JP2005199277A - Septic tank - Google Patents

Septic tank Download PDF

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JP2005199277A
JP2005199277A JP2005102645A JP2005102645A JP2005199277A JP 2005199277 A JP2005199277 A JP 2005199277A JP 2005102645 A JP2005102645 A JP 2005102645A JP 2005102645 A JP2005102645 A JP 2005102645A JP 2005199277 A JP2005199277 A JP 2005199277A
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tank
water
treated
solid
septic tank
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JP4435711B2 (en
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Teru Chin
暉 陳
Norifumi Nakanishi
法文 中西
Hideaki Tsuzuki
秀昭 都築
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Daiei Sangyo Co Ltd
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Daiei Sangyo Co Ltd
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Abstract

<P>PROBLEM TO BE SOLVED: To provide a septic tank in which a discharging pipe bottom can be made shallow and thereby construction work becomes easy. <P>SOLUTION: In the septic tank, an internal part is divided into two or more chambers, a solid-liquid separator 11 in which almost all solid matters in water to be treated are separated and are dropped to a lower part of a sludge storage tank 1 being a first chamber is provided at an upper part of the sludge storage tank 1 and the water to be treated flows in the solid-liquid separator 11 from an inflow pipe 6 for making the water to be treated flow in the septic tank. <P>COPYRIGHT: (C)2005,JPO&NCIPI

Description

本発明は、汚水を処理する浄化槽に関する。   The present invention relates to a septic tank for treating sewage.

従来の浄化槽には、例えば下記非特許文献1に挙げるものがある。この非特許文献1に示される浄化槽は、図8に示すように、嫌気ろ床槽第1室101、嫌気ろ床槽第2室102、生物ろ過槽103、処理水槽104、及び、消毒槽105を備えている。嫌気ろ床槽第1室101及び嫌気ろ床槽第2室102は、流入管106から流入した汚水(被処理水)の1次処理を行う1次処理槽S10であり、生物ろ過槽103及び処理水槽104は、1次処理された被処理水の2次処理を行う2次処理槽S20である。生物ろ過槽103は、上部が担体流動槽103a、下部が生物ろ過槽103bの2層構造となっている。そして、ブロワ110により、担体流動槽103aに常時空気が供給され、ブロワ111により、1日1回逆洗のために生物ろ過槽103bに空気が供給される。   Examples of conventional septic tanks include those listed in Non-Patent Document 1 below. As shown in FIG. 8, the septic tank shown in Non-Patent Document 1 includes an anaerobic filter bed first chamber 101, an anaerobic filter bed second chamber 102, a biological filtration tank 103, a treated water tank 104, and a disinfection tank 105. It has. The anaerobic filter bed first chamber 101 and the anaerobic filter bed second chamber 102 are a primary treatment tank S10 that performs a primary treatment of sewage (treated water) that flows in from the inflow pipe 106, and the biological filtration tank 103 and The treated water tank 104 is a secondary treatment tank S20 that performs a secondary treatment of the treated water subjected to the primary treatment. The biological filtration tank 103 has a two-layer structure in which the upper part is a carrier flow tank 103a and the lower part is a biological filtration tank 103b. The blower 110 constantly supplies air to the carrier flow tank 103a, and the blower 111 supplies air to the biological filtration tank 103b for backwashing once a day.

嫌気ろ床槽第1室101から嫌気ろ床槽第2室102へは、エアリフトポンプを利用した流量調整装置108によって、汚水の流入量の変動に関係なく、略一定量の被処理水が移送される。このように、浄化槽では、水質の安定化のため、ポンプによって流量調整を行うのが一般的である。また、嫌気ろ床槽第2室102から生物ろ過槽103へは、移流口112を介して被処理水が移送される。したがって、通常運転時、嫌気ろ床第2室102と生物ろ過槽103との水位は同水位となっている。   A substantially constant amount of treated water is transferred from the anaerobic filter tank first chamber 101 to the anaerobic filter bed second chamber 102 by a flow rate adjusting device 108 using an air lift pump regardless of fluctuations in the amount of inflow of sewage. Is done. As described above, in the septic tank, the flow rate is generally adjusted by the pump in order to stabilize the water quality. Further, the water to be treated is transferred from the second chamber 102 of the anaerobic filter tank to the biological filtration tank 103 through the advection port 112. Accordingly, during normal operation, the water levels in the second chamber 102 and the biological filtration tank 103 are the same.

2次処理された被処理水は、処理水槽104から消毒槽105に移送され消毒されて、放流管107から放流される。また、処理水槽104内の被処理水は、常時、その一部が循環水移送管109により嫌気ろ床槽第1室101に返送され、再度、嫌気ろ床槽第2室102、生物ろ過槽103を経て処理水槽104に流入する。このように、一般に、浄化槽では、被処理水の循環が常時行われており、この循環により、被処理水の脱窒が起こり、生物ろ過槽103への負担が軽減されて、水質が向上する。
財団法人日本環境整備教育センター編,「高度処理型(窒素除去型、小容量型、膜分離型)小型合併処理浄化槽維持管理講習会テキスト」,第1版,財団法人日本環境整備教育センター,平成13年2月,p.142−175
The treated water subjected to the secondary treatment is transferred from the treated water tank 104 to the sterilization tank 105, sterilized, and discharged from the discharge pipe 107. In addition, a part of the treated water in the treated water tank 104 is always returned to the first anaerobic filter bed tank 101 by the circulating water transfer pipe 109, and again, the anaerobic filter bed tank second chamber 102, the biological filter tank. It flows into the treated water tank 104 through 103. Thus, in general, in the septic tank, the water to be treated is constantly circulated. By this circulation, denitrification of the water to be treated occurs, the burden on the biological filtration tank 103 is reduced, and the water quality is improved. .
Japan Environmental Maintenance Education Center, “Advanced treatment type (nitrogen removal type, small capacity type, membrane separation type) small merged treatment septic tank maintenance management workshop text”, 1st edition, Japan Environmental Education Center, Heisei February 2013, p. 142-175

この発明は、放流管底の位置を浅くできるので、施工が容易となる浄化槽を提供することを目的とする。   An object of the present invention is to provide a septic tank that can be easily constructed because the bottom of the discharge pipe can be shallow.

本発明の浄化槽は、内部が複数の室に仕切られた浄化槽において、上流側から数えて1番目の室(以下、第1室という。)の上部に、被処理水中の固形物を略分離して前記第1室の下部に落下させる固液分離装置が設けられ、被処理水を浄化槽内に流入させる流入管から、前記固液分離装置に被処理水が流入するように構成されたことを特徴とする。   The septic tank of the present invention is a septic tank whose interior is partitioned into a plurality of chambers, and substantially separates solids in the water to be treated at the top of the first chamber (hereinafter referred to as the first chamber) counted from the upstream side. A solid-liquid separation device for dropping to the lower part of the first chamber and configured to allow the water to be treated to flow into the solid-liquid separation device from an inflow pipe through which the water to be treated flows into the septic tank. Features.

ここで、前記第1室が設けられて被処理水を1次処理する1次処理槽と、1次処理された被処理水を2次処理する2次処理槽と、前記1次処理槽から前記2次処理槽へ被処理水を揚水する揚水手段と、を有し、通常運転時に、前記揚水手段により、前記2次処理槽が前記1次処理槽よりも高水位とされることが好ましい。   Here, a primary treatment tank in which the first chamber is provided to primarily treat the treated water, a secondary treatment tank for secondary treatment of the treated water subjected to the primary treatment, and the primary treatment tank A pumping means for pumping water to be treated into the secondary treatment tank, and the secondary treatment tank is preferably set to a higher water level than the primary treatment tank by the pumping means during normal operation. .

