JPH07265900A - Sludge treating device - Google Patents

Sludge treating device

Info

Publication number
JPH07265900A
JPH07265900A JP6065071A JP6507194A JPH07265900A JP H07265900 A JPH07265900 A JP H07265900A JP 6065071 A JP6065071 A JP 6065071A JP 6507194 A JP6507194 A JP 6507194A JP H07265900 A JPH07265900 A JP H07265900A
Authority
JP
Japan
Prior art keywords
sludge
water
pipe
water content
stirrer
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Granted
Application number
JP6065071A
Other languages
Japanese (ja)
Other versions
JP3234710B2 (en
Inventor
Ikuo Maruoka
郁夫 丸岡
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
AUTO SETSUTO KK
Original Assignee
AUTO SETSUTO KK
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by AUTO SETSUTO KK filed Critical AUTO SETSUTO KK
Priority to JP06507194A priority Critical patent/JP3234710B2/en
Publication of JPH07265900A publication Critical patent/JPH07265900A/en
Application granted granted Critical
Publication of JP3234710B2 publication Critical patent/JP3234710B2/en
Anticipated expiration legal-status Critical
Expired - Lifetime legal-status Critical Current

Links

Classifications

    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F11/00Treatment of sludge; Devices therefor
    • C02F11/12Treatment of sludge; Devices therefor by de-watering, drying or thickening
    • C02F11/14Treatment of sludge; Devices therefor by de-watering, drying or thickening with addition of chemical agents

Landscapes

  • Chemical & Material Sciences (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • General Chemical & Material Sciences (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Hydrology & Water Resources (AREA)
  • Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Organic Chemistry (AREA)
  • Treatment Of Sludge (AREA)

Abstract

PURPOSE:To further enhance cost effectiveness and to eliminate the possibility of generation of secondary pollution by improving the efficiency of treating a large amt. of sludge and effectively utilizing the separated water discharged from a dehydrating stage. CONSTITUTION:A sludge press feeding pump 2, a reflux water feed-in pipe 4 for regulating a moisture content to >=30wt.%, a first stirrer 8, more preferably a pipeline stirrer, a flocculating agent supply pipeline 9, a second stirrer 11, more preferably a pipeline stirrer and an expanding pipe for pressure reduction are successively disposed at a sludge transporting pipe 3 from its inlet side. This sludge transporting piping is provided, on its outlet side, with a centrifugal-dehydrated solid separating means consisting of a dehydrated solid separating means, more preferably a centrifugal dehydrating machine loaded with freely attachable and detachable bag-shaped filter cloth and a transfer means for taking out this bag-shaped filter cloth and is provided with a waste water circulating system for returning the separated water discharged by this dehydrating means to the reflux water inflow pipe and a sludge generator.

Description

【発明の詳細な説明】Detailed Description of the Invention

【0001】[0001]

【産業上の利用分野】本発明は、堆積汚泥、産業廃棄ヘ
ドロ汚泥、工事現場から排出されるスライム、高含水ヘ
ドロ又はベントナイト排液等の大量のスラッジを急速処
理して環境の浄化、保全に資するための処理装置に関す
る。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention is intended for the purification and maintenance of the environment by rapidly treating a large amount of sludge such as accumulated sludge, industrial sludge sludge, slime discharged from construction sites, high water content sludge or bentonite drainage. The present invention relates to a processing device for contributing.

【0002】[0002]

【従来の技術】産業廃水、生活廃水を含む各種スラッジ
の水分より固形分を分離して疎質体、即ち、脱水固体と
して処分するための技術としては、従来より多くの提案
がなされ実用に供されている。それらの殆どは、大型の
沈殿槽、曝気槽、消化槽、汚泥分離槽等の大型固定設備
からなるもので、分離水を河川や下水道に放流し、分離
した固形分を焼却、コンポスト化、埋め立て用土等とし
て処分するものであり、このような設備は解体・移設が
困難であるからスラッジ排出場所に応じて随時、随所に
移動し得る機動性に欠けると共に、処理に長時間を要す
る。処理目的や場所に広く適応するために、浚渫または
捕集したヘドロを処理施設までバキューム車で輸送する
ことが一般に行われているが、多量の水分を含んだスラ
ッジの車両輸送には莫大な経費を要し処理費用の高騰を
招く。
2. Description of the Related Art As a technique for separating solids from the water content of various sludges containing industrial wastewater and domestic wastewater and disposing them as sparse bodies, that is, dehydrated solids, many proposals have been made and put to practical use. Has been done. Most of them consist of large fixed facilities such as large settling tanks, aeration tanks, digestion tanks, sludge separation tanks, etc.The separated water is discharged into rivers and sewers, and the separated solids are incinerated, composted, and landfilled. Since such equipment is disposed of as soil, etc., it is difficult to dismantle and relocate such equipment, so that it is not mobile enough to move from place to place depending on the sludge discharge place, and it takes a long time for treatment. It is common practice to transport dredged or trapped sludge to a treatment facility by a vacuum vehicle in order to adapt it widely to the treatment purpose and location, but it is enormous to transport the sludge containing a large amount of water by vehicle. Required, resulting in soaring processing costs.

