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JP4180722B2 - Waste water treatment method and waste water treatment equipment - Google Patents
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JP4180722B2 - Waste water treatment method and waste water treatment equipment - Google Patents

Waste water treatment method and waste water treatment equipment Download PDF

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JP4180722B2
JP4180722B2 JP05495299A JP5495299A JP4180722B2 JP 4180722 B2 JP4180722 B2 JP 4180722B2 JP 05495299 A JP05495299 A JP 05495299A JP 5495299 A JP5495299 A JP 5495299A JP 4180722 B2 JP4180722 B2 JP 4180722B2
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freezing
freeze
tank
concentrated sludge
ice
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JPH11319892A (en
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潤二 松田
誠 佐野
浩 佐藤
克己 藤間
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Mayekawa Manufacturing Co
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Mayekawa Manufacturing Co
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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
    • Y02EREDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
    • Y02E50/00Technologies for the production of fuel of non-fossil origin
    • Y02E50/30Fuel from waste, e.g. synthetic alcohol or diesel

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Description

【0001】
【発明の属する技術分野】
本発明は、生ゴミ等を含む生活排水の処理方法および装置に関し、詳しくは、排水を濃縮した濃縮汚泥を凍結脱水して脱水ケーキ状とした後固形燃料とする新規な排水処理方法および排水処理装置、および生ゴミの凍結乾燥により資源化を図る省エネ、無公害の生ゴミの排水処理装置に関する。
【0002】
【従来の技術】
一般に、下水汚泥処理の前処理として、脱水と予備乾燥が行われている。脱水は、真空脱水機、スクリュープレス脱水機、遠心脱水機等の機械的脱水機が用いられる。このような、機械的脱水で得られた脱水ケーキの含水率には限度があるため、含水率の低減をはかるために乾燥機を持つ乾燥工程を施して乾燥ケーキとしている。従来の乾燥機は、脱水ケーキを加熱して水分を蒸発させる加熱方式のものである。乾燥工程を経て得られた乾燥ケーキを焼却炉に送り、焼却処理を行っている。
【0003】
【発明が解決しようとする課題】
従来の加熱方式による乾燥法は、多量のエネルギーを消費すると共に、乾燥ケーキを焼却炉で焼却処理するため、ダイオキシンや臭い等の公害発生の要因となっている。
また、排水から分離した汚泥ケーキ状物を海洋、陸上等で埋め立てに利用して廃棄する方法も採用されているが、この方法も汚泥ケーキの生成に多量のエネルギーを消費するばかりでなく、埋め立て地まで輸送するのに莫大なエネルギーを消費するという問題がある。
【0004】
また、生ゴミの処理においても、従来は水分を多量に含んだ状態で焼却場で処理するか、そのまま埋め立て廃棄されていた。そのため、多量の水分を含んだままで所定処理地域までの輸送には多大の輸送エネルギとCO2 の発生を余儀なくさせられ、また搬送生ゴミの乾燥には含有水分の蒸発に多大のエネルギの消費と異臭等を含む環境汚染ガスを発生する問題がある。
【0005】
本発明は上述の点に着目してなされたもので、凍結脱水法により汚泥の水分を効率良く除去すると共に、最後に固形燃料化してエネルギー資源として再利用を可能にした排水処理方法および排水処理装置の提供と、低エネルギで水の相変化を起こさせて分離できる省エネ、無公害型の生ゴミの排水処理装置の提供を目的としたものである。
【0006】
【課題を解決するための手段】
かかる課題を解決するために、請求項1記載の発明は、固形物を含む排水から汚泥を分離して汚泥ケーキ状として処理する排水処理方法において、
前記排水を沈殿槽に送って濃縮汚泥を生成する工程と、この濃縮汚泥を凍結乾燥して水分と固形物とを分離する工程と、該凍結脱水工程で生成された乾燥ケーキ状物を脱水して脱水ケーキを生成する工程と、前記脱水ケーキを固形化して固形燃料化物を生成する工程とからなり、前記沈殿槽で分離された上澄み排水を排水凍結分離装置の製氷機に送って清澄な氷と濃縮された排水とに分離し、その氷を蓄熱槽で溶解して得られた水を中水として利用することを特徴とする。
【0007】
排水から得られた濃縮汚泥を、その保有水が氷柱結晶化し、繊維層を破壊するような結晶成長をするように凍結し、その後融解解凍して濃縮汚泥中の生ゴミ等の保有水をドリップ除去した後乾燥させる。
上記操作により、含水率が極めて低い乾燥ケーキ状物が得られる。この乾燥ケーキ状物を脱水して脱水ケーキとし、これを固形燃料化物としてエネルギー資源として再利用が可能となる。
【0008】
【0009】
前記濃縮汚泥を凍結乾燥して水分と固形物とを分離する凍結脱水工程は、凍結・解凍を繰り返し行い、前記濃縮汚よりの脱水を十分に行なうようにしても良い。
【0010】