このようにすれば、2次処理槽の水位を高くできるので、放流管底の位置が浅くなり、放流管を側溝等に接続するときの勾配が付け易くなり、施工が容易となる。   If it does in this way, since the water level of a secondary processing tank can be made high, the position of a discharge pipe bottom will become shallow, it will become easy to attach the gradient when connecting a discharge pipe to a side ditch, etc., and construction will become easy.

以下、本発明の一実施形態を図面に基づいて説明する。   Hereinafter, an embodiment of the present invention will be described with reference to the drawings.

図1及び図2に示すように、本実施形態の浄化槽は、上面に点検口となる3つの開口部H1、H2、H3を有するタンクTと、開口部H1、H2、H3を開閉する蓋L1、L2、L3とを備え、タンクTの内部には、仕切壁10、20、30で仕切られることにより、第1室である汚泥貯留槽1、第2室である予備ろ過槽2、第3室である担体流動槽3、及び、第4室である生物ろ過槽4が形成されている。汚泥貯留槽1及び予備ろ過槽2は被処理水の1次処理(本実施形態では嫌気処理)を行う1次処理槽S1であり、担体流動槽3及び生物ろ過槽4は被処理水の2次処理(本実施形態では好気処理)を行う2次処理槽S2である。また、タンクT内部の生物ろ過槽4の上部には、消毒槽5が配設されている。   As shown in FIGS. 1 and 2, the septic tank of this embodiment includes a tank T having three openings H1, H2, and H3 that serve as inspection ports on the upper surface, and a lid L1 that opens and closes the openings H1, H2, and H3. , L2 and L3, and the inside of the tank T is partitioned by the partition walls 10, 20, and 30, so that the sludge storage tank 1 as the first chamber, the preliminary filtration tank 2 as the second chamber, the third A carrier flow tank 3 as a chamber and a biological filtration tank 4 as a fourth chamber are formed. The sludge storage tank 1 and the preliminary filtration tank 2 are primary treatment tanks S1 that perform primary treatment (anaerobic treatment in this embodiment) of the water to be treated, and the carrier fluidization tank 3 and the biological filtration tank 4 are 2 of the water to be treated. The secondary processing tank S2 performs the next processing (aerobic processing in the present embodiment). In addition, a disinfection tank 5 is disposed above the biological filtration tank 4 inside the tank T.

汚泥貯留槽1は、上部に配置される固液分離部(固液分離装置とも言う。)11と、下部に配置される汚泥濃縮貯留部12とを備えている。固液分離装置11は、汚水中の夾雑物(固形物)と液体とを大まかに分離する装置である。固液分離装置11は、点検口である開口部H1の下方に配置されている。固液分離装置11には、汚水を流入させる流入管6の流出口61が中央前部15の上部に配置され、逆洗排水返送管8の流出口81が中央後部16の上部に配置される。   The sludge storage tank 1 includes a solid-liquid separation unit (also referred to as a solid-liquid separation device) 11 disposed in the upper part and a sludge concentration storage part 12 disposed in the lower part. The solid-liquid separation device 11 is a device that roughly separates impurities (solid matter) and liquid in sewage. The solid-liquid separator 11 is disposed below the opening H1 that is an inspection port. In the solid-liquid separator 11, the outlet 61 of the inflow pipe 6 through which sewage flows is arranged at the upper part of the central front part 15, and the outlet 81 of the backwash drainage return pipe 8 is arranged at the upper part of the central rear part 16. .

固液分離装置11は、図3に示すように、前壁部11a、後壁部11b、右壁部11c、及び、左壁部11dで囲まれて、上方及び下方が開放された略箱体状をなして、仕切壁10に固着されている。なお、本実施形態の浄化槽及び固液分離装置11における前後左右とは、それぞれ図1の矢印で示す方向とする。   As shown in FIG. 3, the solid-liquid separator 11 is a substantially box body surrounded by a front wall portion 11 a, a rear wall portion 11 b, a right wall portion 11 c, and a left wall portion 11 d and opened upward and downward. This is fixed to the partition wall 10. In addition, let the front and rear, right and left in the septic tank and the solid-liquid separator 11 of this embodiment be the directions shown by the arrows in FIG.

前壁部11aの上部には、流入管6が挿通される挿通孔11kが形成されている。後壁部11bの上端部には、逆洗排水返送管8を配置するための凹部11pが形成されている。後壁部11bの左側上部には移流口11rが設けられ、移流口11rは仕切壁10を貫通して、固液分離部11と予備ろ過槽2とを連通している。前壁部11aの下部は後方に折曲されて傾斜し、後壁部11bの下部は前方に折曲されて傾斜しており、それらの間には、固液分離部11と汚泥濃縮貯留部12とを連通する下方開口部11qが形成されている。なお、後壁部11bの下部は、前壁部11aの下部よりも下方まで延びている。   An insertion hole 11k through which the inflow pipe 6 is inserted is formed in the upper part of the front wall portion 11a. A concave portion 11p for arranging the backwash drainage return pipe 8 is formed at the upper end portion of the rear wall portion 11b. An advection port 11r is provided on the upper left side of the rear wall portion 11b, and the advection port 11r passes through the partition wall 10 to communicate the solid-liquid separation unit 11 and the preliminary filtration tank 2. The lower part of the front wall part 11a is bent backward and inclined, and the lower part of the rear wall part 11b is bent forward and inclined, and between them, the solid-liquid separation part 11 and the sludge concentration storage part A lower opening 11q that communicates with 12 is formed. In addition, the lower part of the rear wall part 11b is extended below rather than the lower part of the front wall part 11a.

固液分離装置11の内部には、中央前部15と中央後部16との間に仕切板11jが配設され、中央前部15には、挿通孔11kより下位に傾斜板11eが配設されている。中央前部15及び中央後部16と、右側部17との間には、略垂直方向に伸びる阻流板11fが配設され、阻流板11fの前部11uは、傾斜板11eの下端から下方に延びるように配設されている。なお、阻流板11fの下端の角部11s、11sが切欠かれているのは、下方における流通面積を大きくして、被処理水の流れを遅くするためである。また、中央前部15及び中央後部16と、左側部18との間には、流入した被処理水が固液分離装置11の下部を通らずに移流口11rから流出してしまうことを防止するため、略垂直方向に延びる阻流板11gが配設されている。   Inside the solid-liquid separator 11, a partition plate 11j is disposed between the center front portion 15 and the center rear portion 16, and the center front portion 15 is provided with an inclined plate 11e below the insertion hole 11k. ing. A baffle plate 11f extending in a substantially vertical direction is disposed between the central front portion 15 and the central rear portion 16 and the right side portion 17, and the front portion 11u of the baffle plate 11f extends downward from the lower end of the inclined plate 11e. It is arrange | positioned so that it may extend. The reason why the corners 11s and 11s at the lower end of the baffle plate 11f are notched is to increase the flow area in the lower part and slow down the flow of water to be treated. Moreover, between the central front part 15 and the central rear part 16, and the left side part 18, it prevents that the to-be-processed water which flowed in flows out from the advancing port 11r without passing the lower part of the solid-liquid separator 11. FIG. Therefore, a baffle plate 11g extending in a substantially vertical direction is provided.

