JP2004223417A - Sewage treatment apparatus - Google Patents

Sewage treatment apparatus Download PDF

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Publication number
JP2004223417A
JP2004223417A JP2003014754A JP2003014754A JP2004223417A JP 2004223417 A JP2004223417 A JP 2004223417A JP 2003014754 A JP2003014754 A JP 2003014754A JP 2003014754 A JP2003014754 A JP 2003014754A JP 2004223417 A JP2004223417 A JP 2004223417A
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Japan
Prior art keywords
carrier
water
treated
filtration layer
treatment tank
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JP2003014754A
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Japanese (ja)
Inventor
Yoshito Kitai
良人 北井
Masaaki Kimura
正昭 木村
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Kubota Corp
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Kubota Corp
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Priority to JP2003014754A priority Critical patent/JP2004223417A/en
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    • 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

Abstract

<P>PROBLEM TO BE SOLVED: To provide a sewage treatment apparatus constituted so as to easily keep the filtering function of a carrier filter bed in a carrier treatment tank by backward washing while enhancing the function. <P>SOLUTION: This sewage treatment apparatus is equipped with the carrier treatment tank E2 which is provided with the carrier filter beds E21 and E22 respectively formed by laminating a large number of carriers C1 and C2. A large number of the first carriers C1 comprising a material whose specific gravity is lower than that of water are floated and laminated in the carrier treatment tank E2 (E) to form the carrier filter bed E21 and a large number of the second carriers C2 comprising a material whose specific gravity is higher than that of water are deposited and laminated in the carrier treatment tank E (E2) to form the second carrier filter bed E22. <P>COPYRIGHT: (C)2004,JPO&NCIPI

Description

【0001】
【発明の属する技術分野】
本発明は、多数の担体を積層した担体濾過層を設け、被処理水を濾過処理可能に構成してある担体処理槽を備えた汚水処理装置に関する。
【0002】
【従来の技術】
従来、この種の汚水処理装置としては、前記担体として水よりやや比重の小さな第一の担体を水処理槽内に浮上積層させ、担体濾過層を形成してあるものが知られている。
一方、前記担体として水よりやや比重の大きな第二の担体を水処理槽内に沈降堆積積層させ、担体濾過層を形成してあるものも知られている。
このような担体濾過層は、移流する被処理水を生物濾過し、前記担体に付着した微生物膜により、被処理水を清浄にする機能を有する。また、被処理水注に含まれる固形成分を除去することができ、活性汚泥処理等の微生物処理に供した後の被処理水を清浄にする役目を担う。この担体濾過層で不要になった微生物膜や濾過された固形成分(以下これらを単に固形成分と称する)は、前記担体を逆洗することによって、前記担体から剥離除去され、再度微生物処理されたり、余剰汚泥として引き抜き可能に貯留されたりする。この際担体を逆洗するには、通常前記担体濾過層中に設けられた散気管等からの気泡供給による。
尚、水より比重の小さな担体をあわせて担体処理槽に用いられている場合があるが(特許文献1参照)、散気等により槽内を流動させるべく用いられるのみであって、このような担体を、ともに濾過層に形成することは考えられていない。
【0003】
【特許文献1】
特開平11−147095号公報
【0004】
【発明が解決しようとする課題】