また、請求項記載の発明は、初期沈殿槽と最終沈殿槽からなる排水の沈殿槽と、該初期沈殿槽で得られた濃縮汚泥を貯留する濃縮汚泥タンクと、該濃縮汚泥タンクからの濃縮汚泥を凍結脱水して水分と固形物とを分離して乾燥ケーキ状物を生成する凍結脱水装置と、該乾燥ケーキ状物を脱水して脱水ケーキを生成する遠心分離機と、該脱水ケーキを固形燃料化するペレット化装置と、前記最終沈殿槽で得られた上澄み排水を中水化処理する排水凍結分離装置と、を具え、前記排水凍結分離装置は、冷凍機、製氷機及び蓄熱槽を有し 、最終沈殿槽よりの上澄み排水を前記製氷機に送られて凍結することにより、清澄な水分(氷)と濃縮された排水に分離され、その氷は前記蓄熱槽に送られると共に、濃縮排水は熱交換機を通して初期沈殿槽に返送されるように構成したことを特徴とする。
【0011】
前記凍結脱水装置は、ヒートポンプに接続された蒸発器が設置された冷凍室と、前記ヒートポンプに接続された凝縮器が設置された融解室と、前記濃縮汚泥を載せて前記冷凍室から融解室に移送するターンテーブルと、からなる構成のものが使用される。
【0012】
そして、上記凍結脱水装置は、微細な生ゴミを含む前記濃縮汚泥を前記ターンテーブルの間歇運転により凍結・解凍の繰り返し操作を可能にする構成としても良い。
【0013】
た、粉砕した生ゴミを低温緩慢凍結することにより、生成氷結晶により細胞の組織構造にメカニカル破壊を直接与え、その結果細胞膜の破壊、細胞内保有水の細胞外移行を惹起させ、ついで行なう解凍操作と機械的脱水の組合せによりより効率的に脱水させ、生ゴミの排水乾燥が行なわれる。
【0014】
記生ゴミの排水に際しては、生ゴミを粉砕した状態で低温緩慢凍結するため、生ゴミは細胞外凍結状態におかれ、組織内の細胞間隙には氷結晶を生成成長させ、細胞の組織構造にメカニカル破壊を直接与えることになり、細胞膜は破壊され細胞内の保有水は細胞外へ移行させる。
そのため、解凍融解して旧状態に復帰させても細胞膜は破壊されているため、前記保有水も細胞内に復帰されないため、ついで行なわれる機械的脱水により効率的に脱水することができる。
【0015】
た、上記低温緩慢凍結は略5℃以下の低温で行なうようにし、細胞外に大きな氷晶形成を可能にして、細胞が修復不可能な機械的破壊を受けるようにしたものである。
【0016】
た、凍結・解凍は繰り返し複数回行うことにより、より完全な脱水を行なうようにしても良い。
た、凍結解凍の後段に冷風乾燥により乾燥効果を上げるようにしても良い。
【0017】
そこで生ゴミの排水処理装置は、生ゴミ粉砕機と、粉砕した生ゴミを穴明き受け板上に散布する可動式散布機と、前記穴明け受け板とその上に散布した粉砕生ゴミに凍結・解凍・冷風乾燥の熱処理をして脱水させる押圧ローラとを内蔵する凍結乾燥室と、凍結・解凍・冷風用の熱源を形成する冷凍サイクルと、前記受け板の下部に設けた脱水タンクと、より構成したことを特徴とする。
【0018】
記生ゴミの排水処理装置の凍結乾燥室は、少なくとも二つ以上設ける構成とし、冷凍サイクルよりの熱の切り替え供給により、凍結・解凍・脱水の操作を交互に複数回行なう構成としても良い。
【0019】
【発明の実施の形態】
以下に図面を参照して本発明の実施の形態を例示的に説明する。ただし、この実施の形態に記載されている構造部品の寸法、材質、形状、相対位置などは特に特定的な記載がない限りは、この発明の範囲をそれのみに限定する趣旨ではなく、
単なる説明例に過ぎない。
図1は本発明の排水処理装置の一実施の形態を示す系統図であり、図2は図1の要部模式図であり、図3は図1の凍結脱水装置の一例を示す説明図であり、図4は本発明の生ゴミの排水処理装置の概略の構成を示す模式図である。
【0020】
図1および図2において、住宅地区1から出る生活排水2は管路3を介して廃棄物資源化装置4に送られる。廃棄物資源化装置4は、初期沈殿槽5、最終沈殿槽6、ばっ気槽7、濃縮汚泥タンク8、凍結脱水装置9、遠心分離機10、およびペレット化装置11を備えている。
排水2は初期沈殿槽5に送られ、ここで沈殿した濃縮汚泥は濃縮汚泥タンク8に送られると共に、上澄み排水はばっ気槽7に送られてばっ気されてその上澄み排水が最終沈殿槽6に送られる。最終沈殿槽6で沈殿した濃縮汚泥も濃縮汚泥タンク8に送られると共に、その上澄み排水は排水凍結分離装置25に送られて中水化される(後述する)。
【0021】
濃縮汚泥タンク8で濃縮された濃縮汚泥は凍結脱水装置9に送られて凍結脱水される。
凍結脱水法は種々の方式が知られているが、本発明においては、濃縮汚泥を冷凍機で凍結(濃縮汚泥の保有水が氷柱結晶化し、繊維層を破壊するような結晶成長をする凍結方法)し、その後融解して濃縮汚泥中の生ゴミ等の保有水をドリップ除去した後乾燥させる装置を使用する。必要に応じて上記操作を数回繰り返す。
【0022】
凍結脱水装置9で凍結脱水されて水分が50%以下、好ましくは含水率20%程度にまで除去された乾燥ケーキ状の被乾燥物は遠心分離機10に送られる。遠心分離機10に凝集剤37を送り込み、乾燥ケーキ状物と共に攪拌することにより、脱水された固形の脱水ケーキが生成される。この脱水ケーキがペレット化装置11に送られる。ペレット化装置11には、石灰供給タンク36からの石灰が供給され、ピット35からの可燃ゴミ、ゴム、プラスチック等の廃棄物と共に脱水ケーキが固形化されて固形燃料化物(RDF)12が生成される。
【0023】
なお、遠心分離機10で分離された分離排水は、管路38を介して再び初期沈殿槽5に送られて上記動作を繰り返す。
なお、凍結脱水法は、一般には被乾燥物を凍結した状態で水分を昇華させて除去し乾燥する方式であって、種々の方式が開発されており、本発明においては周知の凍結脱水法を使用してよい。
【0024】
図3に、本発明で使用する凍結脱水装置の一例を示している。冷凍室14と融解室15とを備えた容器16内に、駆動装置17により間欠回転するターンテーブル18を設けている。冷凍室14にはヒートポンプ19に接続された蒸発器20を、融解室15にはヒートポンプ19に接続された凝縮器21を各々設置している。
【0025】
ターンテーブル18には前記濃縮汚泥タンク8からの濃縮汚泥13が送られ、蒸発器20が熱を吸収して濃縮汚泥13を冷凍した後、ターンテーブル18の回転で融解室15に移送する。ヒートポンプ19は冷凍室14における熱源から熱を得て凝縮器21により融解室15で熱放散し、送られてきた冷凍濃縮汚泥を融解することにより、水分がドリップ除去される。このドリップは分離排水として初期沈殿槽5に送られる。
【0026】
凍結脱水された乾燥ケーキ物は管路22から遠心分離機10に送られ、前述のようにここで完全に脱水されて脱水ケーキとした後、ペレット化装置11に送られ、ペレット化装置11において固形化されて固形燃料化物(RDF)12を得る。
【0027】
最終沈殿槽6で得られた上澄み排水は排水凍結分離装置25に送られて中水化処理される。すなわち、排水凍結分離装置25は、冷凍機26および製氷機27を有し、上澄み排水(微小な固形成分を含む)はこの製氷機27に送られて凍結することにより、清澄な水分(氷)と濃縮された排水に分離され、その氷は蓄熱槽28に送られると共に、濃縮排水は熱交換機32を通して初期沈殿槽5に返送される。
【0028】
