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JP3607252B2 - Sewage treatment method and apparatus - Google Patents
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JP3607252B2 - Sewage treatment method and apparatus - Google Patents

Sewage treatment method and apparatus Download PDF

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JP3607252B2
JP3607252B2 JP2002043886A JP2002043886A JP3607252B2 JP 3607252 B2 JP3607252 B2 JP 3607252B2 JP 2002043886 A JP2002043886 A JP 2002043886A JP 2002043886 A JP2002043886 A JP 2002043886A JP 3607252 B2 JP3607252 B2 JP 3607252B2
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sewage
tank
stirring
spraying
adjusting material
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JP2003236590A (en
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賢二 川嶋
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KAWASHIMA CO Ltd
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KAWASHIMA CO Ltd
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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
    • Y02ATECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
    • Y02A40/00Adaptation technologies in agriculture, forestry, livestock or agroalimentary production
    • Y02A40/10Adaptation technologies in agriculture, forestry, livestock or agroalimentary production in agriculture
    • Y02A40/20Fertilizers of biological origin, e.g. guano or fertilizers made from animal corpses

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Description

【0001】
【発明の属する技術分野】
本発明は、家畜などが排泄した糞尿を処理する汚水処理方法及び汚水処理装置に係る技術分野に属する。
【0002】
【従来の技術】
従来、汚水処理装置としては、例えば、特開2001−121175号公報に記載のように、家庭などで使用される浄化槽がある。このような浄化槽においては、糞などの固形物を分離、濾過してこれらを除去する前処理槽と、生物濾過槽、処理水槽、消毒槽などから構成され、最終工程で浄化された水が浄化槽より排出されるものである。このうち、前処理槽には嫌気濾床槽第1室、嫌気濾床槽第2室を備えており、糞などの固形物の分離、除去を行っている。
【0003】
また、他の汚水処理装置としては、特開平10−224137号公報に記載のように、家畜の糞尿などを分解して肥料を製造処理する浄化槽がある。この浄化槽は、好気性バクテリアを含む水が浄化槽内に入れられ微小な気泡を発生させる散気管を備えた第1分解槽と、粗粒気泡が供給される第2分解槽と、熟成濃縮槽とを備え、糞尿は、順に各槽をオーバーフローしながら進んで最後に液肥となり、脱水された成分は細粒堆肥になるような装置である。
【0004】
また、他の汚水処理装置としては、特開平6−92765号公報に記載のものもある。これは、発酵槽に投入した堆肥材料を撹拌装置で攪拌しながら糞尿を攪拌中の堆肥材料に注入することで堆肥材料と糞尿の混合効率を高め、堆肥化することで糞尿を処理するものである。撹拌装置としては、チェーン、スプロケットをモータ駆動し、チェーンに取付けた羽根で堆肥材料を掻き上げ後方に落とす方式が示されている。
【0005】
また、他の汚水処理装置としては、図6に示すように、分離機91と、浄化槽92と、脱水機93と、堆肥製造器94からなるシステムである。すなわち、汚水(原水)90を遠心式などの分離機91に投入して固形物91aと水分91bに分離し、分離した汚水91bは次の浄化槽92(特開2001−121175号公報のような)に投入される。浄化槽92で分離された固形物92aは脱水機93でさらに水分が除かれ、水分の少ない固形物93aが堆肥製造機94(特開平6−92765号公報に示すような)に投入されて堆肥となって処理される。ここで、分離機91で分離された固形物91aは直接堆肥製造器94に投入されて処理される。また、脱水機93で除かれた水分93bは浄化槽92に戻される。そして、浄化槽92で浄化された浄化水92bは河川などに放流される構成となっている。
【0006】
【発明が解決しようとする課題】
前述の特開2001−121175号公報に記載のような汚水処理装置では、前処理槽において固形物を汚水と分離するために2つの嫌気濾床槽を必要とし、この分離工程が大がかりとなって費用がかかっている。また、前処理槽に溜まる汚泥の処理にも費用がかかり、さらに飼育する家畜の規模が大きくなるほど大規模若しくは多数の装置が必要となってしまい、このように大がかりな汚水処理装置では、費用的に採用しにくいという問題がある。
【0007】
また、特開平10−224137号公報に記載の汚水処理装置では、浄化水槽中のバクテリアによる分解で肥料化を行っている構成のため、その処理能力に限界がある。したがって、飼育する家畜の規模が大きくなると処理が追いつかず、より大型の、若しくは多数の装置を必要とし、このように大がかりな汚水処理装置では、費用的に採用しにくいという問題がある。
【0008】
また、特開平6−92765号公報に記載の汚水処理装置では、注入する糞尿の量、特に水分が多い場合は、撹拌装置のチェーンなどの比較的小さな部品の汚水による腐食が顕著であり、耐久性が無くなる。したがって、大量の糞尿、特に水分を多く含む糞尿を処理することができないという問題がある。
【0009】
また、図6に示した汚水処理装置では、分離機91と、浄化槽92と、脱水機93と、堆肥製造器94という4種類の機械を必要とし、大量の汚水を処理するとなると汚水処理プラントのようになってしまい、このように大がかりな汚水処理装置では、費用的に採用しにくいという問題がある。
【0010】
本発明は、このような問題点を考慮してなされたもので、簡素な方法で大量の糞尿を処理することができ、且つ、この処理により堆肥を製造可能な汚水処理方法を提供することを課題とする。
【0011】
また、簡素な装置で大量の糞尿を処理することができ、且つ、この処理により堆肥を製造可能な汚水処理装置を提供することを課題とする。
【0012】
【課題を解決するための手段】
前述の課題を解決するため、本発明に係る汚水処理方法は、次のような手段を採用する。
【0013】