【0003】上記の改善策として、例えば、近時汎用さ
れているジェットグラウト工法、地中連続壁工法、ウラ
ゴメール工法など、水をプロペラントとして用いる工事
現場から排出される大量のスライム、高含水ヘドロ又は
ベントナイト排液等を経済的に処理する目的で、比較的
小型化した配管を利用してスライムの吸引から脱水処理
までを連続的に行う試みがなされている。例えば、図2
に示すような従来の方法においては、スライム101 をポ
ンプ102 で配管103 を通して汲み上げ、疎水化剤を供給
管109 から圧入し、オンラインミキサー111 で攪拌した
後、袋状濾布を収納したネット等の二重袋118 に充填
し、次々に充填される袋 118、118′、118″・・・を適
宜な空間を有する広場まで搬送して懸吊し、長時間貯留
放置する。その間にヘドロ自体の重力によって遊離水が
徐々に絞り出されて、約1昼夜で固形分は処分に適した
状態にまで脱水し疎質体となる。然し乍らこのような工
程によっても、処分までの工程完結には依然として長時
間を必要とするのみならず、脱水工程において、スラッ
ジ充填袋貯留のための広い空間を必要とする等、必ずし
も効率的且つ経済的とは言い難い。更にこのような簡便
な装置においては、脱水工程から排出される酸性または
アルカリ性の遊離水はそのまま作業場外へ放流されるた
め、2次公害発生の虞れがある等、環境保全上充分に安
全とも認められない。
As a measure for improving the above, for example, a jet grout method, an underground continuous wall method, and a Uragomer method, which have been widely used recently, a large amount of slime discharged from a construction site using water as a propellant, and a high water content sludge. Alternatively, for the purpose of economically treating bentonite wastewater and the like, an attempt has been made to continuously perform from the suction of slime to the dehydration treatment using a relatively small pipe. For example, in FIG.
In the conventional method as shown in Fig. 1, the slime 101 is pumped up by the pump 102 through the pipe 103, the hydrophobizing agent is pressure-inserted through the supply pipe 109, stirred by the on-line mixer 111, and then the bag-like filter cloth is stored in a net or the like. The double bags 118 are filled, and the bags 118, 118 ′, 118 ″, ... Which are filled one after another, are transported to a plaza having an appropriate space, suspended, and stored for a long time. Gravity gradually squeezes the free water, and the solid content is dehydrated to a state suitable for disposal in about one day and becomes a sparse body.However, even with such a process, the process up to disposal is still not completed. Not only does it require a long time, but also a large space for storing sludge-filled bags is required in the dehydration process, which is not always efficient and economical. From the dehydration process Since the discharged acidic or alkaline free water is discharged as it is out of the work place, there is a risk of secondary pollution, and it is not considered safe enough for environmental protection.

【0004】[0004]

【発明が解決しようとする課題】従って本発明が解決し
ようとする問題点は、大量のスラッジの処理を効率化す
ると共に、脱水工程からの排出水を作業場外へ放流する
ことなく有効に再利用することによって更に経済性を高
め且つ2次公害発生の懸念を解消するにある。
Therefore, the problem to be solved by the present invention is that the treatment of a large amount of sludge is made efficient, and the drainage water from the dehydration process is effectively reused without being discharged to the outside of the work site. By doing so, the economic efficiency will be further increased and the concern about the occurrence of secondary pollution will be eliminated.

【0005】[0005]

【課題を解決するための手段】本発明は、スラッジ移送
経路の入り口側から、スラッジ圧入ポンプ、含水率調整
手段、第1攪拌器、凝集剤添加手段、第2攪拌器をこの
順序で下流側へ向かって連設してなり、上記移送経路の
出口側に、脱水/疎質体分離手段を配設し、該脱水/疎
質体分離手段よりの分離水を含水率調整手段及びスラッ
ジ発生源へ還流させる排水循環系を備えたことを特徴と
するスラッジ処理装置である。
According to the present invention, a sludge press-fitting pump, a water content adjusting means, a first stirrer, a coagulant adding means, and a second stirrer are arranged in this order from the inlet side of a sludge transfer path to the downstream side. The dehydration / sparse body separating means is provided on the outlet side of the transfer path, and the water separated from the dehydration / sparse body separating means is used as a water content adjusting means and a sludge generation source. It is a sludge treatment device characterized by having a drainage circulation system for recirculating the sludge.