蓄熱槽28で溶解された氷は中水29となって貯水され、この中水29は住宅地区1に送られてそのまま中水として利用され、あるいは公園30に送られて植物用散水等に利用された後河川に放流される。また、浄水化装置31を通すことで浄水として住宅地区1で利用することもできる。
【0029】
蓄熱槽28の氷水は熱交換機33に送られる。熱交換機32、33で冷却されたエアは住宅地区1や工場、ショッピングモール34等の冷房に利用される。
一般に固形物の水分の含水率を50%以下に減じるには、その固形物がもつ細胞内で保有するような水分をも取り出す必要がある。凍結脱水法でこの水分除去を行う場合、細胞内に内在する水分を凍結により大きな単結晶化された氷とし、これを融解することにより上記50%以下の含水率を得ることができる。
【0030】
〔実験例〕
14.340m3(含水率99%=14.197m3)の濃縮汚泥を凍結脱水装置9に入れて凍結脱水することにより、上記水分を凍結させた後融解し、この融解した水分14.161m3を返送水として前記初期沈殿槽5に返送した。得られた乾燥ケーキ状物は、0.179m3(含水率20%=0.036m3)であった。これに要した消費電力量は47kw×10時間であった。したがって、ランニングコストは、47kw×10時間×5円=2,370〔円/1日〕であった。
【0031】
〔比較例〕
同じく、14.340m3(含水率99%=14.197m3)の濃縮汚泥を加熱蒸発乾燥装置に入れて加熱乾燥した。乾燥を行う熱源は蒸気を用い、燃料は都市ガス(料金=40円/Nm3)を使用した。同じく分離水は14.161m3で、0.179m3(含水率20%=0.036m3)の乾燥ケーキ状物を得た。これに要したガス消費量は878Nm3であった。したがって、ランニングコストは、878Nm3×40円=35,120〔円/1日〕であった。
【0032】
上記の実験例および比較例で明らかなように、本発明の凍結脱水法は、従来の加熱蒸発乾燥法に比して乾燥に要するエネルギーが少なく、ランニングコストが大幅に安くなっている。また、臭いがドリップに閉じ込められ、従来の加熱方式のように生ゴミの臭いが出ないため衛生的である。
【0033】
図4には、本発明の生ゴミの排水処理装置の概略の構成を示してある。図において、30a、30bは生ゴミの凍結処理、解凍処理を交互に行なう熱処理室で、内部にはそれぞれ粉砕機38により粉砕生ゴミ39をパンチプレート32、32上に散布する左右横行可能のフィーダ31、31と、散布された粉砕生ゴミに対し凍結ないし解凍ないし冷風熱源を形成する熱交換器35a、35bと、該熱交換器に蒸発潜熱ないし凝縮熱を送るヒートポンプ等の冷凍サイクル36と、解凍した粉砕生ゴミを前記パンチプレート上に押圧して脱水させる上下動及び左右横行可能の押圧ローラ34、34と、脱水した粉砕ゴミをパンチプレートより外部に取り出す掻き出し機33、33と、脱水タンク37、37等を含む構成とする。
なお、上記冷凍サイクル36に内蔵する蒸発器と凝縮器は前記熱交換器35a、35bに交互に切り替え接続させ、例えば熱処理室30aを凍結に使用し熱処理室30bを解凍に使用するときは熱交換器35aを蒸発器に接続させ熱交換器35bには凝縮器に接続させるようにしてある。
なお、上記熱処理室35a、35bを凍結処理に使用する場合は室温を略5℃以下の低温に保持して低温下の緩慢凍結を起こすようにしてある。
【0034】
上記構成であるので、粉砕状の生ゴミ39はフィーダ31を介して例えば熱処理室30a内のパンチプレート32上に散布後、熱交換器35aにより冷凍サイクル36より冷熱を供給すれば、室内温度は略5℃以下の低温に保持され、その結果パンチプレート32上に散布された粉砕状生ゴミ39は緩慢凍結の状態に置かれる。即ち、粉砕生ゴミは細胞外凍結を起こし、細胞間隙には大きな氷結晶を生成成長させ、その結果細胞組織は修復不可能の機械的破壊を直接受け細胞膜は破壊され、細胞内の保有水は細胞外に移行する。
ついで前記熱交換器35aに冷凍サイクル36より凝縮熱を供給すれば、前記凍結生ゴミは解凍されるが、前記細胞外に移行した保有水は細胞膜が破壊されているため、機械的絞り機構である押圧ローラ34の加圧力と相俟って、パンチプレート32のパンチング穴32aを介して脱水タンクに貯留される。
斯くして、低エネルギで水の相変化を起こさせ、無公害型の脱水を可能とし、多目的の資源化を可能にしている。
【0035】
なお、凍結・解凍のみでは十分な脱水が期待出来ない場合は凍結・解凍脱水の回数を複数回繰り返し行なうようにし、必要があれば最後の仕上げに冷風乾燥をさせる。
【0036】
【発明の効果】
以上の記載のように、本発明によれば、排水から得られた濃縮汚泥の固形物を凍結脱水することにより、固形物がもつ細胞内で保有するような水分を凍結により単結晶化された氷とし、これを融解することで含水率が極めて低い乾燥ケーキが得られる。凍結脱水に要する電気料は、従来の加熱蒸発方式の熱源に要する燃料費に比してはるかに少なくてすみ、ランニングコストを低減できる。
【0037】
また、乾燥ケーキを脱水して脱水ケーキとし、これを固形燃料化することにより、エネルギー資源として再利用が可能となるばかりでなく、焼却処理しないため、ダイオキシンや臭い等の公害発生を抑制できる。
【0038】
上記本発明の生ゴミの排水処理により、低エネルギのもとに、無公害型の効率的脱水を可能とするとともに多目的の資源化を図ることができる。
【図面の簡単な説明】
【図1】 本発明の排水処理装置の一実施の形態を示す系統図である。
【図2】 図1の要部を模式図である。
【図3】 図1の凍結脱水装置の一例を示す説明図である。
【図4】 本発明における生ゴミ排水処理装置の概略構成を示す模式図である。
【符号の説明】
2 排水
5 沈殿槽(初期沈殿槽)
6 沈殿槽(最終沈殿槽)
8 濃縮汚泥タンク
9 凍結脱水装置
11 ペレット化装置
12 固形燃料化物
14 冷凍室
15 融解室
18 ターンテーブル
19 ヒートポンプ
20 蒸発器
21 凝縮器
25 排水凍結分離装置
27 製氷機
28 蓄熱槽
30a、30b 熱処理室
31 フィーダ
32 パンチプレート
33 掻き出し機
34 押圧ローラ
35a、35b 熱交換器
36 冷凍サイクル
37 脱水タンク
38 粉砕機
39 粉砕生ゴミ
[0001]
BACKGROUND OF THE INVENTION
TECHNICAL FIELD The present invention relates to a method and apparatus for treating domestic wastewater including raw garbage, and more specifically, a novel wastewater treatment method and wastewater treatment in which concentrated sludge obtained by concentrating wastewater is freeze-dehydrated to form a dehydrated cake and then used as a solid fuel. device, and garbage by lyophilization achieve recycling energy saving relates to wastewater treatment apparatus of garbage pollution-free.