即ち、請求項1では、処理槽に堆積させた水分調整材に家畜などから出る固形物を含む汚水を散布し、水分調整材と汚水を攪拌手段で攪拌するとともに、処理槽の下部に溜まる汚水を回収して処理槽内に散布する汚水処理方法であって、上記処理槽を、汚水を散布しながら攪拌する散布領域と汚水を散布せずに攪拌し乾燥を伴った発酵を熟成する熟成領域とに分け、攪拌手段は水分調整材と汚水との混合物を移送可能な移送機能を備え、上記混合物を所定の速度で散布領域側から熟成領域側へ攪拌しながら移送して発酵させ堆肥を製造することを特徴とする
【0014】
この手段では、固形物を含む汚水は処理槽内で水分調整材に散布され攪拌されて処理されるとともに、水分調整材に混ざらなかった汚水は回収され再び水分調整材に散布されて処理される。これにより、固形物と水分を分離することなく汚水は処理槽内部で全て処理される。
また、汚水は水分調整材と混合されて移送され、堆肥化されるとともに、新しい水分調整材が投入され汚水を散布可能にする。
さらに、散布領域で十分に汚水を散布された混合物は熟成領域に移送され、熟成が進む。
【0015】
また、請求項では、請求項記載の汚水処理方法において、攪拌手段は、1本または複数本のスクリューを備え、スクリューを回転させるとともに処理槽内を移動させて攪拌を行うことを特徴とする。
【0016】
この手段では、処理槽の上方に設けられたスクリューを回転させるとともに、スクリューを処理槽内で移動させて混合物の攪拌、移送が行われる。
【0017】
さらに、前述の課題を解決するために、本発明に係る汚水処理装置は、次のような手段を採用する。
【0018】
すなわち、請求項では、水分調整材を堆積させる処理槽と、家畜などから出る固形物を含む汚水を散布する散布装置と、水分調整材と汚水を攪拌する攪拌手段と、処理槽の下部に溜まる水分を回収する回収手段と、回収した汚水を再び上記散布装置に供給する供給手段を備え、処理槽を、汚水を散布しながら攪拌する散布領域と汚水を散布せずに攪拌し乾燥を伴った発酵を熟成する熟成領域とに分け、上記攪拌手段が、水分調整材と汚水との混合物を所定の速度で散布領域側から熟成領域側へ攪拌しながら移送可能な移送機能を備えてなる。
【0019】
この手段では、固形物を含む汚水は散布装置により水分調整材に散布され攪拌手段で攪拌されて処理されるとともに、水分調整材に混ざらなかった汚水は回収手段で回収され再び水分調整材に散布されて処理される。これにより、固形物と水分を分離する装置を用いることなく、汚水は処理槽内部で全て処理される。
また、汚水は散布領域で処理され、移送された混合物は熟成領域で熟成される。
【0020】
また、請求項では、請求項記載の汚水処理装置において、攪拌手段は、1本または複数本のスクリューを備え、処理槽の上方に移動可能に吊持されていることを特徴とする。
【0021】
この手段では、処理槽の上方に設けられたスクリューを回転させるとともに、スクリューを移動させて混合物の攪拌、移送が行われる。
【0022】
また、請求項では、請求項3又は4記載の汚水処理装置において、回収手段は、処理槽の底面に設けられる複数の汚水路と、複数の汚水路内の汚水をまとめる回収槽とからなることを特徴とする。
【0023】
この手段では、処理槽の底面に溜まる汚水は汚水路に流れ込み、汚水路から回収槽に導かれて回収される。
【0024】
【発明の実施の形態】
以下、本発明に係る汚水処理方法及びその装置の実施の形態を図面に基づいて説明する。
【0025】
図1〜図4は、本発明に係る汚水処理方法及びその装置の実施の形態(1)を示している。
【0026】
この実施の形態の汚水処理装置100は、水分調整材1を堆積させた処理槽2と、家畜などから出る固形物H1を含む汚水H(糞尿)を散布する散布装置3と、水分調整材1と汚水Hを攪拌して混合させる攪拌手段4と、処理槽2の下部に溜まる汚水Hを回収する回収手段5と、回収した汚水Hを散布装置3に供給する供給手段6で主に構成されている。
【0027】
処理槽2は、汚水Hを処理するとともに堆肥Cを製造するために設けられており、コンクリートなどで形成され高さが1m〜2m程度、長さが数m〜数十m若しくはそれ以上に延びる両側の側壁21、22と、底面23とで構成され、長手方向の両端は水分調整材1の投入口24、及び、製造される堆肥Cの取出口25となっている。
【0028】
処理槽2の側壁21、22の上面部21a、22aには、攪拌手段4の移動を可能にするレール(図示しない)が設けられている。また、処理槽2の側壁22に沿って汚水槽7が形成されている。この汚水槽7には、家畜などから排出される固形物H1を含む汚水H(糞尿)が外部から投入される。なお、通常、牛や豚などの家畜から出る汚水Hの構成は、80〜90%が尿からなる水分で、残りの10〜20%が糞からなる固形物H1となっている。
【0029】
また、水分調整材1とは、バーク(木の皮)、籾殻、おがくずなどからなるもので、糞尿を吸着し、その混合物Mが発酵して堆肥Cとなる原料である。
【0030】
なお、処理槽2は、図2に示すように、水分調整材1の投入される投入口24側が汚水を散布する散布領域26とされ、堆肥Cの取出口25側が汚水を散布せずに堆肥Cを発酵させて熟成する熟成領域27(ここに発酵槽が形成される)とされて、所定の比率(例えば半分)で分けられている。なお、散布領域26と熟成領域27の比率は、汚水Hの処理量の増減、製造される堆肥の種類などで適宜変更可能である。
【0031】
散布装置3は、処理槽2の上部の攪拌手段4に取付けられ、固形物H1を含む汚水Hを所定量溜められるほぼ半円管状に形成した汚水溜め31と、汚水溜め31の上面に多数の流出口32を備えたものである。汚水Hは、供給手段6から汚水溜め31に供給され、所定量以上になると汚水溜め31からオーバーフローして流出口32から処理槽2に流れ落ちる構成となっている。
【0032】
攪拌手段4は、処理槽2の上方に吊持された撹拌装置41と、撹拌装置41を処理槽2内で縦横(処理槽2の長手方向と幅方向)に自在に移動可能に吊持する移動装置45とから主に構成され、固形物H1を含む汚水Hと水分調整材1とを攪拌し混合させるものである。攪拌により好気性細菌を活性化させることができるとともに、攪拌手段4は、水分調整材1と汚水Hとの混合物Mを移送可能な移送機能を備えている。
【0033】
撹拌装置41は、2本のスクリュー42と、スクリュー42を駆動するモータ421と、モータ421の速度を減速し駆動トルクを増大させる減速機422を備えている。
【0034】
スクリュー42は、平行な2本の回転軸42aに互いの螺旋状の羽根42bが入り込むように取付けられたものであり、減速機422はモータ421の回転力を2つに分けて、2本のスクリュー42の回転軸42aを互いに逆方向へ回転駆動するように構成されている。なお、2本のスクリュー42は、側壁21、22に向かう方向に前後して並べられている。
【0035】
また、スクリュー42の回転軸42aは、図示しない油圧シリンダを用いた駆動装置により、支持ピン43を中心にしてその回転軸線の角度が調整可能であり、2本のスクリュー42の回転軸42aはその回転軸線を通る面の向きが少なくとも前進方向に90度回転可能となっている。そして、図3に示すようにスクリュー42を前方(図3では左方向)に傾けて回転させ、前方に移動させることで、前方の材料を羽根42bで掻き上げ、掻き上げられた材料が破線の矢印T’で示すように後方に落ちる。すなわち、前方の材料を後方に落としながら前進するので、傾けたスクリュー42は材料の移送機能を備えるものとなっている。
【0036】
なお、スクリュー42は二本に限定されるものではなく、一本でも三本以上でも機能を発揮することができる。なお、攪拌能力はスクリュー42の本数に応じてアップするが、コストアップもあるので、実験などを重ねた結果、2本が最も効率的と分かっている。
【0037】
移動装置45は、撹拌装置41を処理槽2の長手方向に移動させる長手方向移動装置46と、処理槽2の側壁21、22の方向に移動させる幅方向移動装置47とで構成される。
【0038】