しかし、このような汚水処理装置に設けられる担体濾過層は、担体が上方に浮上あるいは下方に沈降することにより層状に堆積し、担体濾過層を形成する。前記担体濾過層が形成されると、前記被処理水中に含まれる固形成分は、前記担体濾過層において担体に捕捉されて濾過される。しかし、濾過された固形成分は前記担体同士の間に捕捉されたままの状態で保持されるため、前記担体同士の間にわたって接触した状態のまま固化しやすい。そのため、前記担体同士を一体に固化させてしまい大きな塊となりやすい。すると、前記担体は、個々には、動きにくくなるので、全体としてほぐれず、その担体同士の間に保持された固形成分は、前記担体から剥離しにくくなる。そのため、上述の逆洗の効果が現れにくくなり、前記担体濾過層が全体として目詰まりを起こしやすくなる。
目詰まりがおきる傾向にあると、前記担体濾過層を介しての被処理水の流れは悪くなる。すると、前記担体処理槽内での被処理水の流れや汚泥の濾過に偏りが生じる。その結果、被処理水が十分に浄化されなかったり、担体濾過層の濾過機能が不十分になったりする。
また、このような状況を回避するために、前記担体濾過層を保守点検する場合、前記担体が上方に浮上積層していると、担体処理槽上部側から容易に点検することができるため、その担体濾過層に固形成分が付着して蓄積されている状況が確認でき、このような固形成分を除去するような保守作業も容易に行える。そのため、前記担体同士が固形成分の付着に従って一体化し、固まるという不都合がおきにくくなり、担体処理槽内における濾過機能を高く維持することができる。
しかし、前記担体が浮上しているだけでは、流動しやすく、密には積層されにくいため、大量の担体を用いなければ十分な生物濾過機能が発揮されにくいという問題があり、さらに、大量の担体を逆洗流動させるためには、大容量の気泡を供給する必要がある。
一方、前記担体は担体処理槽の下方に沈降していると、担体濾過層を目視することが困難であるため、容易に点検することは困難である。
また、いずれの場合であっても、効率よく逆洗するために、前記担体濾過層に大容量の気泡を供給したり、頻繁に逆洗したりすると、前記担体処理槽の水位が気泡により変動して安定しにくくなったり、運転費が嵩んだりするという問題もある。
【0005】
従って、本発明の目的は、上記欠点に鑑み、担体処理槽における担体濾過層での濾過機能を高くしながら、逆洗によりその濾過機能を維持しやすい汚水処理装置を提供することにある。
【0006】
【課題を解決するための手段】
この目的を達成するための本発明の汚水処理装置の特徴構成は、
多数の担体を積層した担体濾過層を設け、被処理水を濾過処理可能に構成してある担体処理槽を備え、
水より比重の小さな材質の第一の担体の多数を、前記担体処理槽内に浮上積層させて第一の担体濾過層を形成してあるとともに、
水より比重の大きな材質の第二の担体の多数を、前記担体処理槽内に堆積積層させて第二の担体濾過層を形成してある点にある。
また、前記担体を前記担体処理槽内で流動させる担体流動装置を設けることが好ましく、
前記担体濾過層に散気する散気装置を設けて前記担体流動装置を構成してあることが好ましい。
また、前記担体濾過層の堆積高さが前記担体処理槽内の被処理水水位高さの1/2以下であることが好ましく、
前記担体処理槽の水面下に前記第一の担体濾過層を形成するとともに、前記担体濾過層に上方側から被処理水を分散供給する被処理水散水管を設けてあれば、尚良い。
【0007】
〔作用効果〕
つまり、多数の担体を積層した担体濾過層を設け、被処理水を濾過処理可能に構成してある担体処理槽を備えた水処理装置は、多数の担体を逆洗するだけで再生し濾過機能を維持できるため、高度水処理に適した担体処理槽を形成する。
前記担体を水より比重の小さな材質から形成すると、その担体は水に浮き、前記担体処理槽の上方に浮上する。すると、前記担体処理槽の上方に第一の担体が多数集合して第一の担体濾過層を形成されられる。
【0008】
尚、第一の担体濾過層における担体濾過の場合、被処理水を上から下方向に濾過する構成とすると、濾過された固形成分は主に担体濾過層の上面に保持されることになり、点検作業が容易になる。また、第一の担体は、下方側にに動きやすい構成であることと、被処理水の流れが、その担体を下方に動かす方向であることとにより、被処理水の濾過時に前記担体は、常時振動させられていることになる。そのため、固形成分が付着した担体は、隣接する担体と一体化しにくく、また、固形成分が多く付着して比重が大きくなった担体が担体濾過層の下部に移動するとともに、固形成分のあまり付着していない新たな担体が担体濾過層の上部に移動するという担体の緩やかな循環が期待でき、固形成分の濾過機能が高く維持されやすいものと考えられる。
【0009】
逆に、下から上方向に濾過する構成としてあれば、固形成分を濾過しながらも、濾過された固形成分が前記担体から剥離した場合に、下方に落下しやすくなるために、後述の第二の担体濾過層で剥離した固形成分を再度捕捉することができる。そのため、前記第一の担体濾過層内には、固形成分が蓄積されにくくなり、また、濾過された被処理水に剥離した固形成分が混入する虞も少なくなると考えられる。
【0010】
さらに、水より比重の大きな第二の担体の多数を前記担体処理槽内に堆積積層させてなる第二の担体濾過層を先の担体濾過層とは別に備えてあるので、前記担体処理槽内で被処理水が上昇、下降いずれの方向に通過する場合でも担体濾過層を2度通過することになる。前記被処理水から固形成分を濾過するために必要な担体濾過層厚みは、被処理水の水質によって決まるが、この厚みを2層に分けて確保することになると、一層あたりの厚みを小さく設定することができ、一層あたりの濾過抵抗を小さくできる。また、捕捉される固形成分の付着位置が分散されるので目詰まりがおきにくく、被処理水の流れが円滑になる。従って、担体濾過層全体としても、少ない担体で十分な生物濾過機能を発揮させることができることになり、その担体を逆洗、再生する場合であっても大きな動力等を要さない。従って、被処理水の処理効率が高く維持されやすく、また、前記担体処理槽の保守点検の省力化が図れる。
【0011】
また、前記担体を前記担体処理槽内で流動させる担体流動装置を設けてあれば、その担体流動装置により、担体を流動させるだけで担体同士の衝突を促し、その担体から固形成分を剥離させることができる。また、剥離された汚泥は、通常比重が水より大きいので沈殿し、沈降堆積させた担体濾過層に比べて、剥離させられた汚泥が担体に再付着するおそれが少ない。従って、前記担体濾過層の濾過機能は、容易に回復され、長期使用に際しても安定した機能を維持することができる。
【0012】