[0002]
[Prior art]
Generally, dehydration and pre-drying are performed as pretreatment for sewage sludge treatment. For the dehydration, a mechanical dehydrator such as a vacuum dehydrator, a screw press dehydrator, or a centrifugal dehydrator is used. Since the moisture content of the dehydrated cake obtained by such mechanical dehydration is limited, in order to reduce the moisture content, a drying process having a dryer is performed to obtain a dried cake. A conventional dryer is of a heating system that heats a dehydrated cake to evaporate moisture. The dried cake obtained through the drying process is sent to an incinerator for incineration.
[0003]
[Problems to be solved by the invention]
A conventional drying method using a heating method consumes a large amount of energy and incinerates the dried cake in an incinerator, which causes pollution such as dioxins and odors.
In addition, a method is also adopted in which sludge cakes separated from wastewater are used for landfill on the ocean, land, etc., but this method not only consumes a lot of energy to produce sludge cake, but also landfill. There is a problem that enormous energy is consumed for transportation to the ground.
[0004]
Also, in the treatment of raw garbage, conventionally, it is treated in an incinerator with a large amount of moisture, or disposed as landfill. Therefore, a great deal of energy and CO2 are generated for transportation to a predetermined treatment area while containing a large amount of water. There is a problem of generating environmental pollutant gases including the like.
[0005]
The present invention has been made paying attention to the above points, and efficiently removes water from sludge by freeze dehydration, and finally makes it a solid fuel that can be reused as an energy resource. and providing a device, in which energy saving can be separated by causing a phase change of water at low energy, to provide a wastewater treatment apparatus of garbage pollution-free type for the purpose.
[0006]
[Means for Solving the Problems]
In order to solve this problem, the invention according to claim 1 is a wastewater treatment method for separating sludge from wastewater containing solids and treating it as a sludge cake.
The step of sending the waste water to a sedimentation tank to produce concentrated sludge, the step of freeze-drying the concentrated sludge to separate water and solids, and the dewatering of the dried cake produced in the freeze-dehydration step generating a dehydrated cake Te, the dehydrated cake was solidified Ri Do and a step of generating a solid fuel product, clarified supernatant drainage separated in the previous SL sedimentation tank is sent to ice machine drainage freezing separator It is characterized in that water obtained by separating the ice into concentrated water and concentrated waste water and dissolving the ice in a heat storage tank is used as intermediate water.