長手方向移動装置46は、その車輪461が処理槽2の側壁21、22の上面部21a、22aのレール(図示しない)に載せられたフレーム462と、車輪461を駆動するモータ463と、フレーム462上に取付けられた作業台464と、作業台464に乗った作業員が操作可能な制御盤465などから構成される。
【0039】
幅方向移動装置47は、長手方向移動装置46のフレーム462に取付けられたアーチフレーム471に図示しない幅方向移動用のレールが設けられ、その上に設けられる車輪472を有するフレーム473と、フレーム移動装置474などから構成される。フレーム移動装置474は、フレーム473に掛けたワイヤーをモータで駆動する構成のものである。
【0040】
回収手段5は、散布装置3により水分調整材1にかけられた汚水Hが水分調整材1に混ざらずに処理槽2の底面23まで達した場合に、この汚水Hを回収する手段であり、底面23に設けられる複数の長手方向汚水路51と、長手方向汚水路51を連結する複数の幅方向汚水路52と、処理槽2の外部に延びる一つの長手方向汚水路51aと、この長手方向汚水路51aに流れる汚水Hを受けることで複数の汚水路51、52内の汚水Hをまとめる回収槽53と、回収槽53に集められた汚水Hを汚水槽7に汲み揚げるポンプ54及び配管55から構成されている。
【0041】
供給手段6は、汚水槽7に延びる吸引管61と、汚水槽7の上方で攪拌手段4の移動装置45に取付けられる吸引ポンプ62と、散布装置3に吸引した汚水Hを供給する供給管63とで構成される。吸引ポンプ62は、制御盤465に設けられるスイッチで、攪拌手段4の作動に連動させることも、また、攪拌手段4の作動と無関係に作動、非作動とすることも選択可能となっている。
【0042】
なお、回収手段5の長手方向汚水路51、及び、幅方向汚水路52には、水分調整材1と汚水Hの混合物Mに発酵を促進させ良質な堆肥Cを製造可能とするように、空気吹出孔81を有する送風パイプ8が入れられ、この送風パイプ8は側壁21、22に設けられるブロア(図示しない)などから空気Aが送られる構成となっている。ここで、長手方向汚水路51、及び、幅方向汚水路52の幅は送風パイプ8の外径より大きくしており、その隙間に汚水Hが流れ込むようになっている。
【0043】
また、処理槽2の上方には建屋の屋根が設けられ、雨水の浸入が防止されるとともに、建家の側壁は開放されて外気との通気性が確保されている。
【0044】
以上の汚水処理装置100による汚水処理方法について、以下に説明する。
【0045】
初めに汚水槽7に家畜などから排出される固形物H1を含む汚水H(糞尿)が投入される。また、処理槽2の投入口24から、バークなどの水分調整材1が投入される。
【0046】
そして、攪拌手段4を散布領域26に位置させ(図2参照)、散布領域26において散布装置3を作動させて汚水Hを散布しながら攪拌手段4を作動させる。このとき、攪拌手段4の撹拌装置41のスクリュー42を回転させながら、矢印Sで示すように処理槽2の側壁22の方向にスクリュー42を移動させ、側壁22に到達したら適度に前進させ(投入口24側に例えば50cm移動させ)、その位置から逆に側壁21の方向に移動させる。そして、側壁21に到達したら同様に適度に前進させるというように、ジグザグに攪拌を行っていく。
【0047】
この攪拌作業において、スクリュー42を前進方向に傾けておくことで、図2の矢印Tに示すように、掻き上げた水分調整材1と汚水Hとの混合物Mを少しずつ熟成領域27側に移送することができる。
【0048】
散布装置3により散布できる汚水Hの量は、処理槽2に投入されている水分調整材1の量によるが、仮に過剰に汚水Hを散布した場合でも、汚水Hは処理槽2の底面23に達し、回収手段5の各溝51、52から回収槽53を経てポンプ54で汚水槽7に戻されるので、汚水Hの投入量をあまり気にする必要がない。
【0049】
なお、従来例に示したチェーンタイプの攪拌手段では、水分調整材1に混ぜ合わされる汚水Hの水分率が高すぎるとチェーンなどの細かい構成部品に腐食などの不具合を容易に起こさせるため、汚水Hの投入量(水分率)に注意が必要だが、この実施の形態に用いているスクリュー42は構成が簡素で、羽根42bも強固なものとできるため、水分率を大きくしても耐久性を確保でき、攪拌作業に支障を来すことがない。
【0050】
したがって、投入口24から次々に水分調整材1を投入すれば大量の汚水Hを処理することが可能になる。また、固形物H1を含む汚水Hを散布できるので、従来の浄化槽や図6に示した分離機91のように汚水Hから固形物H1を分離する装置が必要なく、このような分離装置のコストが削減できる。また、汚水Hから固形物H1を分離する装置には、フィルターが使用される場合が多く、このフィルターは容易に目詰まりを起こすのでメンテナンスに手間がかかる。しかし、本発明では水分調整材1がフィルターの役目をし、そのフィルターは攪拌手段4で汚水Hと混ぜ合わされて常時新しいフィルターを形成しているので、目詰まりのような不具合を生じない。
【0051】
散布領域26で所定時間の攪拌が行われた水分調整材1と汚水Hとの混合物Mは、矢印Tに示すように、熟成領域27に移送され、熟成領域27で攪拌手段4により汚水Hを散布せずに攪拌が行われる。また、混合物Mには、処理槽2の底面23の溝51、52に設けられた送風パイプ8から空気が供給され、発酵が促進される。この発酵過程で、微生物が行う発酵処理に加え、混合物Mに含まれている水分も発酵で空気中に飛ばされ、発酵過程でも汚水処理が行われる。この熟成領域27での攪拌は1日に1回程度でよく、材料の投入から20日ないし30日程度で良好な堆肥Cが製造される。
【0052】
散布した汚水Hは堆肥Cとなって利用され、従来の浄化槽のように外部に排水を出さないので、河川や地下水など周囲の環境を汚染することがなく、また、攪拌手段4は従来のチェーンなどを用いた方式などに比べ、空気中への飛び跳ね量が少ないので、悪臭の発生を少なくでき、環境に優しい汚水処理装置となっている。
【0053】
すなわち、汚水処理装置100は複数の機能を備えるので、図6に示したシステムと比較してみると、分離機91、浄化槽92、脱水機93、堆肥製造器94の4種類の機械に代わることができる。これを費用的にみると、汚水処理装置100は、図6に示したシステムの堆肥製造器94の費用レベルでまかなうことが可能であり、高価な3種類の装置(分離機91、浄化槽92、脱水機93)のコストを省くことができる。
【0054】
なお、図6に示したシステムにおける浄化槽92では、汚水の汚れ度を示すBODが8,000、SSは16,000が限界とされているが、汚水処理装置100では実験によりBOD24,000、SS80,000の汚水も処理可能と分かっている。家畜の糞尿の汚れ度は、牛糞尿混合状態でBOD16,000、SS74,000、また、豚糞尿混合状態でBOD24,000、SS80,000(中央畜産会発表データより)となっており、図6に示したシステムでは、浄化槽92に投入する汚水の汚れ度を所定置まで低下させる分離機91が必要なことが分かる。
【0055】
また、乾燥を伴った堆肥の発酵には60℃以上を維持することが必要である。しかし、従来のチェーンなどを用いた方式の攪拌手段(他にロータリー式と呼ばれ、水車のような羽根車を回転させて堆肥材料をすくい上げて後方に飛ばす方式もある)は堆肥材料を飛ばしてしまい、攪拌によって温度を低下させるのに対し、この形態の攪拌手段4のスクリュー42では混合物Mを飛ばすことがほとんどない。したがって、攪拌による温度低下が少なく、寒冷地の冬季でも発酵温度を維持でき、1年中汚水処理及び発酵による堆肥製造を行うことができる。
【0056】
なお、回収手段5の長手方向汚水路51、及び、幅方向汚水路52には堆肥Cが少しずつ詰まるが、1年に1回程度掃除をすれば汚水Hの回収に支障を生じることはなく、汚水処理装置100のメンテナンスに手間はかからない。
【0057】
また、回収手段5は上記形態に限定されるものでなく、処理槽2の底面23に達する汚水Hを回収可能な構成であれば構わない。
【0058】