前記担体濾過層に散気する散気装置を設けて前記担体流動装置を構成してあると、散気により流動させられるので少ない動力で上述の高い効果を発揮する。また、散気装置によると、気泡の衝突により前記担体から固形成分を剥離する効果を奏し、効率よく前記担体を再生させられる。
尚、剥離された固形成分は、担体処理槽内に循環させられるので、再度生物処理、汚泥引き抜き処理等を行う場合にも、移送しやすい形態とできる。
【0013】
尚、上述の場合、上から下方向に被処理水を濾過すると、最初に固形成分の除去が行われ、固形成分が主に付着する担体濾過層が上に位置することになるので、保守点検作業が容易に行えて好都合である。またこの場合、上部に形成された第一の担体濾過層から固形成分剥離しても下方の第二の担体濾過層で、その固形成分を再度捕捉することができる。そのため、精密な固形成分濾過が可能になる。
【0014】
また、前記担体濾過層の堆積高さは、逆洗時に担体を流動させるに十分なスペースが確保する意味から、前記担体処理槽内の被処理水水位高さの概ね1/2以下とすることが好ましく、本発明の担体濾過層においては、第一、第二の担体濾過層を比較的少ない担体量で、十分な機能を付与しやすいことから、この設定寸法を実現しやすく、前記担体濾過層の形成されない中間空洞部が前記担体の逆洗時の担体の膨張、流動スペースとして活用できるようになるため、保守が効率よく行え、運転費等の低減を図ることができる。
【0015】
また、前記第一の担体濾過層を前記担体処理槽の水面下に形成するとともに上方側から被処理水を分散供給する被処理水散水管を設けてあると、前記担体濾過層に供給される被処理水は、前記担体濾過層の全体にまんべんなく供給されることになる。すると、被処理水が一箇所に集中して供給されると、前記担体濾過層の一部のみに固形成分が集中して付着し、担体の目詰まり一体化を起こしやすくなるのに対して、濾過層が全体的に均一に利用されることになって、担体の目詰まり、一体化が起こりにくくなるので好ましい。また、担体濾過層に供給される被処理水が分散され、一箇所に集中しにくいので、前記担体処理槽の水面下に担体濾過層が形成されているにもかかわらず、担体濾過層の一部が、水流により常時循環させられてしまい、濾過機能を発揮しにくくなるという不都合も回避することができる。尚、担体の浮上を規制する支持部材を水面下に設けると、前記担体処理槽の上部に担体の浮上を制限する担体支持部を設け、前記担体支持部下方側に前記担体濾過層を形成してあると、前記担体は浮上して前記担体支持部で保持されるため、担体が大きく偏って堆積することがないようにガイドできる。そのため、このような担体支持部により、担体に対する固形成分の集中をさけることも考えられるが、この場合、担体支持部材等によって、担体が目視しづらくなるなどして、メンテナンスの利便性が低下したり、その支持部材自体に目詰まりが生じるという不都合が生じやすくなるものと考えられる。そこで、前記第一の担体濾過層を前記担体処理槽の水面下に形成してあると、前記担体処理槽の水面下に担体濾過層が形成されていると、このような不都合も生じにくくなる。
【0016】
【発明の実施の形態】
以下に本発明の実施の形態を図面に基づいて説明する。
図1に示すように、本発明の汚水処理装置は、担体処理槽Eを備えてなる浄化槽を構成している。前記浄化槽は、上流側から、嫌気濾床槽第一室、第二室N1、N2、担体処理槽E、処理水槽Tを被処理水がこの順に移流するように設けてある。
【0017】
前記嫌気濾床槽第一室N1は、被処理水の原水の流入を受けて貯留する水処理室にハニカムネット状の嫌気濾床F1を内装して構成してある。また、前記水処理室には、一旦貯留した被処理水を定量的に前記嫌気濾床槽第二室N2へ移送するエアリフトポンプA1を立設して内装してある。
【0018】
前記嫌気濾床槽第二室N2は、前記嫌気濾床槽第一室N1からの被処理水を受けて一時貯留するとともに嫌気的に生物処理して浄化する嫌気濾床F2を、多数のかご状の担体から構成して設けてある。また、前記嫌気濾床第二室N2と前記担体処理槽Eとの間を仕切る隔壁W2には、被処理水を通過させる移流口Waを設けてあるとともに、その移流口Waから移流する被処理水量を、前記嫌気濾床槽第二室N2の水位に応じて抑制するための流量抑制板Wbを設けて構成してある。
前記嫌気濾床槽第一室N1に流入した被処理水のうち、被処理水の異常流入に伴って、前記嫌気濾床槽第一室、第二室N1,N2を仕切る隔壁W1を越えて前記嫌気濾床槽第二室N2に流入した被処理水は、前記流量抑制版Wbにより前記担体処理槽Eへの流入が抑制され、徐々に移流することになるから、前記嫌気濾床槽第一室、第二室N1,N2内に貯留され、被処理水の定常的に被処理水が移流されるように流量調整する機能を果たす。
【0019】
前記担体処理槽Eは、散気により流動させられる短パイプ状の担体Cとともに、被処理水を好気的に処理する担体流動部E1と、前記担体流動部E1で好気的に処理された被処理水を生物濾過する担体濾過部E2とから構成してある。
前記担体Cは、比重1.08程度のものを用い、前記担体流動部E1の容積のほぼ25〜35%の容積を占める量充填しておく。尚、前記担体Cは、前記担体流動部E1の上下に設けられるネット状の担体支持部S1,S2により、前記担体流動部E1から外部に流出せず、かつ担体流動部E1の内部で良好に流動できるように保持されている。
【0020】
前記担体流動部E1では、散気装置Dにより供給される気泡により、被処理水を汚泥とともに流動させ好気的に生物処理する。生物処理を受け清浄になった被処理水は、エアリフトポンプA2により担体濾過部E2に移送される。
前記エアリフトポンプA2は、前記担体流動部の上方から下方にわたって延設される縦管A21と、その縦管上部に設けられた計量升A22と、その計量升A22に揚水された被処理水を隣接する担体濾過部E2に移送させるための横管A23とからなる。
エアリフトポンプA2により前記担体濾過部E2に移流する被処理水は、担体濾過部E2上部に設けられた被処理水散水管Bにより、定量的に前記担体濾過部E2の上面に分散供給される。
【0021】
前記担体濾過部E2は、上方から供給される被処理水を受け、濾過済みの被処理水を下部の処理水移流部E23より処理水槽Tに移流させられる水処理室に多数の短パイプ状の担体C1,C2を収容して構成してある。前記水処理室は、収容される前記処理水移流部E23のやや上側にネット状の担体支持部S3を設け、隣接する水処理室への担体C1,C2の流出を抑制している。
【0022】