予備ろ過槽2には、図2に示すように、ネット部材23、24で上下を挟まれた中央部に、嫌気性微生物が付着したろ材を充填することにより、ろ床26が形成されている。また、予備ろ過槽2の後部の中央部には、担体流動槽3との間を仕切る仕切壁20と、断面略コ字形状の仕切壁27とで区画されることにより、バッフル部21が形成されている。仕切壁27の下端は、予備ろ過槽2の底壁よりも上に配置され、バッフル部21は、ろ床26の下方に位置する予備ろ過層2の下部28と連通されている。   In the preliminary filtration tank 2, as shown in FIG. 2, a filter bed 26 is formed by filling the center part sandwiched between the net members 23 and 24 with a filter medium to which anaerobic microorganisms are attached. . In addition, a baffle portion 21 is formed in the central portion of the rear portion of the preliminary filtration tank 2 by being partitioned by a partition wall 20 that partitions the carrier flow tank 3 and a partition wall 27 having a substantially U-shaped cross section. Has been. The lower end of the partition wall 27 is disposed above the bottom wall of the preliminary filtration tank 2, and the baffle portion 21 communicates with the lower portion 28 of the preliminary filtration layer 2 located below the filter bed 26.

バッフル部21には、揚水手段である定量移送装置22が、固定用アングル29により所定位置に固定されている。定量移送装置22は周知のエアリフトポンプであり、予備ろ過槽2の水位が図2に示す低水位(L.W.L.)以上の場合に、略一定量の被処理水を間欠的に汲み上げて、担体流動槽3に移送する。定量移送装置22は、エア供給管P1を介して図示しないブロワに連結されている。定量移送装置22の揚水管22aは、仕切壁20を貫通して担体流動槽3まで延設され、揚水管22aの流出口は、担体流動槽3の通常運転時における水位(W.L.)より上となるように、担体流動槽3の上部に配置されている。   A fixed amount transfer device 22 that is a pumping means is fixed to the baffle portion 21 at a predetermined position by a fixing angle 29. The fixed-quantity transfer device 22 is a well-known air lift pump, and when the water level of the preliminary filtration tank 2 is lower than the low water level (LWL) shown in FIG. Transfer to 3. The fixed amount transfer device 22 is connected to a blower (not shown) via an air supply pipe P1. The pumping pipe 22a of the fixed-quantity transfer device 22 extends through the partition wall 20 to the carrier flow tank 3, and the outlet of the pumping pipe 22a is above the water level (WL) during normal operation of the carrier flow tank 3. It arrange | positions at the upper part of the support | carrier flow tank 3 so that it may become.

また、バッフル部21には、図1に示すように、仕切壁20に、ポンプの故障等の異常時にオーバーフローした被処理水を担体流動槽3に逃がすためのオーバーフロー口201が設けられている。オーバーフロー口201の下縁位置は、図7に示すように、予備ろ過槽2の通常運転時における高水位(H.W.L.)、及び、担体流動槽3の通常運転時における水位(W.L.)より上とされる。   Further, as shown in FIG. 1, the baffle portion 21 is provided with an overflow port 201 in the partition wall 20 for allowing the water to be treated that has overflowed when an abnormality such as a pump failure occurs to the carrier flow tank 3. As shown in FIG. 7, the lower edge position of the overflow port 201 includes a high water level (HWL) during normal operation of the preliminary filtration tank 2 and a water level (WW during normal operation of the carrier fluidized tank 3). .L.).

担体流動槽3には、好気性微生物が付着したプラスチック製の担体が充填されている。この担体は、後述するオリフィス92を閉塞させにくい形状(本実施形態では歯車状)とされている。また、担体流動槽3には、散気管32が底部付近まで延設されている。散気管32は、エア供給管P1を介して図示しないブロワに連結されている。仕切壁20には、循環装置である移送管9が、略水平方向に延びるように挿通され、この移送管9により、担体流動槽3と予備ろ過槽2とが連通され、すなわち、2次処理槽S2と1次処理槽S1とが連通されている。   The carrier fluid tank 3 is filled with a plastic carrier to which aerobic microorganisms adhere. The carrier has a shape (in the present embodiment, a gear shape) that makes it difficult to block an orifice 92 described later. Further, in the carrier flow tank 3, an air diffuser 32 is extended to the vicinity of the bottom. The air diffusion pipe 32 is connected to a blower (not shown) through an air supply pipe P1. A transfer pipe 9 as a circulation device is inserted into the partition wall 20 so as to extend in a substantially horizontal direction, and the carrier flow tank 3 and the prefiltration tank 2 are communicated with each other by the transfer pipe 9, that is, a secondary treatment. The tank S2 and the primary treatment tank S1 are in communication.

移送管9の流入側の部分である流入側部90には、図4に示すように、オリフィス92と回動部材94とが設けられている。移送管9は、断面略円形状であり、キャップ部材9a、キャップ部材9aに嵌合される短管部材9b、短管部材9bに連結される長管部材9c、短管部材9bと長管部材9cとを連結する連結部材9d、及び、キャップ部材9aに軸着される回動部材94を備え、キャップ部材9aに、小孔状のオリフィス92が穿設されている。   As shown in FIG. 4, an orifice 92 and a rotating member 94 are provided in the inflow side portion 90 that is a portion on the inflow side of the transfer pipe 9. The transfer pipe 9 has a substantially circular cross section, a cap member 9a, a short pipe member 9b fitted to the cap member 9a, a long pipe member 9c connected to the short pipe member 9b, a short pipe member 9b and a long pipe member The connecting member 9d is connected to the cap member 9c, and the rotating member 94 is pivotally attached to the cap member 9a. A small-hole orifice 92 is formed in the cap member 9a.

詳しくは、移送管9には、図4及び図5に示すように、流入側の端面91にオリフィス92が設けられ、端面91のオリフィス92以外の部位は閉塞されている。オリフィス92の開口面は、担体が通過できないような形状(本実施形態では、上縁が凹んだ略楕円形状)及び大きさとされている。移送管9の流出側の端面99は全面的に開口している。   Specifically, as shown in FIGS. 4 and 5, the transfer pipe 9 is provided with an orifice 92 at the end surface 91 on the inflow side, and a portion other than the orifice 92 on the end surface 91 is closed. The opening surface of the orifice 92 has a shape and a size such that the carrier cannot pass (in this embodiment, a substantially elliptical shape with a concave upper edge). The end face 99 on the outflow side of the transfer pipe 9 is fully open.

また、端面91には、端面91の中心93を中心として端面91上で回動する回動部材94が配設されている。回動部材94は流量調整手段に相当する。回動部材94は、図5(c)に示すように、オリフィス92の横幅よりも少し大きい幅を有して、オリフィス92を閉塞可能な細長い板状部材である。回動部材94の上端部(図5(c)の状態における上端部)は、移送管9の上面95に掛かるように略直角に曲げられて、ガイド部94aをなしている。そして、図4(a)に示すように、ガイド部94aには線状のマークM1が付けられ、上面95には、マークM1に合わせられるように、複数の目盛りM2が付けられている。なお、上面95には、清掃用の開口部96が設けられている。   Further, the end surface 91 is provided with a rotating member 94 that rotates on the end surface 91 about the center 93 of the end surface 91. The rotating member 94 corresponds to a flow rate adjusting means. As shown in FIG. 5C, the rotating member 94 is a long and narrow plate-like member having a width slightly larger than the lateral width of the orifice 92 and capable of closing the orifice 92. The upper end portion (the upper end portion in the state of FIG. 5C) of the rotating member 94 is bent at a substantially right angle so as to be hooked on the upper surface 95 of the transfer tube 9 to form a guide portion 94a. As shown in FIG. 4A, a linear mark M1 is attached to the guide portion 94a, and a plurality of scales M2 are attached to the upper surface 95 so as to be aligned with the mark M1. The upper surface 95 is provided with an opening 96 for cleaning.