この実施の形態によれば、固形物H1を含む汚水Hは処理槽2内で水分調整材1に散布され攪拌されて処理されるとともに、水分調整材1に混ざらなかった汚水Hは回収され再び水分調整材1に散布されて処理される方法としたので、固形物H1と水分を分離することなく汚水Hは処理槽2内部で全て処理され、簡素な方法で大量の糞尿を処理することが可能となる。
【0059】
また、固形物H1を含む汚水Hは散布装置3により水分調整材1に散布され攪拌手段4で攪拌されて処理されるとともに、水分調整材1に混ざらなかった汚水Hは回収手段5で回収され再び水分調整材1に散布されて処理される装置としたので、固形物H1を分離する装置を用いることなく汚水Hは処理槽2内部で全て処理され、簡素な装置で大量の糞尿を処理することが可能となる。
【0060】
また、汚水Hは水分調整材1と混合されて移送され、堆肥化されるとともに、新しい水分調整材1が投入され汚水Hを散布可能にするようにしたので、次々に汚水Hが処理され、この処理に伴って、堆肥が製造されていく。
【0061】
【発明の効果】
以上のように、本発明の請求項1に係る汚水処理方法は、固形物を含む汚水は処理槽で水分調整材に散布され攪拌されて処理されるとともに、水分調整材に混ざらなかった汚水は回収され再び水分調整材に散布されて処理される方法としたので、固形物と水分を分離することなく汚水は処理槽内部で全て処理され、簡素な方法で大量の糞尿を処理することが可能となるという効果がある。
【0062】
また、本発明の請求項に係る汚水処理装置は、固形物を含む汚水は散布装置により水分調整材に散布され攪拌手段で攪拌されて処理されるとともに、水分調整材に混ざらなかった汚水は回収手段で回収され再び水分調整材に散布されて処理される装置としたので、固形物と水分を分離する装置を用いることなく汚水は処理槽内部で全て処理され、簡素な装置で大量の糞尿を処理することが可能となるという効果がある。
【図面の簡単な説明】
【図1】本発明に係る汚水処理方法及びその装置の実施の形態(1)を示す斜視図である。
【図2】本発明に係る汚水処理方法及びその装置の実施の形態(1)を示し、(a)は平面図、(b)は側面断面図である。
【図3】本発明に係る汚水処理方法及びその装置の実施の形態(1)の主要部品の正面図である。
【図4】図1のX−X線断面図である。
【図5】従来の汚水処理方法及びその装置を示す構成図である。
【符号の説明】
1 水分調整材
2 処理槽
3 散布装置
4 攪拌手段
5 回収手段
6 供給手段
7 汚水槽
8 送風パイプ
21 側壁
21a 上面部
22 側壁
22a 上面部
23 底面
24 投入口
25 取出口
26 散布領域
27 熟成領域
31 汚水溜め
32 流出口
41 撹拌装置
42 スクリュー
42a 回転軸
42b 羽根
43 支持ピン
45 移動装置
46 長手方向移動装置
47 幅方向移動装置
51 長手方向汚水路
51a 長手方向汚水路
52 幅方向汚水路
53 回収槽
54 ポンプ
55 配管
61 吸引管
62 吸引ポンプ
63 供給管
81 空気吹出孔
91 分離機
92 浄化槽
93 脱水機
94 堆肥製造機
100 汚水処理装置
421 モータ
422 減速機
461 車輪
462 フレーム
463 モータ
464 作業台
465 制御盤
471 アーチフレーム
472 車輪
473 フレーム
474 フレーム移動装置
A 空気
C 堆肥
M 混合物
H 汚水
H1 固形物
[0001]
BACKGROUND OF THE INVENTION
The present invention belongs to a technical field related to a sewage treatment method and a sewage treatment apparatus for treating manure excreted by livestock and the like.
[0002]
[Prior art]
Conventionally, as a sewage treatment apparatus, there exists a septic tank used at home etc. as described in Unexamined-Japanese-Patent No. 2001-121175, for example. Such a septic tank is composed of a pretreatment tank that separates and filters solids such as feces and removes them, a biological filtration tank, a treated water tank, a disinfection tank, and the like, and the purified water in the final step is the septic tank. Is more discharged. Among these, the pretreatment tank includes an anaerobic filter bed tank first chamber and an anaerobic filter bed tank second chamber, which separates and removes solids such as feces.
[0003]
Moreover, as another sewage treatment apparatus, there exists a septic tank which manufactures and processes fertilizer by decomposing livestock manure etc. as described in Unexamined-Japanese-Patent No. 10-224137. The septic tank includes a first decomposition tank having a diffuser tube in which water containing aerobic bacteria is put into the septic tank to generate fine bubbles, a second decomposition tank to which coarse bubbles are supplied, an aging concentration tank, The manure is a device that progresses while sequentially overflowing each tank, finally becomes liquid fertilizer, and the dehydrated component becomes fine compost.
[0004]
Another sewage treatment apparatus is described in JP-A-6-92765. This is to improve the mixing efficiency of compost material and manure by injecting manure into the compost material being stirred while stirring the compost material put into the fermenter with a stirrer, and treat manure by composting. is there. As a stirring device, a system in which a chain and a sprocket are driven by a motor, and a compost material is scraped up and dropped backward by blades attached to the chain is shown.