[0007]
The concentrated sludge obtained from the drainage is frozen so that the retained water crystallizes into icicles and destroys the fiber layer, and then thawed and thawed to drip the retained water such as raw garbage in the concentrated sludge. Remove and dry.
By the above operation, a dried cake-like product having an extremely low moisture content is obtained. The dried cake can be dehydrated to obtain a dehydrated cake, which can be reused as an energy resource as a solid fuel.
[0008]
[0009]
In the freeze dehydration step in which the concentrated sludge is lyophilized to separate moisture and solids, the freeze and thaw may be repeated to sufficiently dehydrate the concentrated sludge.
[0010]
The invention of claim 3, wherein the initial settling tank and a sedimentation tank consisting final sedimentation tank effluent, and the concentrated sludge tank for storing concentrated sludge obtained in the initial precipitation tank, concentrated from the concentrated sludge tank Freezing and dehydrating sludge to separate moisture and solids to produce a dried cake, a freeze dehydrating device, a centrifuge for dehydrating the dried cake to produce a dehydrated cake, and the dehydrated cake A pelletizing device for converting to solid fuel; and a drainage freezing and separating device for neutralizing the supernatant wastewater obtained in the final settling tank. The drainage freezing and separating device includes a refrigerator, an ice making machine, and a heat storage tank. has, by freezing the supernatant waste water from the final sedimentation tank is sent to the ice machine, it is separated into concentrated and clear water (ice) drainage, with its ice is sent to the heat storage tank, concentrated Wastewater is passed through the heat exchanger to the initial settling tank Characterized by being configured to be sent.
[0011]
The freeze dehydration apparatus includes a freezing chamber in which an evaporator connected to a heat pump is installed, a melting chamber in which a condenser connected to the heat pump is installed, and the concentrated sludge placed on the freezing chamber from the freezing chamber to the melting chamber. The thing of the structure which consists of a turntable to transfer is used.
[0012]
And the said freeze dehydration apparatus is good also as a structure which enables freezing and thawing | decompression operation of the said concentrated sludge containing fine garbage by intermittent operation of the said turntable.
[0013]
Also, by the garbage that pulverizng a low temperature slow freezing provides a mechanical destruction by generating ice crystals in tissue structures directly with the cell, resulting disruption of the cell membrane, to induce extracellular migration of intracellular held water, followed By the combination of the thawing operation and mechanical dehydration performed, the wastewater is more efficiently dehydrated and the garbage is drained and dried .
[0014]
In wastewater upper Kisei dust, to a low temperature slow freezing while pulverizing the garbage, garbage is placed in extracellular freezing conditions, the cell gap in the organization to produce growth of ice crystals, cells of the tissue Mechanical destruction is directly applied to the structure, the cell membrane is destroyed, and the water retained in the cell is transferred out of the cell.
Therefore, since the cell membrane is destroyed even after being thawed and thawed and returned to the old state, the retained water is not returned to the cell, so that it can be efficiently dehydrated by the subsequent mechanical dehydration.
[0015]
Also, the upper Symbol cold slow freezing to perform substantially 5 ° C. in the following low temperature, thereby enabling large ice crystals formed out of the cells, in which cells to receive unrepairable mechanical disruption.
[0016]
Also, by performing freezing and thawing is repeated a plurality of times, it is also possible to perform a more complete dehydration.
Also, by cold air drying in the subsequent stage of freezing thawing but it may also be to raise the drying effect.
[0017]
Therefore, the wastewater treatment equipment for garbage is composed of a garbage crusher, a movable spreader that spreads the crushed garbage on a perforated receiving plate, and the perforated receiving plate and the crushed garbage that is sprinkled on the perforated receiving plate. A freeze-drying chamber containing a pressure roller that dehydrates by heat treatment of freezing, thawing, and cold air drying; a refrigeration cycle that forms a heat source for freezing, thawing, and cold air; and a dehydration tank provided below the receiving plate It is characterized by comprising more.
[0018]
Freeze drying chamber for the waste water treatment apparatus of the above Kisei garbage, a configuration of providing at least two, by switching the supply of heat from the refrigeration cycle may be alternately performed a plurality of times constituting the operation of freezing and thawing and dehydration.
[0019]
DETAILED DESCRIPTION OF THE INVENTION
Embodiments of the present invention will be exemplarily described below with reference to the drawings. However, the dimensions, materials, shapes, relative positions, etc. of the structural parts described in this embodiment are not intended to limit the scope of the present invention only to those unless otherwise specified.
It is just an illustrative example.
FIG. 1 is a system diagram showing an embodiment of the waste water treatment apparatus of the present invention, FIG. 2 is a schematic diagram of a main part of FIG. 1, and FIG. 3 is an explanatory diagram showing an example of the freeze dehydration apparatus of FIG. FIG. 4 is a schematic diagram showing a schematic configuration of the wastewater wastewater treatment apparatus of the present invention.
[0020]
In FIG. 1 and FIG. 2, the domestic wastewater 2 coming out of the residential area 1 is sent to the waste resource recycling apparatus 4 through the pipeline 3. The waste resource recycling apparatus 4 includes an initial sedimentation tank 5, a final sedimentation tank 6, an aeration tank 7, a concentrated sludge tank 8, a freeze dehydration apparatus 9, a centrifuge 10, and a pelletization apparatus 11.