【0006】上記スラッジ移送経路は輸送配管よりな
り、また上記含水率調整手段は好ましくは、圧入される
スラッジの含水率に応じてスラッジ全重量基準で少なく
とも30%の含水率となるよう還流水を輸送配管中へ送入
する送液機構を含んでなる。
The sludge transfer path is composed of a transportation pipe, and the water content adjusting means preferably supplies the reflux water so that the water content is at least 30% based on the total weight of the sludge according to the water content of the sludge to be press-fitted. It comprises a liquid feeding mechanism for feeding into the transportation piping.

【0007】また、上記含水率調整手段は好ましくは、
圧入されるスラッジの含水率を検出し、検出信号により
作動する自動調節弁を還流水送入管に設けてなる。
Further, the water content adjusting means is preferably
An automatic control valve, which detects the water content of the sludge to be press-fitted and operates according to the detection signal, is provided in the reflux water inlet pipe.

【0008】上記第1および第2攪拌器は好ましくは、
輸送配管途中に組み込まれたスタティックミキサーであ
る。
The first and second stirrers are preferably
It is a static mixer installed in the middle of transportation piping.

【0009】上記凝集剤添加手段は好ましくは、凝集剤
を流体と共に輸送配管中へ圧入するための圧入機構を含
んでなる。
The coagulant adding means preferably comprises a press-fitting mechanism for press-fitting the coagulant together with the fluid into the transportation pipe.

【0010】本発明装置は好ましくは、第2攪拌器に続
いて前記輸送配管中の液圧を減圧するための機構よりな
る固形分凝集疎水手段を更に含んでなる。
The apparatus of the present invention preferably further comprises, following the second stirrer, a solid content aggregating hydrophobic means comprising a mechanism for reducing the liquid pressure in the transportation pipe.

【0011】上記脱水/疎質体分離手段は好ましくは、
直立型有孔バスケット駆動式遠心脱水機と、該バスケッ
ト内壁に添接される寸法を有し且つ上方が開口した袋状
濾布と、該袋状濾布を取り出して移送する搬送機構とよ
りなる。
The dehydration / phosporus separation means is preferably
An upright type perforated basket drive type centrifugal dehydrator, a bag-like filter cloth having a size to be attached to the inner wall of the basket and having an upper opening, and a transport mechanism for taking out and transferring the bag-like filter cloth. .

【0012】上記排水循環系は好ましくは、前記脱水/
疎質体分離手段より排出される分離水を捕集して前記含
水率調整手段及びスラッジ発生源へ還流させるための還
流用配管と送液ポンプとを含んでなる。
[0012] The drainage circulation system is preferably the dehydration /
It comprises a reflux pipe and a liquid feed pump for collecting the separated water discharged from the lyophobic body separating means and returning it to the water content adjusting means and the sludge generating source.

【0013】スラッジが、ジェットグラウト工法、地中
連続壁工法、ウラゴメール工法等、大量の水をプロペラ
ントとして用いる土木工事現場より排出されるスライ
ム、高含水ヘドロまたはベントナイト排液であるとき
は、分離水を還流させる上記スラッジ発生源は工事用水
タンクである。
When the sludge is slime, high water content sludge or bentonite drainage discharged from a civil engineering construction site that uses a large amount of water as a propellant, such as the jet grout method, underground continuous wall method, and Uragomer method, it is separated. The sludge generation source that recirculates water is a construction water tank.