[0005]
Further, as another sewage treatment apparatus, as shown in FIG. 6, a system comprising a separator 91, a septic tank 92, a dehydrator 93, and a compost maker 94. That is, sewage (raw water) 90 is put into a separator 91 such as a centrifugal type to separate solid matter 91a and moisture 91b, and the separated sewage 91b is the next septic tank 92 (as disclosed in JP 2001-121175 A). It is thrown into. The solid matter 92a separated in the septic tank 92 is further dehydrated by a dehydrator 93, and the solid matter 93a having a small amount of water is put into a composting machine 94 (as shown in Japanese Patent Laid-Open No. 6-92765) and composted. Will be processed. Here, the solid material 91a separated by the separator 91 is directly put into the composting machine 94 and processed. Further, the water 93b removed by the dehydrator 93 is returned to the septic tank 92. The purified water 92b purified in the septic tank 92 is discharged into a river or the like.
[0006]
[Problems to be solved by the invention]
In the sewage treatment apparatus as described in JP-A-2001-121175, two anaerobic filter bed tanks are required in order to separate solids from sewage in the pretreatment tank, and this separation step becomes a major factor. It costs money. In addition, the treatment of sludge accumulated in the pretreatment tank is also expensive, and as the scale of livestock to be reared increases, a large-scale or a large number of devices are required. There is a problem that it is difficult to adopt.
[0007]
Moreover, in the sewage treatment apparatus described in Japanese Patent Application Laid-Open No. 10-224137, the treatment capacity is limited because of the configuration in which the fertilizer is formed by decomposition with bacteria in the purified water tank. Therefore, when the scale of livestock to be raised becomes large, the treatment cannot catch up, and a larger or a large number of devices are required, and there is a problem that such a large-scale sewage treatment device is difficult to adopt in terms of cost.
[0008]
Further, in the sewage treatment apparatus described in JP-A-6-92765, when the amount of urine to be injected, especially when there is a large amount of water, corrosion due to sewage of relatively small parts such as a chain of a stirring apparatus is remarkable, and durability Sex is lost. Therefore, there is a problem that a large amount of manure, particularly manure containing a lot of water cannot be processed.
[0009]
Further, the sewage treatment apparatus shown in FIG. 6 requires four types of machines, that is, a separator 91, a septic tank 92, a dehydrator 93, and a composting machine 94. When a large amount of sewage is treated, the sewage treatment plant In such a large-scale sewage treatment apparatus, there is a problem that it is difficult to adopt in terms of cost.
[0010]
The present invention has been made in view of such problems, and provides a sewage treatment method capable of treating a large amount of manure by a simple method and capable of producing compost by this treatment. Let it be an issue.
[0011]
It is another object of the present invention to provide a sewage treatment apparatus capable of treating a large amount of manure with a simple apparatus and capable of producing compost by this treatment.
[0012]
[Means for Solving the Problems]
In order to solve the above-described problems, the sewage treatment method according to the present invention employs the following means.
[0013]
That is, according to claim 1, sewage containing solid matter from livestock or the like is sprayed on the moisture adjusting material deposited in the treatment tank, and the moisture adjusting material and the sewage are stirred by the stirring means, and the sewage collected in the lower part of the treatment tank Is a sewage treatment method for collecting and spraying in a treatment tank, wherein the treatment tank is agitated while spraying sewage, and a ripening area for stirring and drying without sewage ripening fermentation. The agitation means is equipped with a transfer function that can transfer a mixture of moisture adjusting material and sewage, and fertilizes the mixture by stirring it from the spraying area side to the aging area side at a predetermined speed and fermenting it. It is characterized by doing .
[0014]
In this means, sewage containing solids is sprinkled on the moisture adjusting material in the treatment tank and stirred and processed, and sewage not mixed with the moisture adjusting material is recovered and again sprayed on the moisture adjusting material and processed. . Thereby, all the sewage is processed inside a processing tank, without isolate | separating a solid substance and a water | moisture content.
In addition, the sewage is mixed with the moisture adjusting material, transferred, and composted, and a new moisture adjusting material is introduced to allow the sewage to be sprayed.
Further, the mixture in which the sewage is sufficiently sprayed in the spraying area is transferred to the maturing area, and the maturing proceeds.
[0015]
Further, according to claim 2 , in the sewage treatment method according to claim 1 , the stirring means includes one or a plurality of screws, and the stirring is performed by rotating the screw and moving the inside of the treatment tank. To do.
[0016]
In this means, the screw provided above the processing tank is rotated, and the screw is moved in the processing tank to stir and transfer the mixture.
[0017]
Furthermore, in order to solve the above-described problems, the sewage treatment apparatus according to the present invention employs the following means.
[0018]
That is, in claim 3 , a treatment tank for depositing moisture adjusting material, a spraying device for spraying sewage containing solid matter from livestock, etc., a stirring means for stirring the moisture adjusting material and sewage, and a lower part of the treatment tank A recovery means for recovering the accumulated water and a supply means for supplying the recovered sewage to the spraying device again. The treatment tank is stirred while spraying the sewage, and is stirred and dried without spraying the sewage. The agitation means is provided with a transfer function capable of transferring the mixture of the moisture adjusting material and the sewage from the spraying area side to the aging area side at a predetermined speed while stirring .
[0019]
In this means, the sewage containing solid matter is sprayed on the moisture adjusting material by the spraying device and stirred and processed by the stirring means, and the sewage not mixed with the moisture adjusting material is collected by the collecting means and sprayed again on the moisture adjusting material. To be processed. Thereby, all the waste water is processed inside a processing tank, without using the apparatus which isolate | separates a solid substance and a water | moisture content.
Further, the sewage is treated in the spraying area, and the transferred mixture is aged in the aging area.
[0020]
According to a fourth aspect of the present invention, in the sewage treatment apparatus according to the third aspect , the stirring means includes one or a plurality of screws and is suspended above the treatment tank so as to be movable.
[0021]
In this means, the screw provided above the treatment tank is rotated and the screw is moved to stir and transfer the mixture.
[0022]
Further, according to claim 5 , in the sewage treatment apparatus according to claim 3 or 4 , the recovery means includes a plurality of sewage channels provided on the bottom surface of the treatment tank and a recovery tank for collecting sewage in the plurality of sewage channels. It is characterized by that.
[0023]
In this means, the sewage collected on the bottom surface of the treatment tank flows into the sewage channel, and is guided from the sewage channel to the recovery tank and collected.
[0024]
DETAILED DESCRIPTION OF THE INVENTION
DESCRIPTION OF EMBODIMENTS Hereinafter, embodiments of a sewage treatment method and apparatus according to the present invention will be described with reference to the drawings.
[0025]
1 to 4 show an embodiment (1) of a sewage treatment method and apparatus according to the present invention.
[0026]
The sewage treatment apparatus 100 according to this embodiment includes a treatment tank 2 in which a moisture adjusting material 1 is deposited, a spraying device 3 that sprays sewage H (feces and urine) containing solid matter H1 from livestock and the like, and a moisture adjusting material 1. And agitation means 4 for agitating and mixing the sewage H, a recovery means 5 for recovering the sewage H collected in the lower part of the treatment tank 2, and a supply means 6 for supplying the recovered sewage H to the spraying device 3. ing.
[0027]
The treatment tank 2 is provided for treating the sewage H and producing the compost C, and is formed of concrete or the like and has a height of about 1 m to 2 m and a length of several m to several tens m or more. It is comprised by the side walls 21 and 22 and the bottom face 23 of both sides, and the both ends of the longitudinal direction are the inlet 24 of the moisture adjusting material 1, and the outlet 25 of the compost C manufactured.