The waste water 2 is sent to the initial sedimentation tank 5, and the concentrated sludge settled here is sent to the concentrated sludge tank 8, and the supernatant waste water is sent to the aeration tank 7 and aerated, and the supernatant waste water is the final sedimentation tank 6. Sent to. The concentrated sludge precipitated in the final sedimentation tank 6 is also sent to the concentrated sludge tank 8, and the supernatant drainage is sent to the drainage freezing and separating device 25 to be hydrated (described later).
[0021]
The concentrated sludge concentrated in the concentrated sludge tank 8 is sent to the freeze dehydration apparatus 9 for freeze dehydration.
Various methods are known for the freeze dehydration method. In the present invention, the concentrated sludge is frozen with a freezer (the freezing method in which the water retained in the concentrated sludge is crystallized into ice columns and crystal growth is performed to destroy the fiber layer). ), And then melted and drip-removed the retained water such as raw garbage in the concentrated sludge, followed by drying. Repeat the above operation several times as necessary.
[0022]
The dried cake-like material to be dried, which has been freeze-dehydrated by the freeze-dehydration apparatus 9 and removed to a moisture content of 50% or less, preferably about 20%, is sent to the centrifuge 10. The flocculant 37 is fed into the centrifuge 10 and stirred together with the dried cake to produce a dehydrated solid dehydrated cake. This dehydrated cake is sent to the pelletizing apparatus 11. The pelletizing apparatus 11 is supplied with lime from the lime supply tank 36, and dehydrated cake is solidified together with waste such as combustible garbage, rubber, plastic, etc. from the pit 35 to produce a solid fuel product (RDF) 12. The
[0023]
The separated waste water separated by the centrifugal separator 10 is sent again to the initial settling tank 5 through the pipe line 38 and the above operation is repeated.
The freeze dehydration method is generally a method in which moisture is sublimated and removed and dried in a frozen state, and various methods have been developed. In the present invention, a well-known freeze dehydration method is used. May be used.
[0024]
FIG. 3 shows an example of a freeze dehydration apparatus used in the present invention. A turntable 18 that is intermittently rotated by a driving device 17 is provided in a container 16 having a freezing chamber 14 and a melting chamber 15. An evaporator 20 connected to a heat pump 19 is installed in the freezer compartment 14, and a condenser 21 connected to the heat pump 19 is installed in the melting chamber 15.
[0025]
The concentrated sludge 13 from the concentrated sludge tank 8 is sent to the turntable 18, and after the evaporator 20 absorbs heat and freezes the concentrated sludge 13, it is transferred to the melting chamber 15 by the rotation of the turntable 18. The heat pump 19 obtains heat from a heat source in the freezer compartment 14 and dissipates heat in the melting chamber 15 by the condenser 21, and melts the sent frozen concentrated sludge to remove drip. This drip is sent to the initial settling tank 5 as separated waste water.
[0026]
The dried cake that has been freeze-dehydrated is sent to the centrifuge 10 from the pipe line 22 and is completely dehydrated here to form a dehydrated cake as described above, and then sent to the pelletizing device 11 where it is sent to the pelletizing device 11. Solidified fuel product (RDF) 12 is obtained by solidification.
[0027]
The supernatant wastewater obtained in the final sedimentation tank 6 is sent to the drainage freeze separator 25 and subjected to the middle water treatment. That is, the drainage freezing / separating apparatus 25 has a refrigerator 26 and an ice making machine 27, and the supernatant drainage (including minute solid components) is sent to the ice making machine 27 and frozen, thereby clear water (ice). The ice is sent to the heat storage tank 28, and the concentrated waste water is returned to the initial settling tank 5 through the heat exchanger 32.
[0028]
The ice melted in the heat storage tank 28 is stored as intermediate water 29, and the intermediate water 29 is sent to the residential area 1 and used as it is, or sent to the park 30 for watering plants. And then released into the river. Moreover, it can also utilize in the residential area 1 as purified water by letting the water purification apparatus 31 pass.
[0029]
The ice water in the heat storage tank 28 is sent to the heat exchanger 33. The air cooled by the heat exchangers 32 and 33 is used for cooling the residential district 1, the factory, the shopping mall 34, and the like.
In general, in order to reduce the moisture content of a solid substance to 50% or less, it is necessary to take out the moisture contained in the cells of the solid substance. When this water removal is performed by the freeze dehydration method, the moisture content in the cells is converted into large single crystal ice by freezing, and the water content of 50% or less can be obtained by thawing the ice.
[0030]
[Experimental example]
A concentrated sludge having a moisture content of 14.340 m 3 (water content 99% = 14.197 m 3 ) is placed in the freeze dehydration apparatus 9 and freeze-dehydrated to freeze and thaw the moisture, and the melted moisture 14.161 m 3 Was returned to the initial settling tank 5 as return water. The obtained dried cake-like product was 0.179 m 3 (water content 20% = 0.036 m 3 ). The power consumption required for this was 47 kw × 10 hours. Therefore, the running cost was 47 kW × 10 hours × 5 yen = 2,370 [yen / day].
[0031]
[Comparative Example]
Similarly, 14.340 m 3 (water content 99% = 14.197 m 3 ) of concentrated sludge was placed in a heating evaporation drying apparatus and dried by heating. Steam was used as the heat source for drying, and city gas (rate = 40 yen / Nm 3 ) was used as the fuel. Similarly, the separated water was 14.161 m 3 , and a dried cake of 0.179 m 3 (water content 20% = 0.036 m 3 ) was obtained. The gas consumption required for this was 878 Nm 3 . Therefore, the running cost was 878 Nm 3 × 40 yen = 35,120 [yen / day].
