受け面902で受けられた後に、横方向受け面902が流入部7の側に傾斜していることにより流入方向とは逆方向である背面壁91の側に向かって流れて、その後下降して、流出口95から排出される。また、横方向受け面902の水平面に対する傾斜角度θが、急傾斜でもなく、平ら過ぎでもなく、適度な傾斜である20°~35°であることで、被処理水Wの流下速度を減速させることができ、かつ被処理水W中に含まれる固形物等が横方向受け面902の水平面に堆積することもなく、円滑に流下することができる。即ち、バッフル9内の空間がより有効に活用されて、被処理水Wの勢いをより確実に低減することができる。 As a result, as shown in FIG. 4, the untreated water W discharged from the opening 71 of the pipe 70 is received by the lateral receiving surface 902 of the baffle 9. Because the lateral receiving surface 902 is inclined toward the inlet section 7, the untreated water W flows toward the rear wall 91, which is in the opposite direction to the inflow direction, and then descends and is discharged from the outlet 95. Furthermore, the inclination angle θ of the lateral receiving surface 902 relative to the horizontal plane is neither too steep nor too flat, but is a moderate inclination of 20° to 35°. This allows the flow rate of the untreated water W to be slowed down, and solids contained in the untreated water W do not accumulate on the horizontal surface of the lateral receiving surface 902, allowing the water to flow smoothly downward. In other words, the space within the baffle 9 is utilized more effectively, and the momentum of the untreated water W can be more reliably reduced.

また、配管70の開口71が横方向受け面902の上方に位置していない場合は、横方向受け面902における流入部7の側の端部と、配管70の開口71との間の水平方向における距離Tを、10mm~20mmとすることが望ましい。 Furthermore, if the opening 71 of the pipe 70 is not located above the lateral receiving surface 902, it is desirable that the horizontal distance T between the end of the lateral receiving surface 902 on the inlet section 7 side and the opening 71 of the pipe 70 be 10 mm to 20 mm.

〔その他の実施形態〕
上述の実施形態においては、被処理水Wが抽出する流出口95が、バッフル9の底部94に形成してある構成が示されているが、この構成に限定されるものでなく、例えば、図5及び図6に示すように、被処理水Wが流出する流出口95が、バッフル9の右側面壁92及び左側面壁93のそれぞれにおける底部94近くの下部に形成されている構成としても良い。また、流出口95をバッフル9の側壁に設ける場合は、側壁の前後左右のいずれでもよく、即ち本実施形態では、正面壁90、背面壁91(浄化槽本体との間に隙間がある場合)、右側面壁92、左側面壁93のいずれでもよく、また一か所、もしくは複数か所に設ける構成としても良い。
Other Embodiments
In the above-described embodiment, the outlet 95 through which the water to be treated W is extracted is formed in the bottom 94 of the baffle 9, but the present invention is not limited to this configuration. For example, as shown in Figures 5 and 6, the outlet 95 through which the water to be treated W flows may be formed in the lower part near the bottom 94 of each of the right side wall 92 and the left side wall 93 of the baffle 9. Furthermore, when the outlet 95 is provided in a side wall of the baffle 9, it may be provided on any of the front, rear, left and right sides of the side wall. That is, in this embodiment, it may be provided on any of the front wall 90, the rear wall 91 (if there is a gap between the septic tank body), the right side wall 92, and the left side wall 93, and may be provided in one location or in multiple locations.

尚、上述のように図面を参照しつつ本発明を説明したが、本発明は当該図面の構成に限定されるものではなく、本発明の要旨を逸脱しない範囲において様々な態様で実施することができることは言うまでもない。 Although the present invention has been described above with reference to the drawings, it goes without saying that the present invention is not limited to the configuration shown in the drawings, and can be embodied in various forms without departing from the spirit and scope of the present invention.

本発明に係る浄化槽は、小型の浄化槽だけでなく、中型及び大型の浄化槽にも適用することができる。 The septic tank of the present invention can be applied not only to small septic tanks, but also to medium-sized and large septic tanks.