[0028]
Rails (not shown) that allow the stirring means 4 to move are provided on the upper surface portions 21 a and 22 a of the side walls 21 and 22 of the processing tank 2. A sewage tank 7 is formed along the side wall 22 of the treatment tank 2. The sewage tank 7 is filled with sewage H (feces and urine) containing solid matter H1 discharged from livestock and the like from the outside. Normally, the composition of sewage H from livestock such as cows and pigs is 80 to 90% of water composed of urine, and the remaining 10 to 20% is solid matter H1 composed of feces.
[0029]
The moisture adjusting material 1 is made of bark (bark of wood), rice husk, sawdust, etc., and is a raw material that adsorbs manure and fermentes the mixture M into compost C.
[0030]
In the treatment tank 2, as shown in FIG. 2, the side of the inlet 24 into which the moisture adjusting material 1 is charged is a spraying area 26 for spraying sewage, and the compost C outlet 25 side is composted without spraying sewage. A ripening region 27 (fermenter is formed here) in which C is fermented and matured is divided at a predetermined ratio (for example, half). In addition, the ratio of the spreading | spreading area | region 26 and the maturation area | region 27 can be suitably changed with the increase / decrease in the processing amount of the sewage H, the kind of compost manufactured.
[0031]
The spraying device 3 is attached to the stirring means 4 at the upper part of the treatment tank 2, and has a sewage reservoir 31 formed in a substantially semicircular tubular shape capable of storing a predetermined amount of sewage H containing solid matter H 1, and a large number of sewage reservoirs 31 An outflow port 32 is provided. The sewage H is supplied from the supply means 6 to the sewage reservoir 31 and overflows from the sewage reservoir 31 and flows down from the outlet 32 to the treatment tank 2 when the amount exceeds a predetermined amount.
[0032]
The stirring means 4 suspends the stirring device 41 suspended above the processing tank 2 and the stirring device 41 so as to be freely movable in the processing tank 2 in the vertical and horizontal directions (longitudinal direction and width direction of the processing tank 2). It is mainly comprised from the moving apparatus 45, and the waste water H containing the solid substance H1 and the moisture adjusting material 1 are stirred and mixed. The aerobic bacteria can be activated by stirring, and the stirring means 4 has a transfer function capable of transferring the mixture M of the moisture adjusting material 1 and the sewage H.
[0033]
The stirring device 41 includes two screws 42, a motor 421 that drives the screw 42, and a speed reducer 422 that reduces the speed of the motor 421 and increases the driving torque.
[0034]
The screw 42 is attached so that the two spiral blades 42b enter the two parallel rotating shafts 42a. The speed reducer 422 divides the rotational force of the motor 421 into two parts, The rotary shaft 42a of the screw 42 is configured to be driven to rotate in opposite directions. The two screws 42 are arranged back and forth in the direction toward the side walls 21 and 22.
[0035]
Further, the rotation axis 42a of the screw 42 can be adjusted in the angle of the rotation axis around the support pin 43 by a driving device using a hydraulic cylinder (not shown). The direction of the surface passing through the rotation axis is rotatable at least 90 degrees in the forward direction. Then, as shown in FIG. 3, the screw 42 is tilted and rotated forward (leftward in FIG. 3) and moved forward, whereby the material in front is scraped up by the blades 42b, and the scraped material is broken by a broken line. It falls backward as indicated by arrow T ′. That is, since the forward material is moved forward while dropping, the tilted screw 42 has a material transfer function.
[0036]
Note that the number of screws 42 is not limited to two, and the function can be exhibited by one or three or more screws. The stirring capacity increases according to the number of screws 42, but there is also an increase in cost, and as a result of repeated experiments, it has been found that two are the most efficient.
[0037]
The moving device 45 includes a longitudinal direction moving device 46 that moves the stirring device 41 in the longitudinal direction of the processing tank 2, and a width direction moving device 47 that moves the stirring device 41 in the direction of the side walls 21 and 22 of the processing tank 2.
[0038]
The longitudinal movement device 46 includes a frame 462 on which wheels 461 are mounted on rails (not shown) of the upper surface portions 21a and 22a of the side walls 21 and 22 of the processing tank 2, a motor 463 that drives the wheels 461, and a frame 462. The work table 464 is mounted on the work table 464, and a control panel 465 that can be operated by a worker on the work table 464.
[0039]
The width direction moving device 47 includes a frame 473 having wheels 472 provided on a rail for moving in the width direction (not shown) provided on an arch frame 471 attached to the frame 462 of the longitudinal direction moving device 46, and frame movement. The apparatus 474 is configured. The frame moving device 474 has a configuration in which a wire hung on the frame 473 is driven by a motor.
[0040]
The recovery means 5 is means for recovering the sewage H when the sewage H applied to the moisture adjusting material 1 by the spraying device 3 reaches the bottom surface 23 of the treatment tank 2 without being mixed with the moisture adjusting material 1. 23, a plurality of longitudinal sewage channels 51, a plurality of widthwise sewage channels 52 connecting the longitudinal sewage channels 51, a longitudinal sewage channel 51a extending to the outside of the treatment tank 2, and the longitudinal sewage channels. From the collection tank 53 that collects the sewage H in the plurality of sewage paths 51 and 52 by receiving the sewage H flowing in the channel 51a, the pump 54 and the pipe 55 that pump the sewage H collected in the collection tank 53 to the sewage tank 7 It is configured.
[0041]
The supply means 6 includes a suction pipe 61 extending to the sewage tank 7, a suction pump 62 attached to the moving device 45 of the stirring means 4 above the sewage tank 7, and a supply pipe 63 for supplying the sewage H sucked to the spraying device 3. It consists of. The suction pump 62 is a switch provided in the control panel 465 and can be selected to be interlocked with the operation of the stirring means 4 or to be activated or deactivated independently of the operation of the stirring means 4.
[0042]
In addition, in the longitudinal direction sewage channel 51 and the width direction sewage channel 52 of the recovery means 5, air is used so that the mixture M of the moisture adjusting material 1 and the sewage H can promote fermentation and can produce high-quality compost C. A blower pipe 8 having a blowout hole 81 is inserted, and the blower pipe 8 is configured such that air A is sent from blowers (not shown) provided on the side walls 21 and 22. Here, the widths of the longitudinal direction sewage channel 51 and the width direction sewage channel 52 are larger than the outer diameter of the blower pipe 8, and the sewage H flows into the gaps.
[0043]
In addition, a roof of the building is provided above the treatment tank 2 to prevent intrusion of rainwater, and the side wall of the building is opened to ensure air permeability with outside air.
[0044]
The sewage treatment method by the above sewage treatment apparatus 100 will be described below.
[0045]
First, sewage H (feces and urine) containing solid matter H1 discharged from livestock and the like is charged into the sewage tank 7. Further, the moisture adjusting material 1 such as bark is fed from the charging port 24 of the processing tank 2.