[0032]
As is clear from the above experimental examples and comparative examples, the freeze dehydration method of the present invention requires less energy for drying than the conventional heat evaporation drying method, and the running cost is significantly reduced. Moreover, since the odor is confined in the drip and the odor of garbage is not produced unlike the conventional heating method, it is hygienic.
[0033]
FIG. 4 shows the schematic configuration of the wastewater treatment apparatus for garbage of the present invention. In the figure, reference numerals 30a and 30b denote heat treatment chambers for alternately performing the freezing and thawing processes of the garbage, and inside the feeders, which are capable of traversing the left and right traversing the crushed garbage 39 on the punch plates 32 and 32 by the crusher 38, respectively. 31, 31, heat exchangers 35 a and 35 b that form a freezing or thawing or cold air heat source for the dispersed ground garbage, a refrigeration cycle 36 such as a heat pump that sends latent heat of vaporization or heat of condensation to the heat exchanger, Press rollers 34, 34 that can dehydrate the crushed raw garbage by pressing it onto the punch plate, can be moved up and down and left and right, scrapers 33, 33 for taking out the dehydrated crushed garbage to the outside from the punch plate, and a dehydration tank 37, 37, etc.
The evaporator and the condenser built in the refrigeration cycle 36 are alternately connected to the heat exchangers 35a and 35b. For example, when the heat treatment chamber 30a is used for freezing and the heat treatment chamber 30b is used for thawing, heat exchange is performed. The condenser 35a is connected to the evaporator, and the heat exchanger 35b is connected to the condenser.
When the heat treatment chambers 35a and 35b are used for freezing, the room temperature is kept at a low temperature of about 5 ° C. or lower to cause slow freezing at a low temperature.
[0034]
Since it is the said structure, if the crushed garbage 39 is spread | dispersed on the punch plate 32 in the heat processing chamber 30a through the feeder 31, for example, if cold heat is supplied from the freezing cycle 36 with the heat exchanger 35a, indoor temperature will be The ground garbage 39 which is kept at a low temperature of about 5 ° C. or less and is spread on the punch plate 32 as a result is placed in a slowly frozen state. In other words, the ground garbage is extracellular frozen, and large ice crystals are generated and grown in the cell gap. As a result, the cell tissue is directly subjected to mechanical repair that cannot be repaired, and the cell membrane is destroyed. Migrate out of the cell.
Then, if the heat of condensation is supplied to the heat exchanger 35a from the refrigeration cycle 36, the frozen garbage is thawed, but the retained water that has moved out of the cell has broken the cell membrane. Combined with the pressing force of a certain pressing roller 34, it is stored in the dewatering tank through the punching hole 32 a of the punch plate 32.
Thus, the phase change of water is caused with low energy, non-polluting dehydration is possible, and multipurpose resource recycling is possible.
[0035]
If sufficient dehydration cannot be expected only by freezing and thawing, the number of times of freezing and thawing is repeated a plurality of times, and if necessary, cold air drying is performed for the final finish.
[0036]
【The invention's effect】
As described above, according to the present invention, the solid matter of the concentrated sludge obtained from the waste water was freeze-dehydrated, so that the water contained in the cells of the solid matter was single-crystallized by freezing. By making it into ice and melting it, a dry cake with a very low water content can be obtained. The electric charge required for freeze dehydration is much smaller than the fuel cost required for the heat source of the conventional heating evaporation method, and the running cost can be reduced.
[0037]
Moreover, by dehydrating the dried cake to form a dehydrated cake and converting it into a solid fuel, not only can it be reused as an energy resource, but also the incineration treatment is not performed, so that the occurrence of pollution such as dioxins and odors can be suppressed.
[0038]
By the above-described wastewater drainage treatment of the present invention, it is possible to achieve pollution-free and efficient dehydration with low energy, and to achieve multipurpose resources.
[Brief description of the drawings]
FIG. 1 is a system diagram showing an embodiment of a waste water treatment apparatus of the present invention.
FIG. 2 is a schematic diagram of a main part of FIG.
FIG. 3 is an explanatory view showing an example of the freeze dehydrating apparatus in FIG. 1;
FIG. 4 is a schematic diagram showing a schematic configuration of a garbage wastewater treatment apparatus in the present invention.
[Explanation of symbols]
2 Drainage 5 Sedimentation tank (initial sedimentation tank)
6 Settling tank (final settling tank)
DESCRIPTION OF SYMBOLS 8 Concentrated sludge tank 9 Freezing dehydration apparatus 11 Pelletization apparatus 12 Solid fuelization thing 14 Freezing room 15 Melting room 18 Turntable 19 Heat pump 20 Evaporator 21 Condenser 25 Waste water freezing separation apparatus 27 Ice machine 28 Thermal storage tank 30a, 30b Heat processing chamber 31 Feeder 32 Punch plate 33 Scraping machine 34 Press roller 35a, 35b Heat exchanger 36 Refrigeration cycle 37 Dehydration tank 38 Pulverizer 39 Pulverized garbage

Claims (7)

固形物を含む排水から汚泥を分離して汚泥ケーキ状として処理する排水処理方法において、
前記排水を沈殿槽に送って濃縮汚泥を生成する工程と、この濃縮汚泥を凍結乾燥して水分と固形物とを分離する工程と、該凍結脱水工程で生成された乾燥ケーキ状物を脱水して脱水ケーキを生成する工程と、前記脱水ケーキを固形化して固形燃料化物を生成する工程とからなり、前記沈殿槽で分離された上澄み排水を排水凍結分離装置の製氷機に送って清澄な氷と濃縮された排水とに分離し、その氷を蓄熱槽で溶解して得られた水を中水として利用することを特徴とする排水処理方法。
In the wastewater treatment method for separating sludge from wastewater containing solids and treating it as sludge cake,
The step of sending the waste water to a sedimentation tank to produce concentrated sludge, the step of freeze-drying the concentrated sludge to separate water and solids, and the dewatering of the dried cake produced in the freeze-dehydration step generating a dehydrated cake Te, the dehydrated cake was solidified Ri Do and a step of generating a solid fuel product, clarified supernatant drainage separated in the previous SL sedimentation tank is sent to ice machine drainage freezing separator A wastewater treatment method characterized in that water obtained by separating the ice into concentrated wastewater and melting the ice in a heat storage tank is used as intermediate water.