前記担体は、比重0.98程度の水より軽い第一担体C1および比重1.08程度の水より重い第二担体C2を備え、水面と担体支持部S3に挟まれた担体濾過部E2内のほぼ20〜25%の容積を占める量を充填しておく。
これにより、前記担体流動部E2には、水面の下方に前記第一担体C1の浮上堆積した第一担体濾過層E21が形成されるとともに、下側の担体支持部S2上に第二担体C2の沈降堆積した第二担体濾過層E22を形成する。
通常は、前記第一、第二担体濾過層E21,E22は、担体C1,C2が堆積した状態で、供給された被処理水を生物濾過する。生物濾過により清浄化された被処理水は、処理水として処理水槽Tへ移流させられるとともに、前記第一、第二担体濾過層E21,E22を構成する第一、第二担体C1,C2には、生物濾過により固形成分が付着する。
前記担体濾過部E2には、それぞれの担体濾過層E21,E22に堆積した第一、第二担体C1,C2に気泡を供給して前記担体濾過部E2内に流動させ、前記第一、第二担体C1,C2を流動させてほぐし、さらに、第一、第二担体C1,C2同士の衝突等により付着した固形成分を剥離除去させ再生させられる第一、第二散気装置D1,D2を設けて担体流動装置を形成してある。尚、前記第一散気装置は、前記第一担体濾過層のやや下方側に設けることが好ましい。
前記第一、第二担体C1,C2の堆積高さは前記担体濾過部E2の高さの40〜50%となっているので、前記担体流動装置のうち、前記第二散気装置D2からの散気により、容易にかつ効率よく流動させられ、第一、第二担体濾過層E21,E22を構成する第一、第二担体C1,C2を逆洗して再生させ、生物濾過効率を常に高く維持できるものとしてある。また、前記担体濾過部E2では、被処理水が上方から下方に濾過される構成となるので、前記固形成分は前記第一担体濾過層で優先的に捕捉される。そのため、前記第一散気装置D1を作動させると、前記第一担体濾過層のみを優先的に逆洗して再生することができ、前記担体濾過部E2を長期的に安定運転するのに役立てられる。また、このような構成により被処理水浄化機能が大きく向上し、硝化機能が高くなる。また、従来、第一、第二担体濾過層のいずれか一方しか備えない担体処理槽を用いてで運転されていた汚水処理装置では、透視度30〜35cm、BOD15〜20mg/L、COD30mg/L程度にしか浄化することができなかった被処理水を、上述の本発明の汚水処理装置で処理すると、透視度45〜50cm、BOD5〜10mg/L、COD15mg/L程度にまで浄化できることがわかり、きわめて高度な水処理が可能であることがわかった。
【0023】
また、前記第一、第二担体濾過層E21,E22の下方から被処理水を揚水するエアリフトポンプA3を設けて、前記担体濾過層E21,E22の再生により発生した固形成分等を嫌気濾床槽第一室N1に返送可能に構成してある。
前記エアリフトポンプA3は、前記担体濾過部E2の上方から前記担体濾過部E2の下方にまで延設される縦管A31と、その縦管A31上部に設けられた計量升A32と、その計量升A32に揚水された被処理水を前記嫌気濾床槽第一室N1に移送させるための横管A33とを備える。また、さらに余剰に揚水される被処理水を前記エアリフトポンプA2の計量升に返送する横管A34を備え、常時被処理水が循環させられる構成としてある。
これにより、前記エアリフトポンプA3は、常時濾過済の処理水を揚水するとともに、その処理水を前記嫌気濾床槽第一室N1に返送して脱窒をはかる。さらに、前記処理水中の窒素含有量を低下させるとともに、一部を前記担体濾過部E1に返送して濾過された処理水の再濾過を繰り返し、被処理水中からの固形成分の除去がより有効に行われる。また、担体濾過層E21,E22の逆洗時には、逆洗により発生した剥離汚泥等を急速に揚水返送することによって、固形成分のほとんどすべてが嫌気濾床槽第一室N1に返送され、処理水槽Tに固形成分が移流するのを防止する。
【0024】
前記第一、第二担体濾過層E21,E22を通過した処理水は、処理水移流部E23を経て処理水槽Tに移流する。前記処理水槽Tでは、被処理水を一時貯留しつつ、前記担体処理槽Eで除去しきれなかった被処理水中の固形成分を沈殿させ、上澄液のみを前記処理水槽T上部に設けられた消毒部Qを介して消毒した後、汚水処理装置外部に放流させられるように構成してある。
【図面の簡単な説明】
【図1】浄化槽の縦断側面図
【図2】浄化槽の要部縦断正面図
【図3】浄化槽の要部横断平面図
【図4】浄化槽の要部縦断斜視図
【符号の説明】
C1 第一担体
C2 第二担体
E2 担体処理槽
E21 第一担体濾過層
E22 第二担体濾過層
[0001]
TECHNICAL FIELD OF THE INVENTION
The present invention relates to a sewage treatment apparatus including a carrier treatment tank provided with a carrier filtration layer in which a number of carriers are stacked, and configured to be capable of filtering water to be treated.
[0002]
[Prior art]
Conventionally, as this type of sewage treatment apparatus, there has been known a sewage treatment apparatus in which a first carrier having a specific gravity slightly smaller than that of water is floated and laminated in a water treatment tank to form a carrier filtration layer.
On the other hand, there is also known a carrier in which a second carrier having a specific gravity slightly higher than that of water is settled and deposited in a water treatment tank to form a carrier filtration layer.