そして、移送管9は、図2に示すように、オリフィス92が設けられた端面91が担体流動槽3内に配置され、端面99が予備ろ過槽2内の高水位(H.W.L.)よりも高い位置に配置される。端面91は、水平面に対して略90°の角度をなしているので、オリフィス92の開口面は、水平面に対して略90°の角度をなしている。   As shown in FIG. 2, the transfer pipe 9 has an end surface 91 provided with an orifice 92 disposed in the carrier flow tank 3, and an end surface 99 having a high water level (HWL. ). Since the end surface 91 forms an angle of approximately 90 ° with respect to the horizontal plane, the opening surface of the orifice 92 forms an angle of approximately 90 ° with respect to the horizontal plane.

仕切壁30には、上部の両側部に移流口33、33が開口している。移流口33、33の下縁位置は、オリフィス92の下縁位置よりも若干低い位置とされている。   In the partition wall 30, advection ports 33, 33 are opened on both upper side portions. The lower edge position of the convection ports 33 and 33 is a position slightly lower than the lower edge position of the orifice 92.

生物ろ過槽4には、ネット部材42、43で上下を挟まれた中央部に、好気性微生物が付着した担体を充填することにより、ろ床45が形成されている。また、生物ろ過槽4の前部の中央部には、担体流動槽3との間を仕切る仕切壁30と、断面略コ字形状の仕切壁46とで区画されることにより、処理水貯留部41が形成されている。仕切壁46の下端は、生物ろ過槽4の底壁よりも上に配置され、処理水貯留部41は、ろ床45の下方に位置する生物ろ過層4の下部47と連通されている。仕切壁46には、図1に示すように、異常時にオーバーフローした水を逃がすためのオーバーフロー口401が設けられている。   In the biological filtration tank 4, a filter bed 45 is formed by filling a center part sandwiched between the net members 42 and 43 with a carrier attached with aerobic microorganisms. In addition, the central portion of the front portion of the biological filtration tank 4 is partitioned by a partition wall 30 that partitions the carrier flow tank 3 and a partition wall 46 having a substantially U-shaped cross section, thereby providing a treated water storage section. 41 is formed. The lower end of the partition wall 46 is disposed above the bottom wall of the biological filtration tank 4, and the treated water storage unit 41 is communicated with the lower part 47 of the biological filtration layer 4 located below the filter bed 45. As shown in FIG. 1, the partition wall 46 is provided with an overflow port 401 for escaping water that has overflowed in the event of an abnormality.

処理水貯留部41には、逆洗排水返送用のエアリフトポンプ48が配設され、エアリフトポンプ48の下端部は、下部47に配置されている。また、生物ろ過槽4には、逆洗管49が、処理水貯留部41を通って底部付近まで延設されている。エアリフトポンプ48及び逆洗管49は、エア供給管P2を介して図示しないブロワに連結されている。また、エアリフトポンプ48には、逆洗排水返送管8が連結され、逆洗排水返送管8は、固液分離部11の中央後部16まで延設されている。   The treated water storage unit 41 is provided with an air lift pump 48 for returning the backwash waste water, and the lower end portion of the air lift pump 48 is arranged in the lower part 47. In the biological filtration tank 4, a backwash pipe 49 is extended to the vicinity of the bottom through the treated water storage part 41. The air lift pump 48 and the backwash pipe 49 are connected to a blower (not shown) via an air supply pipe P2. Further, the backwash drainage return pipe 8 is connected to the air lift pump 48, and the backwash drainage return pipe 8 extends to the central rear part 16 of the solid-liquid separation part 11.

処理水貯留部41の上部には、消毒槽5が配置されている。処理水貯留部41の後壁には移送管51が挿通され、略水平方向に延設されて、処理水貯留部41と消毒槽5とを連通している。移送管51は、両端面が全面的に開口されている。移送管51の流入口51aの下縁位置は、移流口33、33の下縁位置よりも高く、さらに、オリフィス92の上縁位置よりも高い位置とされている。また、オーバーフロー口401の下縁位置は、流入口51aの下縁位置より高い位置とされている。消毒槽5の上部には薬剤筒52が配設されている。消毒槽5の後壁には、浄化処理された処理水を放流する放流管7が挿通されている。放流管7の流入口71の下縁位置は、移送管51の流出口51bの下縁よりも低い位置とされる。放流管7は、タンクTの後壁を貫通して、浄化槽の外部に延設される。   A disinfection tank 5 is disposed above the treated water storage unit 41. A transfer pipe 51 is inserted through the rear wall of the treated water storage unit 41 and extends substantially in the horizontal direction, and the treated water storage unit 41 and the disinfection tank 5 communicate with each other. Both ends of the transfer pipe 51 are fully opened. The lower edge position of the inlet 51 a of the transfer pipe 51 is higher than the lower edge position of the inlets 33 and 33, and is higher than the upper edge position of the orifice 92. The lower edge position of the overflow port 401 is higher than the lower edge position of the inflow port 51a. A medicine cylinder 52 is disposed on the upper part of the sterilization tank 5. In the rear wall of the sterilization tank 5, a discharge pipe 7 for discharging the purified treated water is inserted. The lower edge position of the inlet 71 of the discharge pipe 7 is a position lower than the lower edge of the outlet 51 b of the transfer pipe 51. The discharge pipe 7 penetrates the rear wall of the tank T and extends outside the septic tank.

以上のように構成された浄化槽の作用について、次に説明する。図6は、浄化槽の処理の流れを示したものであり、図7は、被処理水の流れを矢印で示したものである。   Next, the operation of the septic tank configured as described above will be described. FIG. 6 shows the flow of treatment in the septic tank, and FIG. 7 shows the flow of water to be treated by arrows.

まず、被処理水は、流入管6から固液分離部11の中央前部15に流入する。そして、被処理水は傾斜板11eに沿って流下し、すなわち、被処理水は固液分離装置11の長手方向に流れて、右側部17に至って下方に潜り込む。このとき、被処理水は、傾斜板11eに沿って流下し流速が遅くなることから、汚泥貯留部12に貯留されている汚泥を巻き上げることが少ない。   First, the water to be treated flows from the inflow pipe 6 into the central front part 15 of the solid-liquid separation part 11. Then, the water to be treated flows down along the inclined plate 11e, that is, the water to be treated flows in the longitudinal direction of the solid-liquid separator 11 and reaches the right side portion 17 and sinks downward. At this time, since the water to be treated flows down along the inclined plate 11e and the flow speed becomes slow, the sludge stored in the sludge storage unit 12 is rarely rolled up.

被処理水中の比較的重い夾雑物は、下方開口部11qから汚泥濃縮貯留部12に落下する。このとき、夾雑物が、傾斜した前壁部11aの下部及び後壁部11bの下部に沿って下降することから、夾雑物の落下速度が遅くなり、汚泥の巻上げが抑制される。   Relatively heavy impurities in the water to be treated fall from the lower opening 11q to the sludge concentration storage part 12. At this time, since the contaminants descend along the inclined lower portion of the front wall portion 11a and the lower portion of the rear wall portion 11b, the falling speed of the contaminants is slowed and sludge winding is suppressed.

落下した夾雑物は、汚泥として汚泥濃縮貯留部12に貯留される。ここで、固液分離装置11の下方開口部11qが浄化槽の左右方向に長く開口し、また、後壁部11bの下部が、前壁部11aの下部よりも下方まで延びて、前方に傾斜していることから、汚泥が汚泥濃縮貯留部12に略均等に堆積することとなり、汚泥の偏りによる詰まりの発生の虞を低減できる。   The fallen foreign matter is stored in the sludge concentration storage part 12 as sludge. Here, the lower opening 11q of the solid-liquid separation device 11 opens longer in the left-right direction of the septic tank, and the lower portion of the rear wall portion 11b extends below the lower portion of the front wall portion 11a and tilts forward. Therefore, sludge is deposited almost uniformly in the sludge concentration storage section 12, and the possibility of clogging due to sludge bias can be reduced.