[0046]
Then, the stirring means 4 is positioned in the spraying region 26 (see FIG. 2), and the stirring device 4 is operated while spraying the sewage H by operating the spraying device 3 in the spraying region 26. At this time, while rotating the screw 42 of the stirring device 41 of the stirring means 4, the screw 42 is moved in the direction of the side wall 22 of the processing tank 2 as indicated by the arrow S, and when reaching the side wall 22, the screw 42 is moved forward moderately (input). For example, it is moved 50 cm to the mouth 24 side), and is moved in the direction of the side wall 21 from the position. And if it reaches the side wall 21, it stirs zigzag so that it may advance appropriately similarly.
[0047]
In this stirring operation, by tilting the screw 42 in the forward direction, as shown by an arrow T in FIG. 2, the mixture M of the moisture adjusting material 1 and the sewage H that have been scraped up is gradually transferred to the aging region 27 side. can do.
[0048]
The amount of sewage H that can be sprayed by the spraying device 3 depends on the amount of the moisture adjusting material 1 that has been put into the treatment tank 2, but even if the sewage H is sprayed excessively, the sewage H remains on the bottom surface 23 of the treatment tank 2. Since it reaches the sewage tank 7 by the pump 54 from the grooves 51 and 52 of the recovery means 5 through the recovery tank 53, it is not necessary to worry too much about the input amount of the sewage H.
[0049]
In the chain type stirring means shown in the conventional example, if the moisture content of the sewage H mixed with the moisture adjusting material 1 is too high, fine components such as the chain easily cause problems such as corrosion. However, since the screw 42 used in this embodiment has a simple structure and the blades 42b can be made strong, durability is ensured even if the moisture content is increased. It does not hinder the stirring work.
[0050]
Therefore, a large amount of sewage H can be treated by sequentially supplying the moisture adjusting material 1 from the inlet 24. Moreover, since the sewage H containing the solid matter H1 can be sprayed, there is no need for a device for separating the solid matter H1 from the sewage H as in the conventional septic tank or the separator 91 shown in FIG. 6, and the cost of such a separation device. Can be reduced. In addition, a filter is often used for the apparatus that separates the solid matter H1 from the sewage H. Since this filter easily clogs, maintenance is troublesome. However, in the present invention, the moisture adjusting material 1 serves as a filter, and the filter is mixed with the sewage H by the stirring means 4 to form a new filter at all times, so that a problem such as clogging does not occur.
[0051]
The mixture M of the moisture adjusting material 1 and the sewage H that has been stirred for a predetermined time in the spraying region 26 is transferred to the aging region 27 as indicated by an arrow T, and the sewage H is removed by the stirring means 4 in the aging region 27. Agitation is carried out without spraying. Moreover, air is supplied to the mixture M from the ventilation pipe 8 provided in the groove | channels 51 and 52 of the bottom face 23 of the processing tank 2, and fermentation is accelerated | stimulated. In this fermentation process, in addition to the fermentation process performed by the microorganisms, the water contained in the mixture M is also blown into the air by fermentation, and the sewage process is also performed in the fermentation process. Stirring in the ripening region 27 may be about once a day, and good compost C is produced in about 20 to 30 days after the material is charged.
[0052]
Dispersed sewage H is used as compost C and does not discharge to the outside unlike conventional septic tanks, so it does not pollute the surrounding environment such as rivers and groundwater, and stirring means 4 is a conventional chain. Compared to methods using the above, etc., the amount of jumping into the air is small, so that the generation of bad odor can be reduced and the sewage treatment apparatus is environmentally friendly.
[0053]
In other words, since the sewage treatment apparatus 100 has a plurality of functions, when compared with the system shown in FIG. Can do. Looking at this in terms of cost, the sewage treatment apparatus 100 can cover the cost level of the compost maker 94 of the system shown in FIG. 6, and three kinds of expensive apparatuses (separator 91, septic tank 92, The cost of the dehydrator 93) can be saved.
[0054]
In the septic tank 92 in the system shown in FIG. 6, BOD indicating the degree of contamination of sewage is limited to 8,000 and SS is limited to 16,000. However, in the sewage treatment apparatus 100, BOD 24,000 and SS80 are experimentally determined. It is known that 1,000 sewage can be treated. The degree of contamination of livestock manure is BOD 16,000 and SS 74,000 in the cattle manure mixed state, and BOD 24,000 and SS 80,000 in the swine manure mixed state (from data presented by the Central Livestock Association). In the system shown in FIG. 5, it is understood that the separator 91 that reduces the degree of contamination of the sewage introduced into the septic tank 92 to a predetermined position is necessary.
[0055]
Moreover, it is necessary to maintain 60 degreeC or more for the fermentation of the compost accompanying drying. However, conventional agitation means using a chain or the like (also called a rotary type, there is also a method of rotating an impeller like a water wheel to scoop up the compost material and fly it backwards). In contrast, the temperature is lowered by stirring, whereas the screw M of the stirring means 4 of this embodiment hardly blows the mixture M. Therefore, the temperature drop due to stirring is small, the fermentation temperature can be maintained even in winter in cold regions, and compost production can be performed through sewage treatment and fermentation throughout the year.
[0056]
The longitudinal sewage channel 51 and the widthwise sewage channel 52 of the collecting means 5 are clogged with compost C little by little. However, if the cleaning is performed once a year, there is no problem in collecting the sewage H. The maintenance of the sewage treatment apparatus 100 does not take time.
[0057]
Moreover, the collection | recovery means 5 is not limited to the said form, What is necessary is just a structure which can collect | recover the sewage H which reaches the bottom face 23 of the processing tank 2. FIG.
[0058]
According to this embodiment, the sewage H containing the solid matter H1 is sprinkled on the moisture adjusting material 1 in the treatment tank 2 and stirred and processed, and the sewage H that has not been mixed with the moisture adjusting material 1 is recovered and again. Since it was set as the method of disperse | distributing and processing to the moisture adjusting material 1, all the waste water H is processed inside the processing tank 2 without isolate | separating a solid substance H1 and a water | moisture content, and it can process a lot of excrement by a simple method. It becomes possible.
[0059]
Further, the sewage H containing the solid matter H1 is sprayed on the moisture adjusting material 1 by the spraying device 3 and stirred and processed by the stirring means 4, and the sewage H not mixed with the moisture adjusting material 1 is recovered by the collecting means 5. Since the device is again sprayed on the moisture adjusting material 1 and processed, the sewage H is completely processed inside the processing tank 2 without using a device for separating the solid matter H1, and a large amount of manure is processed with a simple device. It becomes possible.
[0060]
In addition, since the sewage H is mixed with the moisture adjusting material 1 and transferred and composted, and the new moisture adjusting material 1 is introduced so that the sewage H can be sprayed, the sewage H is treated one after another. With this treatment, compost is produced.