Such a carrier filtration layer has a function of biologically filtering the water to be treated that is advancing, and purifying the water to be treated with a microorganism film attached to the carrier. In addition, the solid component contained in the water to be treated can be removed, and plays a role of cleaning the water to be treated after being subjected to microbial treatment such as activated sludge treatment. The microbial membrane and the filtered solid components (hereinafter simply referred to as “solid components”) that are no longer needed in the carrier filtration layer are separated and removed from the carrier by backwashing the carrier and subjected to microbial treatment again. , And are stored so as to be able to be extracted as surplus sludge. At this time, the carrier is usually back-washed by supplying air bubbles from an air diffuser or the like provided in the carrier filtration layer.
In some cases, a carrier having a specific gravity lower than that of water is used in the carrier treatment tank in combination (see Patent Document 1). However, such a carrier is only used to flow in the tank by aeration or the like. It is not envisaged that both carriers are formed in the filtration layer.
[0003]
[Patent Document 1]
Japanese Patent Application Laid-Open No. H11-147095
[Problems to be solved by the invention]
However, the carrier filtration layer provided in such a sewage treatment apparatus accumulates in a layered manner when the carrier floats upward or sinks downward, forming a carrier filtration layer. When the carrier filtration layer is formed, solid components contained in the water to be treated are captured by the carrier in the carrier filtration layer and filtered. However, since the filtered solid component is held in a state of being captured between the carriers, it is likely to be solidified while being in contact with the carriers. For this reason, the carriers are solidified together and tend to be a large lump. Then, the carriers are hard to move individually, so that the carriers are not loosened as a whole, and the solid components held between the carriers are less likely to be separated from the carriers. Therefore, the above-described effect of the backwashing is less likely to appear, and the carrier filtration layer is likely to be clogged as a whole.
If the clogging tends to occur, the flow of the water to be treated through the carrier filtration layer becomes worse. Then, the flow of the water to be treated and the filtration of sludge in the carrier treatment tank are biased. As a result, the water to be treated is not sufficiently purified, or the filtration function of the carrier filtration layer becomes insufficient.
Further, in order to avoid such a situation, when performing maintenance and inspection of the carrier filtration layer, the carrier can be easily inspected from the upper side of the carrier treatment tank when the carrier is floated and laminated upward, The situation where the solid components adhere to and accumulate on the carrier filtration layer can be confirmed, and a maintenance operation for removing such solid components can be easily performed. Therefore, the inconvenience that the carriers are integrated and solidified according to the adhesion of the solid components is less likely to occur, and the filtration function in the carrier treatment tank can be maintained at a high level.
However, if the carrier is only floating, it is easy to flow and is difficult to be densely laminated. Therefore, there is a problem that it is difficult to exert a sufficient biological filtration function unless a large amount of the carrier is used. , It is necessary to supply a large volume of air bubbles.
On the other hand, if the carrier is settled below the carrier treatment tank, it is difficult to visually inspect the carrier filtration layer, and thus it is difficult to easily inspect the carrier filtration layer.
Also, in any case, in order to efficiently backwash, if a large volume of bubbles is supplied to the carrier filtration layer or if frequent backwashing is performed, the water level of the carrier treatment tank fluctuates due to bubbles. There is also a problem that it becomes difficult to stabilize and the operating cost increases.
[0005]
Accordingly, an object of the present invention is to provide a sewage treatment apparatus in which the filtration function of a carrier filtration layer in a carrier treatment tank is enhanced while the filtration function is easily maintained by backwashing, in view of the above-mentioned drawbacks.
[0006]
[Means for Solving the Problems]
The characteristic configuration of the sewage treatment apparatus of the present invention for achieving this object is as follows:
Providing a carrier filtration layer in which a number of carriers are laminated, comprising a carrier treatment tank configured to be capable of filtering the water to be treated,
A large number of first carriers of a material having a lower specific gravity than water are floated and laminated in the carrier treatment tank to form a first carrier filtration layer,
A point that the second carrier filtration layer is formed by depositing and laminating a large number of second carriers made of a material having a specific gravity larger than that of water in the carrier treatment tank.
Further, it is preferable to provide a carrier flow device for flowing the carrier in the carrier treatment tank,
It is preferable that an air diffuser that diffuses air to the carrier filtration layer is provided to constitute the carrier flow device.
Further, it is preferable that the deposition height of the carrier filtration layer is 1 / or less of the water level of the water to be treated in the carrier treatment tank,
It is more preferable that the first carrier filtration layer is formed below the water surface of the carrier treatment tank, and that the carrier filtration layer is provided with a treated water sprinkling pipe for dispersing and supplying the treated water from above.
[0007]
(Function and effect)
In other words, a water treatment apparatus provided with a carrier filtration layer in which a large number of carriers are laminated and provided with a carrier treatment tank configured to be capable of filtering the water to be treated is regenerated by simply backwashing a large number of carriers to perform a filtration function. Therefore, a carrier treatment tank suitable for advanced water treatment is formed.
When the carrier is formed of a material having a specific gravity smaller than that of water, the carrier floats on water and floats above the carrier treatment tank. Then, a large number of first carriers are gathered above the carrier treatment tank to form a first carrier filtration layer.
[0008]
Incidentally, in the case of the carrier filtration in the first carrier filtration layer, if the water to be treated is configured to be filtered downward from above, the filtered solid component is mainly held on the upper surface of the carrier filtration layer, Inspection work becomes easy. Further, the first carrier is configured to be easily moved downward, and the flow of the water to be treated is in a direction to move the carrier downward, so that the carrier is filtered during the filtration of the water to be treated, It means that it is always vibrated. Therefore, the carrier to which the solid component adheres is difficult to be integrated with the adjacent carrier, and the carrier having a large specific gravity due to the large amount of the solid component moves to the lower part of the carrier filtration layer, and the solid component adheres little. Slow circulation of the carrier can be expected in that a new carrier that has not moved to the upper part of the carrier filtration layer, and it is considered that the function of filtering solid components is easily maintained at a high level.