固液分離装置11によって比較的重い夾雑物が取り除かれた被処理水は、移流口11rから予備ろ過槽2に流入する。   The treated water from which relatively heavy impurities have been removed by the solid-liquid separator 11 flows into the preliminary filtration tank 2 from the advection port 11r.

予備ろ過槽2に流入した被処理水は、下降してろ床26を通過し、ろ床26中のろ材により残余の夾雑物が補足(物理ろ過)されるとともに、嫌気性微生物によって分解処理(嫌気処理)される。そして、下部28からバッフル部21に流入して、定量移送装置22により汲み上げられ、揚水管22aから担体流動槽3に流入する。   The treated water that has flowed into the preliminary filtration tank 2 descends and passes through the filter bed 26, and the remaining contaminants are supplemented (physical filtration) by the filter medium in the filter bed 26, and decomposed by anaerobic microorganisms (anaerobic). It is processed. And it flows in into the baffle part 21 from the lower part 28, is pumped up by the fixed quantity transfer apparatus 22, and flows in into the support | carrier flow tank 3 from the pumping pipe 22a.

担体流動槽3はばっ気処理が行なわれる槽であり、通常運転時には、常時、散気管32から空気が噴出されているため、担体が槽内を流動している。この担体に付着している好気性微生物により、被処理水中の有機物が分解処理(好気処理)される。そして、被処理水は、移流口33、33から生物ろ過槽4に流入する。また、被処理水の一部は、後述するようにオリフィス92を介して、予備ろ過槽2に返送される。   The carrier fluid tank 3 is a tank in which an aeration process is performed. During normal operation, air is constantly ejected from the air diffuser 32, so that the carrier flows in the tank. The organic matter in the water to be treated is decomposed (aerobic treatment) by the aerobic microorganisms adhering to the carrier. Then, the water to be treated flows into the biological filtration tank 4 from the advection ports 33 and 33. Moreover, a part of to-be-processed water is returned to the preliminary filtration tank 2 through the orifice 92 so that it may mention later.

生物ろ過槽4に流入した被処理水は、下降してろ床45を通過し、ろ床45中の担体により浮遊物が捕捉(物理ろ過)されて、図7の色の薄い矢印で示すように、処理水貯留部41に入り、移送管51の流出口51bから消毒槽5に流入する。なお、この明細書では、処理水貯留部41に流入した段階以降の被処理水を、処理水というものとする。   The treated water that has flowed into the biological filtration tank 4 descends and passes through the filter bed 45, and suspended matter is captured (physical filtration) by the carrier in the filter bed 45, as shown by the light arrow in FIG. 7. Then, it enters the treated water storage section 41 and flows into the disinfection tank 5 from the outlet 51 b of the transfer pipe 51. In addition, in this specification, the to-be-processed water after the step which flowed into the treated water storage part 41 shall be called treated water.

生物ろ過槽4では、1日に1〜2回、逆洗管49から空気を噴出させることにより、担体に捕捉された浮遊物を剥離し、エアリフトポンプ48で槽内の水を引き抜くことにより、処理水貯留部41内の処理水を逆流させて、ろ床45の洗浄(逆洗)を行う。なお、引き抜かれた逆洗排水は、多量の浮遊物を含むため、逆洗排水返送管8により固液分離装置11の中央後部16に返送されて再処理される。   In the biological filtration tank 4, air is ejected from the backwash tube 49 once or twice a day to peel off the suspended matter captured by the carrier, and the water in the tank is pulled out by the air lift pump 48. The treated water in the treated water storage unit 41 is caused to flow backward, and the filter bed 45 is washed (backwashed). In addition, since the withdrawn backwash drainage contains a large amount of suspended solids, it is returned to the central rear portion 16 of the solid-liquid separator 11 by the backwash drainage return pipe 8 and reprocessed.

消毒槽5では、薬剤による処理水の消毒を行う。消毒後の処理水は放流管7から放流される。   In the sterilization tank 5, the treated water is sterilized with chemicals. The treated water after disinfection is discharged from the discharge pipe 7.

次に、各槽の水位について説明する。汚泥貯留槽1の水位は、移流口11rの下縁位置で決まり、図7に示す汚泥貯留槽1中のW.L.の位置となる。なお、移流口11rの下縁位置は、予備ろ過槽2における高水位(H.W.L.)よりも高く設定され、処理水貯留部41に配設される移送管51の流入口51aの下縁位置よりは低く設定される。   Next, the water level of each tank will be described. The water level of the sludge storage tank 1 is determined by the lower edge position of the advection port 11r and becomes the position of W.L. in the sludge storage tank 1 shown in FIG. The lower edge position of the transfer port 11r is set higher than the high water level (HWL) in the preliminary filtration tank 2, and is lower than the lower edge position of the inlet 51a of the transfer pipe 51 provided in the treated water storage unit 41. Set low.

予備ろ過槽2の水位は、流入汚水の時間変動に伴って変動するが、設計上、図7に示す高水位(H.W.L.)から低水位(L.W.L.)の範囲で変動するものとされている。この範囲は、所定の基準にしたがって定められるものであり、通常運転時においては、予備ろ過槽2の水位はこの範囲で変動する。なお、通常運転時とは、通常の使用状態で通常の運転がなされているときを言い、故障等の異常時や、予定人数を超えて使用する等の異常な使われ方をしたときは除くものとする。   The water level of the preliminary filtration tank 2 varies with time variation of the influent sewage, but is designed to vary in the range from the high water level (H.W.L.) to the low water level (L.W.L.) shown in FIG. This range is determined according to a predetermined standard, and the water level of the preliminary filtration tank 2 varies within this range during normal operation. Normal operation means when normal operation is performed under normal operating conditions, except when there is an abnormality such as a malfunction or when the user has used the product more than planned. Shall.

処理水貯留部41を含む生物ろ過槽4の水位は、移送管51の流入口51aの下縁位置で決まり、また、移流口33、33の下縁位置が流入口51aの下縁位置よりも低いことから、担体流動槽3の水位は、生物ろ過槽4の水位と同レベルとなって、図7に示す担体流動槽3中のW.L.で示す位置となる。   The water level of the biological filtration tank 4 including the treated water storage section 41 is determined by the lower edge position of the inlet 51a of the transfer pipe 51, and the lower edge positions of the inlets 33 and 33 are higher than the lower edge position of the inlet 51a. Since it is low, the water level of the carrier fluidized tank 3 becomes the same level as the water level of the biological filtration tank 4 and becomes the position indicated by WL in the carrier fluidized tank 3 shown in FIG.

そして、移送管9の端面99が、予備ろ過槽2における高水位(H.W.L.)よりも高く、移送管51の流入口51aの下縁位置が、移送管9のオリフィス92の上縁位置、及び、汚泥貯留槽1の移流口11rの下縁位置よりも高いことから、担体流動槽3の水位は、予備ろ過槽2における高水位(H.W.L.)よりも高くなり、さらに、汚泥貯留槽1の水位よりも高くなる。すなわち、通常運転時において、2次処理槽S2は1次処理槽S1よりも高水位となる。   And the end surface 99 of the transfer pipe 9 is higher than the high water level (HWL) in the preliminary filtration tank 2, the lower edge position of the inlet 51a of the transfer pipe 51 is the upper edge position of the orifice 92 of the transfer pipe 9, and Since it is higher than the lower edge position of the advection port 11r of the sludge storage tank 1, the water level of the carrier flow tank 3 is higher than the high water level (HWL) in the preliminary filtration tank 2, and moreover than the water level of the sludge storage tank 1. Also gets higher. That is, during normal operation, the secondary treatment tank S2 has a higher water level than the primary treatment tank S1.