1 浄化槽
2 固液分離槽(水処理部の一例)
3 嫌気ろ床槽
30 嫌気ろ材
4 担体流動槽
5 処理水槽
6 消毒槽
7 流入部
70 配管
71 開口
8 放流口
9 バッフル
90 正面壁
901 縦面
902 横方向受け面
903 縦方向受け面
91 背面壁
92 右側面壁
93 左側面壁
94 底部
95 流出口
W 被処理水
WL 水位
AP エアリフトポンプ
T 距離
θ 傾斜角度
1 Purification tank 2 Solid-liquid separation tank (an example of a water treatment unit)
3 Anaerobic filter bed tank 30 Anaerobic filter material 4 Carrier fluidized bed tank 5 Treated water tank 6 Disinfection tank 7 Inlet 70 Pipe 71 Opening 8 Discharge port 9 Baffle 90 Front wall 901 Vertical surface 902 Horizontal receiving surface 903 Vertical receiving surface 91 Back wall 92 Right side wall 93 Left side wall 94 Bottom 95 Outlet W Treated water WL Water level AP Air lift pump T Distance θ Tilt angle

Claims (4)

被処理水の水処理を行う水処理部と、前記水処理部へと被処理水が流入する流入部と、前記流入部に接続されているバッフルと、を備える浄化槽において、
前記流入部の正面に位置する前記バッフルの正面壁に、被処理水を受けるための横方向に延びる横方向受け面が形成されており、
被処理水を移送可能な配管が、前記流入部から前記バッフルの正面壁の側に向かって延伸しており、前記配管の開口より排出された被処理水が、前記横方向受け面で受けられた後に前記バッフルの流出口から排出されるように構成され
前記バッフルの正面壁が、前記バッフルの底部より立ち上がる縦面と、前記縦面に連設する前記横方向受け面と、前記横方向受け面に連設して縦方向に延びる縦方向受け面とを備え、
前記配管の開口が、前記バッフルの正面壁の下端部の略真上か、もしくは前記横方向受け面の上方に位置する浄化槽。
A septic tank comprising a water treatment unit that treats water to be treated, an inlet through which the water to be treated flows into the water treatment unit, and a baffle connected to the inlet,
a lateral receiving surface extending laterally for receiving the water to be treated is formed on a front wall of the baffle located in front of the inlet portion,
A pipe capable of transporting the water to be treated extends from the inlet portion toward the front wall side of the baffle, and the water to be treated discharged from the opening of the pipe is received by the lateral receiving surface and then discharged from the outlet of the baffle ,
a front wall of the baffle including a vertical surface rising from a bottom of the baffle, a horizontal receiving surface connected to the vertical surface, and a vertical receiving surface connected to the horizontal receiving surface and extending in the vertical direction;
A septic tank in which the opening of the piping is located approximately directly above the lower end of the front wall of the baffle or above the lateral support surface .
被処理水の水処理を行う水処理部と、前記水処理部へと被処理水が流入する流入部と、前記流入部に接続されているバッフルと、を備える浄化槽において、
前記流入部の正面に位置する前記バッフルの正面壁に、被処理水を受けるための横方向に延びる横方向受け面が形成されており、
被処理水を移送可能な配管が、前記流入部から前記バッフルの正面壁の側に向かって延伸しており、前記配管の開口より排出された被処理水が、前記横方向受け面で受けられた後に前記バッフルの流出口から排出されるように構成され、
前記バッフルの正面壁が、前記バッフルの底部より立ち上がる縦面と、前記縦面に連設する前記横方向受け面と、前記横方向受け面に連設して縦方向に延びる縦方向受け面とを備え、
前記横方向受け面における前記流入部の側の端部と、前記配管の開口との間の水平方向における距離が、10mm~20mmである浄化槽
A septic tank comprising a water treatment unit that treats water to be treated, an inlet through which the water to be treated flows into the water treatment unit, and a baffle connected to the inlet,
a lateral receiving surface extending laterally for receiving the water to be treated is formed on a front wall of the baffle located in front of the inlet portion,
A pipe capable of transporting the water to be treated extends from the inlet portion toward the front wall side of the baffle, and the water to be treated discharged from the opening of the pipe is received by the lateral receiving surface and then discharged from the outlet of the baffle,
a front wall of the baffle including a vertical surface rising from a bottom of the baffle, a horizontal receiving surface connected to the vertical surface, and a vertical receiving surface connected to the horizontal receiving surface and extending in the vertical direction;
A septic tank in which the horizontal distance between the end of the lateral receiving surface on the side of the inlet portion and the opening of the piping is 10 mm to 20 mm .
前記横方向受け面が、前記流入部の側に傾斜している請求項1又は2に記載の浄化槽。 3. The septic tank according to claim 1 , wherein the lateral receiving surface is inclined toward the inlet portion. 前記横方向受け面の水平面に対する傾斜角度が20°~35°である請求項3に記載の浄化槽。 The septic tank according to claim 3, wherein the inclination angle of the lateral receiving surface relative to the horizontal plane is between 20° and 35°.
JP2022159519A 2022-10-03 2022-10-03 septic tank Active JP7773455B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP2022159519A JP7773455B2 (en) 2022-10-03 2022-10-03 septic tank