[0009]
Conversely, if it is configured to filter upward from the bottom, while filtering the solid component, when the filtered solid component is peeled off from the carrier, it is easy to drop downward, so that the second component described below is used. The solid component separated by the carrier filtration layer can be captured again. Therefore, it is considered that the solid component hardly accumulates in the first carrier filtration layer, and the possibility that the separated solid component is mixed into the filtered water to be treated is reduced.
[0010]
Further, since a second carrier filtration layer formed by stacking and laminating a large number of second carriers having a specific gravity greater than that of water in the carrier treatment tank is provided separately from the previous carrier filtration tank, Therefore, even if the water to be treated passes in either the upward or downward direction, the water passes through the carrier filtration layer twice. The thickness of the carrier filtration layer required for filtering solid components from the water to be treated is determined by the quality of the water to be treated, but if this thickness is to be divided into two layers, the thickness per layer is set to be small. And the filtration resistance per layer can be reduced. In addition, since the position where the captured solid component adheres is dispersed, clogging hardly occurs, and the flow of the water to be treated becomes smooth. Therefore, even the entire carrier filtration layer can exhibit a sufficient biofiltration function with a small amount of carrier, and does not require large power or the like even when the carrier is backwashed and regenerated. Therefore, the treatment efficiency of the water to be treated is easily maintained at a high level, and the maintenance and inspection of the carrier treatment tank can be labor-saving.
[0011]
In addition, if a carrier flow device for flowing the carrier in the carrier processing tank is provided, the carrier flow device promotes collision between the carriers simply by flowing the carriers, thereby separating solid components from the carrier. Can be. Further, the separated sludge usually precipitates because its specific gravity is larger than water, and the separated sludge is less likely to re-attach to the carrier as compared with the carrier filtration layer settled and deposited. Therefore, the filtration function of the carrier filtration layer can be easily restored, and a stable function can be maintained even during long-term use.
[0012]
When the carrier flow device is configured by providing an air diffusing device for diffusing air to the carrier filtration layer, the above-described high effect can be exhibited with a small amount of power because the carrier fluidizing device is made to flow by the air diffusing. In addition, according to the air diffuser, the solid component is separated from the carrier by collision of air bubbles, and the carrier can be efficiently regenerated.
Since the separated solid components are circulated in the carrier treatment tank, the solid components can be easily transported even when performing biological treatment, sludge extraction treatment, and the like again.
[0013]
In the case described above, if the water to be treated is filtered downward from the top, the solid component is removed first, and the carrier filtration layer to which the solid component mainly adheres is located on the upper side. The work is easy and convenient. Further, in this case, even if the solid component is peeled off from the first carrier filtration layer formed on the upper portion, the solid component can be captured again by the second carrier filtration layer below. Therefore, precise solid component filtration becomes possible.
[0014]
In addition, the deposition height of the carrier filtration layer is set to be approximately 以下 or less of the water level of the water to be treated in the carrier treatment tank in order to secure a sufficient space for flowing the carrier during the backwashing. Preferably, in the carrier filtration layer of the present invention, the first and second carrier filtration layers are relatively small in the amount of carrier, and since it is easy to impart sufficient functions, it is easy to realize this set dimension, and the carrier filtration Since the intermediate hollow portion where the layer is not formed can be used as an expansion and a flow space of the carrier at the time of back washing of the carrier, maintenance can be performed efficiently, and operation costs and the like can be reduced.
[0015]
Further, when the first carrier filtration layer is formed below the surface of the carrier treatment tank and a treated water sprinkling pipe for dispersing the treated water from above is provided, the first carrier filtration layer is supplied to the carrier filtration layer. The water to be treated is supplied evenly to the entire carrier filtration layer. Then, when the water to be treated is supplied in a concentrated manner at one location, the solid component is concentrated and adhered only to a part of the carrier filtration layer, whereas the carrier is likely to be clogged and integrated. This is preferable because the filter layer is uniformly used as a whole and the carrier is less likely to be clogged and integrated. Further, since the water to be treated supplied to the carrier filtration layer is dispersed and hardly concentrated at one place, the carrier filtration layer is formed under the water surface of the carrier treatment tank. The inconvenience that the part is constantly circulated by the water flow and it is difficult to exhibit the filtering function can be avoided. Incidentally, when a support member for regulating the floating of the carrier is provided below the water surface, a carrier supporting portion for restricting the floating of the carrier is provided above the carrier processing tank, and the carrier filtration layer is formed below the carrier supporting portion. In this case, since the carrier floats and is held by the carrier supporting portion, the carrier can be guided so as not to be largely unevenly deposited. For this reason, it is conceivable to avoid concentration of the solid component on the carrier by such a carrier support portion, but in this case, the carrier support member or the like makes it difficult to visually recognize the carrier, resulting in reduced maintenance convenience. It is considered that the disadvantage that the support member itself is clogged is likely to occur. Therefore, if the first carrier filtration layer is formed below the surface of the carrier treatment tank, and if the carrier filtration layer is formed below the surface of the carrier treatment tank, such inconveniences are less likely to occur. .
[0016]
BEST MODE FOR CARRYING OUT THE INVENTION
Embodiments of the present invention will be described below with reference to the drawings.
As shown in FIG. 1, the sewage treatment apparatus of the present invention constitutes a septic tank including a carrier treatment tank E. The septic tank is provided so that water to be treated flows through the first anaerobic filter bed tank, the second chambers N1, N2, the carrier treatment tank E, and the treated water tank T in this order from the upstream side.