消毒槽5の水位は、移送管51の流出口51bの下縁位置よりも約50mm以上低い位置とされ、放流管7の流入口71の下縁位置で決まる。   The water level of the disinfection tank 5 is a position that is lower by about 50 mm or more than the lower edge position of the outlet 51 b of the transfer pipe 51, and is determined by the lower edge position of the inlet 71 of the outlet pipe 7.

オリフィス92は、流入口51aの下縁位置よりも低い位置に配置されていることから、図7のW.L.よりも低い位置、すなわち、水面下に配置される。一方、移送管9の端面99は、予備ろ過槽2における高水位(H.W.L.)よりも高い位置に配置されることから、オリフィス92を介して担体流動槽3内の被処理水の一部が予備ろ過槽2に返送されることとなり、水位差の利用により無動力で、被処理水の常時循環が行われることとなる。   Since the orifice 92 is disposed at a position lower than the lower edge position of the inflow port 51a, the orifice 92 is disposed at a position lower than W.L. in FIG. On the other hand, the end surface 99 of the transfer pipe 9 is disposed at a position higher than the high water level (HWL) in the preliminary filtration tank 2, so that the water to be treated in the carrier flow tank 3 through the orifice 92. A part of the water is returned to the preliminary filtration tank 2, and the water to be treated is constantly circulated without power by utilizing the water level difference.

オリフィス92から返送される被処理水の流量は、オリフィス92の開口面積とオリフィス92から担体流動槽3の水面までの高さによって決まる。そして、通常運転時においては、担体流動槽3の水位は略一定であることから、オリフィス92から返送される被処理水の流量は略一定となり、循環される被処理水の流量が略一定となって、処理が安定し、水質が安定する。   The flow rate of the water to be treated returned from the orifice 92 is determined by the opening area of the orifice 92 and the height from the orifice 92 to the water surface of the carrier flow tank 3. During normal operation, since the water level in the carrier fluidized tank 3 is substantially constant, the flow rate of the treated water returned from the orifice 92 is substantially constant, and the flow rate of the circulated treated water is substantially constant. The treatment becomes stable and the water quality becomes stable.

また、オリフィス92は、ばっ気処理が行われる担体流動槽3に配設されているため、槽内を流動する担体によってオリフィス92が常時洗浄されるので、堆積物による閉塞が起こりにくい。このため、循環される被処理水の流量が略一定に保たれる。   In addition, since the orifice 92 is disposed in the carrier flow tank 3 in which the aeration process is performed, the orifice 92 is always washed by the carrier flowing in the tank, so that clogging with deposits hardly occurs. For this reason, the flow rate of the treated water to be circulated is kept substantially constant.

さらに、一般に浄化槽では容量(人槽)によって循環水の流量を変える必要があるが、図5に示すように、回動部材94を回動させて、オリフィス92の開口面積を変えることにより、循環される被処理水の流量を容易に変えることができる。図5において、(a)は5人槽、(b)は10人槽、(c)は循環停止の場合を示している。   Further, in general, in the septic tank, it is necessary to change the flow rate of the circulating water depending on the capacity (human tank), but as shown in FIG. 5, the circulating member 94 is rotated to change the opening area of the orifice 92. The flow rate of the water to be treated can be easily changed. In FIG. 5, (a) shows a 5-person tank, (b) shows a 10-person tank, and (c) shows a case where circulation is stopped.

そして、浄化槽では上面の開口部H1、H2、H3から確認、操作、清掃等が行われるが、図4に示すように、回動部材94には上面95に掛かるガイド部94aが延設されているため、上方からガイド部94aを持って回動部材94を回動できるとともに、上方からガイド部94aの位置を視認することにより回動の程度が確認でき、調整が容易である。特に、マークM1と目盛りM2とを設けて、これらを合わせることとすれば、調整が一層容易である。なお、目盛りM2には、人槽や容量を表す数字等を付記しておくとよい。また、マークM1と目盛りM2は線以外の印でもよく、目盛りM2は、人槽、容量、流量、回転角度、または、開口面積の少なくとも1つを示す何らかの印であればよく、マークM1は、目盛りM2に合わせるための印であればよい。また、マークM1を突起としてもよい。   In the septic tank, confirmation, operation, cleaning, and the like are performed from the openings H1, H2, and H3 on the upper surface. As shown in FIG. 4, the rotating member 94 is provided with a guide portion 94a extending on the upper surface 95. Therefore, the rotation member 94 can be rotated by holding the guide portion 94a from above, and the degree of rotation can be confirmed by visually recognizing the position of the guide portion 94a from above, and adjustment is easy. In particular, if a mark M1 and a scale M2 are provided and these are combined, adjustment is easier. It should be noted that the scale M2 may be accompanied by a number indicating a human tank or capacity. The mark M1 and the scale M2 may be marks other than a line, and the scale M2 may be any mark indicating at least one of a human tank, a capacity, a flow rate, a rotation angle, or an opening area. What is necessary is just the mark for adjusting to the scale M2. The mark M1 may be a protrusion.

以上のように、本実施形態の浄化槽は、通常運転時に、1次処理槽S1の水位より2次処理槽S2の水位を高くして、水位差を利用して移送管9により2次処理槽S2から1次処理槽S1に被処理水を返送することとしたので、返送用のポンプを常時作動させる必要が無くなり、動力を低減できる。また、定量移送装置22を使用することにより、時間当たり略一定量の被処理水が2次処理槽S2に移送されるので、処理が安定して行われ、水質が安定する。そして、上述したように、オリフィス92によって循環水の流量が略一定に保たれることからも、水質の安定化が図られる。   As described above, the septic tank according to the present embodiment is configured so that the water level of the secondary treatment tank S2 is higher than the water level of the primary treatment tank S1 during normal operation, and the secondary treatment tank is transferred by the transfer pipe 9 using the water level difference. Since the water to be treated is returned from S2 to the primary treatment tank S1, it is not necessary to always operate the return pump, and the power can be reduced. In addition, by using the quantitative transfer device 22, a substantially constant amount of water to be treated per hour is transferred to the secondary treatment tank S2, so that the treatment is performed stably and the water quality is stabilized. As described above, since the flow rate of the circulating water is kept substantially constant by the orifice 92, the water quality can be stabilized.

また、2次処理槽S2の水位を高くすることにより、2次処理槽の容量を略最大限に利用でき、浄化槽の小型化が可能になる。そして、消毒槽5の水位は2次処理槽S2の水位より低くする必要があるが、2次処理槽S2の水位を高くすれば、消毒槽5の水位も高くできるため、消毒槽5に連結される放流管7の位置を高くできる(すなわち、放流管7の管底を浅くできる)。このため、放流管7を側溝等に接続するときの勾配が付け易くなり、放流管7の位置を上げるためのポンプが不要となる。   Moreover, by raising the water level of the secondary treatment tank S2, the capacity of the secondary treatment tank can be utilized to a maximum extent, and the septic tank can be downsized. And it is necessary to make the water level of the disinfection tank 5 lower than the water level of the secondary treatment tank S2, but if the water level of the secondary treatment tank S2 is increased, the water level of the disinfection tank 5 can also be raised, so it is connected to the disinfection tank 5. The position of the discharge pipe 7 can be increased (that is, the bottom of the discharge pipe 7 can be made shallow). For this reason, it becomes easy to give a gradient when connecting the discharge pipe 7 to a side groove or the like, and a pump for raising the position of the discharge pipe 7 is not necessary.