[0061]
【The invention's effect】
As described above, in the sewage treatment method according to claim 1 of the present invention, the sewage containing solid matter is sprayed and treated in the moisture adjusting material in the treatment tank, and the sewage not mixed with the moisture adjusting material is Because it is a method that is recovered and sprayed again on the moisture adjusting material, all wastewater is treated inside the treatment tank without separating solids and moisture, and a large amount of manure can be treated with a simple method. It has the effect of becoming.
[0062]
Further, in the sewage treatment apparatus according to claim 3 of the present invention, the sewage containing solid matter is sprayed on the moisture adjusting material by the dispersing device and stirred and processed by the stirring means, and the sewage not mixed with the moisture adjusting material is Since it is a device that is recovered by the recovery means and sprayed again on the moisture adjusting material, it is processed without any use of a device that separates solids and moisture, and all sewage is processed inside the processing tank. There is an effect that it becomes possible to process.
[Brief description of the drawings]
FIG. 1 is a perspective view showing an embodiment (1) of a wastewater treatment method and apparatus according to the present invention.
FIG. 2 shows an embodiment (1) of the sewage treatment method and apparatus according to the present invention, wherein (a) is a plan view and (b) is a side sectional view.
FIG. 3 is a front view of main components of Embodiment (1) of the sewage treatment method and apparatus according to the present invention.
4 is a cross-sectional view taken along line XX of FIG.
FIG. 5 is a block diagram showing a conventional sewage treatment method and apparatus.
[Explanation of symbols]
DESCRIPTION OF SYMBOLS 1 Moisture adjusting material 2 Processing tank 3 Spreading device 4 Agitation means 5 Recovery means 6 Supply means 7 Sewage tank 8 Blow pipe 21 Side wall 21a Upper surface part 22 Side wall 22a Upper surface part 23 Bottom face 24 Inlet 25 Outlet 26 Spreading area 27 Aging area 31 Wastewater reservoir 32 Outlet 41 Stirring device 42 Screw 42a Rotating shaft 42b Blade 43 Support pin 45 Moving device 46 Longitudinal moving device 47 Widthwise moving device 51 Longitudinal sewage channel 51a Longitudinal sewage channel 52 Widthwise sewage channel 53 Recovery tank 54 Pump 55 Pipe 61 Suction pipe 62 Suction pump 63 Supply pipe 81 Air blowing hole 91 Separator 92 Septic tank 93 Dehydrator 94 Composting machine 100 Sewage treatment device 421 Motor 422 Decelerator 461 Wheel 462 Frame 463 Motor 464 Work table 465 Control panel 471 Arch frame 472 Wheel 473 Frame 474 Frame moving device A air C compost M mixture H wastewater H1 solids

Claims (5)

処理槽に堆積させた水分調整材に家畜などから出る固形物を含む汚水を散布し、水分調整材と汚水を攪拌手段で攪拌するとともに、処理槽の下部に溜まる汚水を回収して処理槽内に散布する汚水処理方法であって、上記処理槽を、汚水を散布しながら攪拌する散布領域と汚水を散布せずに攪拌し乾燥を伴った発酵を熟成する熟成領域とに分け、攪拌手段は水分調整材と汚水との混合物を移送可能な移送機能を備え、上記混合物を所定の速度で散布領域側から熟成領域側へ攪拌しながら移送して発酵させ堆肥を製造することを特徴とする汚水処理方法Sprinkle sewage containing solids from livestock etc. on the water conditioner deposited in the treatment tank, stir the moisture conditioner and sewage with stirring means, and collect the sewage collected at the bottom of the treatment tank The sewage treatment method is to divide the treatment tank into a sprinkling region that stirs while sprinkling sewage and a ripening region that stirs without sprinkling sewage and matures fermentation with drying, and the stirring means is A sewage having a transfer function capable of transferring a mixture of a moisture adjusting material and sewage, and fermenting the mixture while stirring from the spraying area side to the aging area side at a predetermined speed to produce compost Processing method . 請求項記載の汚水処理方法において、攪拌手段は、1本または複数本のスクリューを備え、スクリューを回転させるとともに処理槽内を移動させて攪拌を行うことを特徴とする汚水処理方法。2. The sewage treatment method according to claim 1, wherein the stirring means includes one or a plurality of screws, and the stirring is performed by rotating the screw and moving the inside of the treatment tank. 水分調整材を堆積させる処理槽と、家畜などから出る固形物を含む汚水を散布する散布装置と、水分調整材と汚水を攪拌する攪拌手段と、処理槽の下部に溜まる水分を回収する回収手段と、回収した汚水を再び上記散布装置に供給する供給手段を備え、処理槽を、汚水を散布しながら攪拌する散布領域と汚水を散布せずに攪拌し乾燥を伴った発酵を熟成する熟成領域とに分け、上記攪拌手段が、水分調整材と汚水との混合物を所定の速度で散布領域側から熟成領域側へ攪拌しながら移送可能な移送機能を備えてなる汚水処理装置。A processing tank for depositing moisture adjusting material, a spraying device for spraying sewage containing solid matter from livestock, etc., a stirring means for stirring the moisture adjusting material and sewage, and a collecting means for recovering water accumulated in the lower part of the processing tank And supply means for supplying the recovered sewage to the spraying device again, and a ripening region in which the treatment tank is stirred while spraying the sewage, and a ripening region in which stirring is performed without spraying the sewage and the fermentation is matured. The sewage treatment apparatus in which the agitation means has a transfer function capable of transferring the mixture of the moisture adjusting material and the sewage at a predetermined speed while stirring the mixture from the spraying area side to the aging area side . 請求項記載の汚水処理装置において、攪拌手段は、1本または複数本のスクリューを備え、処理槽の上方に移動可能に吊持されていることを特徴とする汚水処理装置。4. The sewage treatment apparatus according to claim 3, wherein the agitation unit includes one or a plurality of screws and is suspended above the treatment tank so as to be movable. 請求項3又は4記載の汚水処理装置において、回収手段は、処理槽の底面に設けられる複数の汚水路と、複数の汚水路内の汚水をまとめる回収槽とからなることを特徴とする汚水処理装置。5. The sewage treatment apparatus according to claim 3, wherein the recovery means comprises a plurality of sewage channels provided on the bottom surface of the treatment tank and a recovery tank that collects the sewage in the plurality of sewage channels. apparatus.
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Publication number Priority date Publication date Assignee Title
KR101408207B1 (en) 2013-12-10 2014-06-16 농업회사법인 주식회사 태초의 자연으로 Mixer for waste organic matter

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JP2007008755A (en) * 2005-06-30 2007-01-18 Fujiki:Kk Compost production equipment
CN104150731B (en) * 2014-08-20 2016-03-30 武汉理工大学 A kind of method realizing heavy metals in city sewage sludge stabilization that biochemical-physical combines
JP6039834B1 (en) * 2016-01-22 2016-12-07 愛和産業株式会社 Organic fuel and composting equipment

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Publication number Priority date Publication date Assignee Title
KR101408207B1 (en) 2013-12-10 2014-06-16 농업회사법인 주식회사 태초의 자연으로 Mixer for waste organic matter

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