[0017]
The anaerobic filter bed first chamber N1 is provided with a honeycomb net-shaped anaerobic filter bed F1 inside a water treatment chamber that receives and stores raw water to be treated. The water treatment chamber is provided with an air lift pump A1 for quantitatively transferring the to-be-processed water once stored to the anaerobic filter tank second chamber N2, and is internally provided.
[0018]
The anaerobic filter bed tank second chamber N2 receives the water to be treated from the anaerobic filter tank first chamber N1, temporarily stores the anaerobic filter bed tank N2, and anaerobically treats the biologically anaerobic filter bed F2 by a large number of baskets. It is constituted by a carrier in the shape of a circle. The partition wall W2, which partitions between the anaerobic filter bed second chamber N2 and the carrier treatment tank E, is provided with an advection port Wa through which the water to be treated passes, and a treatment port advected from the advection port Wa. A flow control plate Wb for controlling the amount of water in accordance with the water level of the anaerobic filter bed second chamber N2 is provided.
Of the water to be treated that has flowed into the anaerobic filter bed tank first chamber N1, the anaerobic filter bed tank first chamber and the partition wall W1 partitioning the second chambers N1 and N2 with the abnormal inflow of the water to be treated. The water to be treated that has flowed into the anaerobic filter bed tank second chamber N2 is prevented from flowing into the carrier treatment tank E by the flow suppression plate Wb, and is gradually transferred. One of the chambers is stored in the second chambers N1 and N2, and functions to adjust the flow rate so that the water to be treated is constantly transferred.
[0019]
The carrier treatment tank E was aerobically treated in the carrier flow section E1 and the carrier flow section E1 for aerobically treating the water to be treated, together with the short pipe-shaped carrier C caused to flow by aeration. And a carrier filtration unit E2 for biologically filtering the water to be treated.
The carrier C has a specific gravity of about 1.08, and is filled in an amount occupying approximately 25 to 35% of the volume of the carrier flowing section E1. Note that the carrier C does not flow out of the carrier flowing portion E1 due to the net-shaped carrier supporting portions S1 and S2 provided above and below the carrier flowing portion E1, and satisfactorily flows inside the carrier flowing portion E1. It is held so that it can flow.
[0020]
In the carrier flowing section E1, the water to be treated flows along with the sludge and is aerobically biologically treated by the bubbles supplied by the diffuser D. The water to be treated, which has been cleaned by the biological treatment, is transferred to the carrier filtration unit E2 by the air lift pump A2.
The air lift pump A2 adjoins a vertical pipe A21 extending from the upper part to the lower part of the carrier flow part, a measuring cell A22 provided on the upper part of the vertical pipe, and water to be treated pumped to the measuring cell A22. And a horizontal pipe A23 for transfer to the carrier filtration unit E2.
The water to be treated, which is transferred to the carrier filtration unit E2 by the air lift pump A2, is quantitatively dispersed and supplied to the upper surface of the carrier filtration unit E2 by the treated water sprinkling pipe B provided above the carrier filtration unit E2.
[0021]
The carrier filtration unit E2 receives the water to be treated supplied from above, and a large number of short pipe-shaped water treatment chambers in which the filtered water to be treated is transferred from the lower treated water advancing unit E23 to the treated water tank T. It is configured to accommodate the carriers C1 and C2. The water treatment chamber is provided with a net-shaped carrier support portion S3 slightly above the accommodated treated water advancing section E23 to suppress outflow of the carriers C1 and C2 to the adjacent water treatment chamber.
[0022]
The carrier has a first carrier C1 lighter than water having a specific gravity of about 0.98 and a second carrier C2 heavier than water having a specific gravity of about 1.08, and is provided in a carrier filtration section E2 sandwiched between a water surface and a carrier support section S3. An amount occupying approximately 20-25% of the volume is filled.
Thereby, the first carrier filtration layer E21 in which the first carrier C1 floats and accumulates is formed below the water surface in the carrier flow section E2, and the second carrier C2 is formed on the lower carrier support section S2. The second carrier filtration layer E22 that has settled and deposited is formed.
Normally, the first and second carrier filtration layers E21 and E22 biologically filter the supplied water to be treated while the carriers C1 and C2 are deposited. The water to be treated, which has been purified by biological filtration, is transferred to the treatment water tank T as treated water, and the first and second carriers C1 and C2 constituting the first and second carrier filtration layers E21 and E22 are provided with the treated water. The solid component adheres due to biological filtration.
In the carrier filtration unit E2, air bubbles are supplied to the first and second carriers C1 and C2 deposited on the respective carrier filtration layers E21 and E22 to flow into the carrier filtration unit E2, First and second air diffusers D1 and D2 are provided, which allow the carriers C1 and C2 to flow and loosen, and further remove and regenerate and regenerate solid components adhered by collision between the first and second carriers C1 and C2. To form a carrier flow device. Preferably, the first air diffuser is provided slightly below the first carrier filtration layer.
Since the deposition height of the first and second carriers C1 and C2 is 40 to 50% of the height of the carrier filtration unit E2, of the carrier flow device, the height of the second air diffusion device D2 It is easily and efficiently fluidized by aeration, and the first and second carriers C1 and C2 constituting the first and second carrier filtration layers E21 and E22 are backwashed and regenerated, and the biological filtration efficiency is always high. There are things that can be maintained. Further, in the carrier filtration unit E2, since the water to be treated is filtered downward from above, the solid component is preferentially captured by the first carrier filtration layer. Therefore, when the first air diffuser D1 is operated, only the first carrier filtration layer can be preferentially backwashed and regenerated, which is useful for long-term stable operation of the carrier filtration unit E2. Can be Further, with such a configuration, the treatment water purification function is greatly improved, and the nitrification function is enhanced. Further, conventionally, in a sewage treatment apparatus that has been operated using a carrier treatment tank provided with only one of the first and second carrier filtration layers, the transparency is 30 to 35 cm, the BOD is 15 to 20 mg / L, and the COD is 30 mg / L. The treated water that could only be purified to a degree was treated with the above-mentioned sewage treatment apparatus of the present invention, and it was found that the degree of transparency could be reduced to about 45 to 50 cm, BOD 5 to 10 mg / L, and COD 15 mg / L. It has been found that very advanced water treatment is possible.