また、固液分離装置11は、固液分離装置11の長手方向に沿った前壁部11aに流入管6の挿通孔11kを設けることにより、固液分離装置11の長手方向と流入管6の軸方向とが略直交するように、流入管6を配置できる。ここで、流入管6の軸方向は、浄化槽の長手方向(前後方向)に略一致する。すなわち、固液分離装置11は、固液分離装置11の長手方向が浄化槽の短手方向(左右方向)に略一致し、固液分離装置11の短手方向が浄化槽の長手方向に略一致するように配置可能に構成されているので、槽内のスペースを有効利用でき、容量が小さく前後方向の長さが短い浄化槽にも設置可能である。また、固液分離装置11の長手方向を浄化槽の長手方向に一致させた場合のように、平面視においてタンクTの開口部H1の略全面を固液分離装置11が占めてしまうことがなくなり、開口部H1に対して若干オフセットして配置可能であり、図1の符号Sに示すように、汚泥濃縮貯留部12の清掃用のスペースが確保できるので、汚泥濃縮貯留部12の清掃が容易である。そして、固液分離装置11の清掃等の管理も、開口部H1から可能であるので、全体として浄化槽の維持管理が容易となる。   Further, the solid-liquid separation device 11 is provided with the insertion hole 11k of the inflow pipe 6 in the front wall portion 11a along the longitudinal direction of the solid-liquid separation apparatus 11, so that the longitudinal direction of the solid-liquid separation apparatus 11 and the inflow pipe 6 are The inflow pipe 6 can be arranged so that the axial direction is substantially orthogonal. Here, the axial direction of the inflow pipe 6 substantially coincides with the longitudinal direction (front-rear direction) of the septic tank. That is, in the solid-liquid separation device 11, the longitudinal direction of the solid-liquid separation device 11 substantially coincides with the short direction (left-right direction) of the septic tank, and the short direction of the solid-liquid separation device 11 substantially coincides with the longitudinal direction of the septic tank. Thus, the space in the tank can be used effectively, and it can be installed in a septic tank with a small capacity and a short length in the front-rear direction. Further, as in the case where the longitudinal direction of the solid-liquid separator 11 is made coincident with the longitudinal direction of the septic tank, the solid-liquid separator 11 does not occupy substantially the entire surface of the opening H1 of the tank T in a plan view, It can be arranged with a slight offset with respect to the opening H1, and as shown by the symbol S in FIG. 1, since the space for cleaning the sludge concentration storage section 12 can be secured, the sludge concentration storage section 12 can be easily cleaned. is there. And since management, such as cleaning of the solid-liquid separation apparatus 11, is also possible from the opening part H1, the maintenance management of a septic tank becomes easy as a whole.

また、固液分離装置11を設けることにより、従来、夾雑物除去のために1次処理槽の前側の槽内に配置していたろ材が不要となるため、夾雑物の堆積量が多い場合の流入水流によるろ材の流出が発生しない。   In addition, by providing the solid-liquid separation device 11, a filter medium that has conventionally been arranged in the tank on the front side of the primary treatment tank for removing contaminants becomes unnecessary. No outflow of filter media due to inflowing water flow.

なお、本実施形態では、オリフィス92の開口面を水平面に対して略90°の角度としたが、この角度は、オリフィス92の開口面が斜め下を向くように、水平面に対して45〜90°の範囲で変えてもよい。オリフィス92の開口面が斜め下を向くことにより、オリフィス92が担体によって洗われ易くなり、一層閉塞しにくくなるからである。なお、オリフィス92の開口面の角度を変えるには、キャップ部材9aの端面91の角度を変えるとよい。また、オリフィス92の形状は、円形、楕円形、長方形、あるいは、それらの形状の組み合わせ等、種々の形状を採り得る。また、回動部材94は、回動角度によってオリフィス92の開口面の少なくとも一部を開閉可能であればよい。   In the present embodiment, the opening surface of the orifice 92 is set at an angle of approximately 90 ° with respect to the horizontal plane. However, this angle is 45 to 90 with respect to the horizontal plane so that the opening surface of the orifice 92 faces obliquely downward. It may be changed in the range of °. This is because when the opening surface of the orifice 92 faces obliquely downward, the orifice 92 is easily washed by the carrier and is more difficult to close. In order to change the angle of the opening surface of the orifice 92, the angle of the end surface 91 of the cap member 9a may be changed. Moreover, the shape of the orifice 92 may take various shapes such as a circle, an ellipse, a rectangle, or a combination of these shapes. Moreover, the rotation member 94 should just be able to open and close at least one part of the opening surface of the orifice 92 with a rotation angle.

また、移送管9を水平に配設せずに、1次処理槽S1に向かって下降するように傾斜させて配設してもよい。また、移送管9を長くして、1次処理槽S1の前部の槽である汚泥貯留槽1に循環水を返送するようにしてもよい。また、逆洗排水の返送先を、固液分離装置11の中央前部15としてもよい。   Further, the transfer pipe 9 may be disposed so as to be lowered toward the primary processing tank S1 without being disposed horizontally. Moreover, you may make it lengthen the transfer pipe | tube 9 and return circulating water to the sludge storage tank 1 which is the tank of the front part of primary treatment tank S1. Further, the return destination of the backwash waste water may be the central front portion 15 of the solid-liquid separator 11.

また、移送管9を設けずに、循環装置としてオリフィス92を直接仕切壁9に穿設してもよいが、移送管9にオリフィス92を穿設し、かかる移送管9をタンクTの開口部H2の直下に配設することにより、調整操作や清掃が行い易くなり、また、ポンプ22やバッフル部21を避けて、ろ床26の真上に循環水を返送することができる。   Alternatively, the orifice 92 may be directly drilled in the partition wall 9 as a circulation device without providing the transfer pipe 9, but the orifice 92 is drilled in the transfer pipe 9, and the transfer pipe 9 is connected to the opening of the tank T. By disposing it directly under H2, adjustment operations and cleaning can be easily performed, and the circulating water can be returned directly above the filter bed 26 while avoiding the pump 22 and the baffle portion 21.

さらに、本実施形態の浄化槽では、1次処理槽S1を汚泥貯留槽1と予備ろ過槽2とから構成し、2次処理槽S2を担体流動槽3と生物ろ過槽4とから構成したが、1次処理槽S1及び2次処理槽S2の構成はこれに限られず、1次処理槽S1を嫌気ろ床槽第1室と嫌気ろ床槽第2室とから構成し、2次処理槽S2を、担体流動・生物ろ過槽と、処理水を貯留する処理水槽とから構成することもできる。担体流動・生物ろ過槽とは、上部が担体流動槽3、下部が生物ろ過槽4の2層構造とされた槽である。また、2次処理槽S2を、生物膜ろ過槽と、本実施形態の処理水貯留部41に相当する処理水槽とから構成することもできる。また、オリフィス92を、2次処理槽S2の後部の槽である処理水槽や、生物ろ過槽4の処理水貯留部41に設けることとしてもよい。   Furthermore, in the septic tank of the present embodiment, the primary treatment tank S1 is composed of the sludge storage tank 1 and the preliminary filtration tank 2, and the secondary treatment tank S2 is composed of the carrier fluidization tank 3 and the biological filtration tank 4, The configuration of the primary treatment tank S1 and the secondary treatment tank S2 is not limited to this, and the primary treatment tank S1 is composed of an anaerobic filter bed first chamber and an anaerobic filter bed second chamber. Can also be composed of a carrier flow / biological filtration tank and a treated water tank for storing treated water. The carrier flow / biological filtration tank is a tank having a two-layer structure in which the upper part is a carrier flow tank 3 and the lower part is a biological filtration tank 4. Moreover, secondary treatment tank S2 can also be comprised from the biofilm filtration tank and the treated water tank equivalent to the treated water storage part 41 of this embodiment. The orifice 92 may be provided in the treated water tank that is the rear tank of the secondary treatment tank S2 or the treated water storage part 41 of the biological filtration tank 4.