【0014】上記のような構成になる本発明装置は、比
較的構造簡単で解体・移設容易であるから、大量のスラ
ッジを随所において随時に頗る効率的に且つ経済的に処
理することができ、好適な実施例においては、例えば僅
かに10数分間内で処分に適したケーキ状脱水スラッジと
することが可能であり、また、分離水をスラッジ含水率
調整工程に還流し再利用することによって凝集剤の使用
量の著しい節減が達成されると共に、分離水を、更にス
ラッジ発生源、例えば工事用水タンク或いはジェットグ
ラウト工法、地中連続壁工法、ウラゴメール工法等大量
の水をプロペラントとして用いる工事用水タンクに還流
再使用することによって、かかる工法に消費される水の
大幅な節約を可能とする。また、スラッジ処理系をこの
ようにクローズドサイクルとして分離水を作業場外へ放
流することがないから、2次公害発生の虞れは皆無とな
る。
Since the device of the present invention having the above-mentioned structure has a relatively simple structure and is easy to dismantle and relocate, it is possible to efficiently and economically process a large amount of sludge everywhere. In a preferred embodiment, the cake-like dewatered sludge suitable for disposal can be obtained, for example, within 10 minutes or less, and the separated water is recycled to the sludge moisture content adjusting step and reused for coagulation. A significant reduction in the amount of chemicals used is achieved, and separated water is used as a propellant for sludge generation sources, such as construction water tanks or jet grout construction methods, underground continuous wall construction methods, and Uragomer construction methods. Recycling back into the tank allows for a significant savings in the water consumed by such methods. Further, since the sludge treatment system is not used as a closed cycle to discharge the separated water to the outside of the work site, there is no possibility of secondary pollution.

【0015】[0015]

【実施例】以下、本発明を添付図面を参照し、その実施
例について詳述する。図1は、本発明装置の最も好適な
実施例のフローシートである。スラッジ1はその発生源
である湖沼、河川、下水等、または貯留槽よりスラッジ
圧入ポンプ2によって汲み上げられ、スラッジ移送用経
路である輸送配管3に送入される。送入されたスラッジ
はその含水率がスラッジ全重量基準で約30%未満の場合
には、次工程における凝集効果が低く疎水化しにくいた
め、先ず含水率調整手段を経て含水率を増大させる。含
水率調整手段は、輸送配管3の途中に設けたノズルとそ
れに最終工程からの還流水をポンプで圧入する還流水送
入管4とからなる。この場合、原スラッジをサンプリン
グして測定し、含水率が約30%未満の場合にはそれが約
30%以上、好ましくは約40%以上となるようにスラッジ
送入量に応じて適量の水を還流水送入管4から連続的に
圧入する。
Embodiments of the present invention will now be described in detail with reference to the accompanying drawings. FIG. 1 is a flow sheet of the most preferred embodiment of the device of the present invention. The sludge 1 is pumped up by a sludge injection pump 2 from a lake, a river, a sewage or the like, which is a source of the sludge, and is sent to a transportation pipe 3 which is a sludge transfer route. When the water content of the sludge fed is less than about 30% based on the total weight of the sludge, the coagulation effect in the next step is low and it is difficult to hydrophobize, so that the water content is first increased through the water content adjusting means. The water content adjusting means is composed of a nozzle provided in the middle of the transportation pipe 3 and a reflux water inlet pipe 4 into which the reflux water from the final step is pressed by a pump. In this case, raw sludge is sampled and measured, and when the water content is less than about 30%, it is about
An appropriate amount of water is continuously injected from the reflux water inlet pipe 4 in accordance with the amount of sludge fed so that the amount becomes 30% or more, preferably about 40% or more.

【0016】また、スラッジの含水率を輸送配管3の入
り口付近で検知する含水率検知手段5と、検知された濃
度と標準濃度とを比較演算して適正な給水量を算出する
演算回路6と、還流水送入管4の途中に設けられ且つ演
算回路からの信号を受けて作動する自動調節弁7とより
なる給水量自動制御系を設けることは極めて好ましいこ
とである。
Further, a water content detecting means 5 for detecting the water content of the sludge near the entrance of the transportation pipe 3, and an arithmetic circuit 6 for comparing and operating the detected concentration and the standard concentration to calculate an appropriate water supply amount. It is extremely preferable to provide an automatic water supply amount control system, which is provided in the middle of the return water inlet pipe 4 and is composed of an automatic control valve 7 that operates by receiving a signal from the arithmetic circuit.

【0017】次いで、含水率調整手段に引き続き、第1
攪拌器8が設けられる。含水率を調整されたスラッジ
は、一旦タンクに落として通常の回転翼式攪拌器で攪拌
してもよく、また輸送配管中で渦巻きポンプ等を通して
乱流による攪拌作用を施してもよい。最も好ましくは、
図示の如く所謂オンラインミキサー或いはスタティック
ミキサーとして知られる管路攪拌器8、即ち管中に多数
の流路反転素子を直列に配列した静止型ミキサーであ
る。
Then, following the water content adjusting means, the first
A stirrer 8 is provided. The sludge whose water content has been adjusted may be once dropped into a tank and stirred with a normal rotary blade type agitator, or may be subjected to a turbulent agitation action through a spiral pump or the like in a transportation pipe. Most preferably,
As shown in the figure, it is a line mixer 8 known as a so-called online mixer or static mixer, that is, a static mixer in which a large number of flow path inverting elements are arranged in series in the pipe.