[0023]
In addition, an air lift pump A3 for pumping water to be treated from below the first and second carrier filtration layers E21 and E22 is provided to remove solid components and the like generated by regeneration of the carrier filtration layers E21 and E22. It is configured so that it can be returned to the first room N1.
The air lift pump A3 includes a vertical tube A31 extending from above the carrier filtration unit E2 to below the carrier filtration unit E2, a measuring box A32 provided above the vertical tube A31, and a measuring box A32. And a horizontal pipe A33 for transferring the to-be-treated water pumped to the first anaerobic filter bed tank N1. Further, a horizontal pipe A34 for returning the excess water to be treated to the metering box of the air lift pump A2 is provided, and the water to be treated is constantly circulated.
Thus, the air lift pump A3 constantly pumps up the filtered treated water and returns the treated water to the first anaerobic filter bed tank N1 for denitrification. Furthermore, while reducing the nitrogen content in the treated water, a part of the treated water is returned to the carrier filtration unit E1, and the re-filtration of the filtered treated water is repeated, whereby the removal of solid components from the treated water is more effectively performed. Done. Also, at the time of back washing of the carrier filtration layers E21 and E22, almost all solid components are returned to the first anaerobic filter bed tank N1 by rapidly pumping and returning exfoliated sludge and the like generated by the back washing. Prevents solid components from advancing to T.
[0024]
The treated water that has passed through the first and second carrier filtration layers E21 and E22 flows through the treated water advancing section E23 to the treated water tank T. In the treated water tank T, while temporarily storing the treated water, solid components in the treated water that could not be removed in the carrier treatment tank E were precipitated, and only the supernatant was provided above the treated water tank T. After being disinfected through the disinfecting section Q, it is configured to be discharged outside the sewage treatment apparatus.
[Brief description of the drawings]
FIG. 1 is a vertical sectional side view of a septic tank. FIG. 2 is a vertical sectional front view of a main part of the septic tank. FIG. 3 is a cross-sectional plan view of a main part of the septic tank.
C1 first carrier C2 second carrier E2 carrier treatment tank E21 first carrier filtration layer E22 second carrier filtration layer

Claims (5)

多数の担体を積層した担体濾過層を設け、被処理水を濾過処理可能に構成してある担体処理槽を備えた汚水処理装置であって、
水より比重の小さな材質の第一の担体の多数を、前記担体処理槽内に浮上積層させて第一の担体濾過層を形成してあるとともに、
水より比重の大きな材質の第二の担体の多数を、前記担体処理槽内に堆積積層させて第二の担体濾過層を形成してある汚水処理装置。
A sewage treatment apparatus provided with a carrier filtration tank provided with a carrier filtration layer in which a large number of carriers are laminated, and a water to be treated is configured to be capable of being filtered.
A large number of first carriers of a material having a lower specific gravity than water are floated and laminated in the carrier treatment tank to form a first carrier filtration layer,
A sewage treatment apparatus in which a large number of second carriers having a specific gravity higher than that of water are deposited and laminated in the carrier treatment tank to form a second carrier filtration layer.
前記担体を前記担体処理槽内で流動させる担体流動装置を設けた請求項1に記載の汚水処理装置。The sewage treatment apparatus according to claim 1, further comprising a carrier flow device that causes the carrier to flow in the carrier treatment tank. 前記担体濾過層に散気する散気装置を設けて前記担体流動装置を構成してある請求項2に記載の汚水処理装置。The sewage treatment apparatus according to claim 2, wherein an air diffuser that diffuses air to the carrier filtration layer is provided to constitute the carrier flow device. 前記担体濾過層の堆積高さが前記担体処理槽内の被処理水水位高さの1/2以下である請求項1〜3のいずれか一項に記載の汚水処理装置。The sewage treatment apparatus according to any one of claims 1 to 3, wherein a deposition height of the carrier filtration layer is equal to or less than の of a water level of the water to be treated in the carrier treatment tank. 前記担体処理槽の水面下に前記第一の担体濾過層を形成するとともに、前記担体濾過層に上方側から被処理水を分散供給する被処理水散水管を設けた請求項1〜4のいずれか一項に記載の汚水処理装置。The first carrier filtration layer is formed below the surface of the carrier treatment tank, and a treated water sprinkling pipe for dispersing and supplying treated water from above is provided on the carrier filtration layer. The sewage treatment apparatus according to claim 1.
JP2003014754A 2003-01-23 2003-01-23 Sewage treatment apparatus Pending JP2004223417A (en)

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Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2010201378A (en) * 2009-03-04 2010-09-16 Kubota Corp Water-purifier tank and method for operating the same
JP2011000555A (en) * 2009-06-19 2011-01-06 Kubota Corp Wastewater treatment facility and method of rebuilding the same

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2010201378A (en) * 2009-03-04 2010-09-16 Kubota Corp Water-purifier tank and method for operating the same
JP2011000555A (en) * 2009-06-19 2011-01-06 Kubota Corp Wastewater treatment facility and method of rebuilding the same

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