また、固液分離装置11の右側部17の右端部に、右壁部11cに接しつつ前壁部11aと後壁部11bとを連結するように略水平方向に延びる阻流板を配設することとしてもよい。かかる阻流板により、汚泥の巻き上げが抑制されるとともに、略水平方向に水流が変えられる。さらに、固液分離装置11の左側部18の移流口11rの下に、後壁部11bに接しつつ左壁部11dと阻流板11gとを連結するように略水平方向に延びる阻流板を配設するようにしてもよい。かかる阻流板により、真下からの流れが妨げられて、略水平方向の水流が形成される。このように、阻流板により水流方向を変えれば、被処理水の流路を長くできるので、分離性能を高めることができる。   Further, a baffle plate extending in a substantially horizontal direction is disposed at the right end portion of the right side portion 17 of the solid-liquid separator 11 so as to connect the front wall portion 11a and the rear wall portion 11b while being in contact with the right wall portion 11c. It is good as well. Such a baffle plate suppresses sludge winding and changes the water flow in a substantially horizontal direction. Further, a baffle plate that extends in a substantially horizontal direction so as to connect the left wall portion 11d and the baffle plate 11g while being in contact with the rear wall portion 11b under the advancing port 11r of the left side portion 18 of the solid-liquid separator 11. It may be arranged. By such a baffle plate, the flow from right below is prevented, and a substantially horizontal water flow is formed. Thus, if the water flow direction is changed by the baffle plate, the flow path of the water to be treated can be lengthened, so that the separation performance can be improved.

さらに、固液分離装置11の長手方向と浄化槽の長手方向とがなす角度は、スペースの有効利用の観点からは、本実施形態のように平面視において約90°が望ましいが、平面視において約45°以上約90°以下の角度(すなわち、固液分離装置11の長手方向が浄化槽の長手方向と一致した状態から、固液分離装置11を水平方向に約45°以上約90°以下回転させた状態)であれば、汚泥濃縮貯留部12の清掃用スペースが確保できて浄化槽の維持管理が容易となる。   Furthermore, the angle formed by the longitudinal direction of the solid-liquid separation device 11 and the longitudinal direction of the septic tank is preferably about 90 ° in plan view as in the present embodiment from the viewpoint of effective use of space, but about 90 ° in plan view. An angle of 45 ° or more and about 90 ° or less (that is, from the state where the longitudinal direction of the solid-liquid separation device 11 coincides with the longitudinal direction of the septic tank, the solid-liquid separation device 11 is rotated about 45 ° or more and about 90 ° or less in the horizontal direction. If it is the state), the cleaning space of the sludge concentration storage part 12 can be secured, and the maintenance management of the septic tank becomes easy.

すなわち、特許請求の範囲を逸脱しない範囲で、本発明は種々の構成を採り得る。   That is, the present invention can adopt various configurations without departing from the scope of the claims.

本発明の浄化槽の一実施形態の概略横断面図である。It is a schematic cross-sectional view of one embodiment of the septic tank of the present invention. 図1の浄化槽の概略縦断面図である。It is a schematic longitudinal cross-sectional view of the septic tank of FIG. 前壁部と右壁部とを2点鎖線表示した固液分離装置の概略斜視図である。It is a schematic perspective view of the solid-liquid separator which displayed the front wall part and the right wall part with the dashed-two dotted line. (a)は移送管の平面図、(b)は移送管の断面図である。(A) is a top view of a transfer pipe, (b) is sectional drawing of a transfer pipe. 移送管の背面図であり、(a)は5人槽、(b)は10人槽、(c)はオリフィスを閉塞させた状態である。It is a rear view of a transfer pipe, (a) is a 5-person tank, (b) is a 10-person tank, and (c) is a state where an orifice was closed. 図1の浄化槽の処理の流れを示す図である。It is a figure which shows the flow of a process of the septic tank of FIG. 図1の浄化槽の被処理水の流れを示す図である。It is a figure which shows the flow of the to-be-processed water of the septic tank of FIG. 従来の浄化槽の概略縦断面図である。It is a schematic longitudinal cross-sectional view of the conventional septic tank.

符号の説明Explanation of symbols

1 汚泥貯留槽(第1室)
6 流入管
9 移送管(循環装置)
11 固液分離装置
22 定量移送装置(揚水手段)
90 流入側部
91 端面
92 オリフィス
93 中心
94 回動部材(流量調整手段)
94a ガイド部
S1 1次処理槽
S2 2次処理槽
1 Sludge storage tank (first room)
6 Inflow pipe 9 Transfer pipe (circulation device)
11 Solid-liquid separator 22 Fixed-quantity transfer device (pumping means)
90 Inflow side 91 End face 92 Orifice 93 Center 94 Rotating member (flow rate adjusting means)
94a Guide part S1 Primary treatment tank S2 Secondary treatment tank

Claims (2)

内部が複数の室に仕切られた浄化槽において、
上流側から数えて1番目の室(以下、第1室という。)の上部に、被処理水中の固形物を略分離して前記第1室の下部に落下させる固液分離装置が設けられ、
被処理水を浄化槽内に流入させる流入管から、前記固液分離装置に被処理水が流入するように構成された
ことを特徴とする浄化槽。
In the septic tank whose interior is partitioned into multiple chambers,
A solid-liquid separation device is provided at the top of the first chamber (hereinafter referred to as the first chamber) counted from the upstream side to substantially separate the solid matter in the water to be treated and drop it to the lower portion of the first chamber.
A septic tank characterized in that the sewage water flows into the solid-liquid separator from an inflow pipe through which the sewage water flows into the septic tank.
前記第1室が設けられて被処理水を1次処理する1次処理槽と、
1次処理された被処理水を2次処理する2次処理槽と、
前記1次処理槽から前記2次処理槽へ被処理水を揚水する揚水手段と、
を有し、
通常運転時に、前記揚水手段により、前記2次処理槽が前記1次処理槽よりも高水位とされる
ことを特徴とする請求項1記載の浄化槽。
A primary treatment tank in which the first chamber is provided to primarily treat the treated water;
A secondary treatment tank for secondary treatment of the treated water subjected to the primary treatment;
Pumping means for pumping water to be treated from the primary treatment tank to the secondary treatment tank;
Have
The septic tank according to claim 1, wherein, during normal operation, the secondary treatment tank is set to a higher water level than the primary treatment tank by the pumping means.
JP2005102645A 2005-03-31 2005-03-31 Septic tank Expired - Lifetime JP4435711B2 (en)

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Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2008012466A (en) * 2006-07-07 2008-01-24 Hitachi Housetec Co Ltd Water treatment apparatus
JP2008012465A (en) * 2006-07-07 2008-01-24 Hitachi Housetec Co Ltd Water treatment apparatus
JP2013123663A (en) * 2011-12-13 2013-06-24 Daiei Sangyo Kk Wastewater treatment apparatus and wastewater treatment method

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2008012466A (en) * 2006-07-07 2008-01-24 Hitachi Housetec Co Ltd Water treatment apparatus
JP2008012465A (en) * 2006-07-07 2008-01-24 Hitachi Housetec Co Ltd Water treatment apparatus
JP4702748B2 (en) * 2006-07-07 2011-06-15 株式会社ハウステック Water treatment equipment
JP4702749B2 (en) * 2006-07-07 2011-06-15 株式会社ハウステック Water treatment equipment
JP2013123663A (en) * 2011-12-13 2013-06-24 Daiei Sangyo Kk Wastewater treatment apparatus and wastewater treatment method

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