前記濃縮汚泥を凍結乾燥して水分と固形物とを分離する凍結脱水工程は、凍結・解凍を繰り返し行い、前記濃縮汚泥よりの脱水を十分に行なうようにしたことを特徴とする請求項1記載の排水処理方法。  The freeze dehydration step of freeze-drying the concentrated sludge to separate water and solids is performed by repeatedly freezing and thawing to sufficiently dehydrate the concentrated sludge. Wastewater treatment method. 初期沈殿槽と最終沈殿槽からなる排水の沈殿槽と、該初期沈殿槽で得られた濃縮汚泥を貯留する濃縮汚泥タンクと、該濃縮汚泥タンクからの濃縮汚泥を凍結脱水して水分と固形物とを分離して乾燥ケーキ状物を生成する凍結脱水装置と、該乾燥ケーキ状物を脱水して脱水ケーキを生成する遠心分離機と、該脱水ケーキを固形燃料化するペレット化装置と、前記最終沈殿槽で得られた上澄み排水を中水化処理する排水凍結分離装置と、を具え、前記排水凍結分離装置は、冷凍機、製氷機及び蓄熱槽を有し、最終沈殿槽よりの上澄み排水を前記製氷機に送られて凍結することにより、清澄な水分(氷)と濃縮された排水に分離され、その氷は前記蓄熱槽に送られると共に、濃縮排水は熱交換機を通して初期沈殿槽に返送されるように構成したことを特徴とする排水処理装置。 Initial sedimentation tank and sedimentation tank consisting final sedimentation tank effluent, the initial settling tank and the concentrated sludge tank for storing concentrated sludge obtained in water and solid was freeze dried concentrated sludge from the concentrated sludge tank Doo and freezing dehydrator to separate to produce a dry cake to a centrifuge and dehydrated the dried cake to produce a dewatered cake, and pelletizing apparatus for solid fuel a dehydration cake, the A drainage freezing and separating device that neutralizes the supernatant drainage obtained in the final settling tank, and the drainage freezing and separating apparatus includes a refrigerator, an ice making machine, and a heat storage tank, and the supernatant drainage from the final settling tank. The ice is sent to the ice making machine and frozen to separate it into clear water (ice) and concentrated waste water, and the ice is sent to the heat storage tank, and the concentrated waste water is returned to the initial settling tank through a heat exchanger. configured things to be Waste water treatment apparatus according to claim. 前記凍結脱水装置は、ヒートポンプに接続された蒸発器が設置された冷凍室と、前記ヒートポンプに接続された凝縮器が設置された融解室と、前記濃縮汚泥を載せて前記冷凍室から融解室に移送するターンテーブルと、からなることを特徴とする請求項3記載の排水処理装置。  The freeze dehydration apparatus includes a freezing chamber in which an evaporator connected to a heat pump is installed, a melting chamber in which a condenser connected to the heat pump is installed, and the concentrated sludge placed on the freezing chamber from the freezing chamber to the melting chamber. The wastewater treatment apparatus according to claim 3, comprising a turntable to be transferred. 前記凍結脱水装置は、微細な生ゴミを含む前記濃縮汚泥を前記ターンテーブルの間歇運転により凍結・解凍の繰り返し操作を可能にする構成としたことを特徴とする請求項記載の排水処理装置。5. The waste water treatment apparatus according to claim 4 , wherein the freeze dehydration apparatus is configured to allow repeated operation of freezing and thawing the concentrated sludge containing fine raw garbage by intermittent operation of the turntable. 生ゴミ粉砕機と、粉砕した生ゴミを穴明き受け板上に散布する可動式散布機と、前記穴明け受け板とその上に散布した粉砕生ゴミに凍結・解凍・冷風乾燥の熱処理をして脱水させる押圧ローラとを内蔵する凍結乾燥室と、凍結・解凍・冷風用の熱源を形成する冷凍サイクルと、前記受け板の下部に設けた脱水タンクと、より構成したことを特徴とする生ゴミの排水処理装置。  A garbage grinder, a movable spreader that spreads the crushed garbage on a perforated backing plate, and a heat treatment of freezing, thawing, and cold air drying on the perforated backing plate and the crushed garbage that has been sprinkled on it. A freeze-drying chamber containing a pressure roller for dehydration, a refrigeration cycle that forms a heat source for freezing, thawing, and cold air, and a dehydrating tank provided below the backing plate. Garbage wastewater treatment equipment. 前記凍結乾燥室は少なくとも二つ以上設ける構成とし、冷凍サイクルよりの熱の切り替え供給により、凍結・解凍・脱水の操作を交互に複数回行なう構成としたことを特徴とする請求項記載の生ゴミの排水処理装置。7. The raw material according to claim 6, wherein at least two freeze-drying chambers are provided, and the operation of freezing, thawing and dewatering is alternately performed a plurality of times by switching supply of heat from the refrigeration cycle. Waste water treatment equipment.
JP05495299A 1998-03-16 1999-03-03 Waste water treatment method and waste water treatment equipment Expired - Fee Related JP4180722B2 (en)

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