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP2022159519A JP7773455B2 (en) 2022-10-03 2022-10-03 septic tank

Publications (2)

Publication Number Publication Date
JP2024053327A JP2024053327A (en) 2024-04-15
JP7773455B2 true JP7773455B2 (en) 2025-11-19

Family

ID=90667431

Family Applications (1)

Application Number Title Priority Date Filing Date
JP2022159519A Active JP7773455B2 (en) 2022-10-03 2022-10-03 septic tank

Country Status (1)

Country Link
JP (1) JP7773455B2 (en)

Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2016120471A (en) 2014-12-25 2016-07-07 フジクリーン工業株式会社 Baffle
JP2020182895A (en) 2019-05-07 2020-11-12 株式会社ハウステック Water treatment apparatus and its operation method

Patent Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2016120471A (en) 2014-12-25 2016-07-07 フジクリーン工業株式会社 Baffle
JP2020182895A (en) 2019-05-07 2020-11-12 株式会社ハウステック Water treatment apparatus and its operation method

Also Published As

Publication number Publication date
JP2024053327A (en) 2024-04-15

Similar Documents

Publication Publication Date Title
KR100409056B1 (en) Aerobic treatment method and treatment tank of sewage
JP5665307B2 (en) Organic waste water treatment apparatus and organic waste water treatment method
KR100942716B1 (en) Aerobic and Anaerobic Digestion Apparatus and Method by Plug Flow Reactor
JP4119997B2 (en) Wastewater septic tank
JP7773455B2 (en) septic tank
JP7182944B2 (en) septic tank
JP4702749B2 (en) Water treatment equipment
CN108147534A (en) Nitration denitrification integrated bioreactor
JP3263267B2 (en) Septic tank
JP2008272702A (en) Consolidated septic tank
JP5814583B2 (en) Septic tank
KR20050109743A (en) Apparatus for purificating of closed water area by rapid cohesive precipitation
JP2001079576A (en) Septic tank
JP2000271583A (en) Septic tank
JP5818360B2 (en) Moving bed type filtration tank and septic tank equipped with moving bed type filtration tank
KR101180338B1 (en) a sewage disposal plant
JP4022815B2 (en) Solid-liquid separation tank and sewage septic tank having a filter medium layer in the second chamber
JP2007117908A (en) Septic tank
JP5647556B2 (en) Septic tank
CN103459331B (en) Sewage purifier
JP2008012491A (en) Aerobic digestion tank and sewage cleaning tank equipped with the same
KR102611416B1 (en) Waste water treatment system with bubbling device
CN218371944U (en) Aerobic three-phase separator and reactor
CN104379511A (en) Filtration and airlift dual-purpose device and water treatment system
JP4598705B2 (en) Septic tank

Legal Events

Date Code Title Description
A621 Written request for application examination

Free format text: JAPANESE INTERMEDIATE CODE: A621

Effective date: 20241213

A131 Notification of reasons for refusal

Free format text: JAPANESE INTERMEDIATE CODE: A131

Effective date: 20250805

A521 Request for written amendment filed

Free format text: JAPANESE INTERMEDIATE CODE: A523

Effective date: 20250912

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: 20251029

A61 First payment of annual fees (during grant procedure)

Free format text: JAPANESE INTERMEDIATE CODE: A61

Effective date: 20251107

R150 Certificate of patent or registration of utility model

Ref document number: 7773455

Country of ref document: JP

Free format text: JAPANESE INTERMEDIATE CODE: R150