【0018】上記第1攪拌器8の下流側の輸送配管に
は、含水率30%以上の適宜な濃度で均質化されたスラッ
ジに対して凝集剤を添加するためのノズルと、このノズ
ルに対して凝集剤を流体媒体と共に圧入するための凝集
剤供給管路9とよりなる凝集剤添加手段が設けられる。
流体媒体が液体例えば水であって、それに凝集剤を溶解
または分散して供給する場合には、圧入はポンプ10で行
い、粉体の凝集剤を気体流体例えば空気で搬送する場合
にはエアコンプレッサー(図示しない)の助けを借りて
圧縮空気で圧入する。また、粉体の凝集剤の場合には、
スクリューフィーダーで圧送して供給してもよい。
A nozzle for adding a coagulant to sludge homogenized at an appropriate concentration with a water content of 30% or more is provided in the transportation pipe on the downstream side of the first stirrer 8, and to this nozzle. And a coagulant supply line 9 for press-fitting the coagulant together with the fluid medium.
When the fluid medium is a liquid such as water, and the flocculating agent is dissolved or dispersed and supplied to the liquid medium, press-fitting is performed by the pump 10, and when the powder flocculating agent is conveyed by a gas fluid such as air, an air compressor. Press in with compressed air with the help of (not shown). Further, in the case of a powder flocculant,
It may be fed by pressure with a screw feeder.

【0019】凝集力の高い凝集剤としては、例えば、硫
酸アルミニウム、塩化アルミニウム等の無機質酸性凝集
剤、アルミン酸ソーダ、ポリ塩化アルミニウム、低塩基
性アルミニウム等の無機質塩基性凝集剤、硫酸アルミニ
ウムとポリ塩化アルミニウムとを併用した無機質両性凝
集剤およびポリアクリル酸アミノエステル、ジアミンジ
アミド、アルギン酸ソーダ等の有機高分子凝集剤等があ
るが、有機高分子凝集剤は、最終的に得られる疎質体ケ
ーキ中に残存して粘着性を示し、ケーキの崩壊分離を妨
げ団塊化する傾向があるため、その後のケーキの処分目
的によっては好ましくなく、無機質凝集剤が好ましく適
用される。最も好ましくは、本発明者が特開平1-254292
号に提案した水中懸濁物の凝固分離方法で用いた(株)
オートセット製のアルミニウム系凝集剤「ムキフロック
TM」を適用することである。またこの凝集剤にセメント
系固化材、或いはそれに適量の石膏を混合した固化材、
例えば代表例としては(株)オートセット製「オートセ
ット(登録商標)固化材」を、前記凝集剤に対する固化
材の重量比、1/1〜1/5、好ましくは1/2〜1/
4の割合で適用すれば極めて満足すべき結果が得られ、
遊離水を分離した疎質体ケーキは適度に抱水し、粘着凝
集性を失って、一般残土として容易に取り扱うことがで
きる。
Examples of the coagulant having a high cohesive force include inorganic acidic coagulants such as aluminum sulfate and aluminum chloride, inorganic basic coagulants such as sodium aluminate, polyaluminum chloride and low basicity aluminum, and aluminum sulfate and poly There are inorganic amphoteric flocculants combined with aluminum chloride and polyacrylic acid aminoesters, diaminediamide, organic polymer flocculants such as sodium alginate, etc., but the organic polymer flocculants are sparse cakes finally obtained. Since it remains inside and shows tackiness and tends to prevent the cake from separating and collapsing, it is not preferable depending on the purpose of the subsequent disposal of the cake, and the inorganic flocculant is preferably applied. Most preferably, the present inventor
Used in the coagulation separation method of water suspension proposed in No.
Autoset aluminum coagulant "Mukiflock
TM "is applied. In addition, this flocculant is a cement-based solidifying material, or a solidifying material in which an appropriate amount of gypsum is mixed,
For example, as a representative example, "Autoset (registered trademark) solidifying material" manufactured by Autoset Co., Ltd. is used, and the weight ratio of the solidifying material to the coagulant is 1/1 to 1/5, preferably 1/2 to 1 /.
Applying at a ratio of 4 gives very satisfactory results,
The sparse substance cake from which the free water is separated retains water moderately, loses its adhesive and cohesive properties, and can be easily handled as general residual soil.

【0020】凝集剤を添加したスラッジは、次いで第2
攪拌器11により攪拌され均質化される。この際スラッジ
は、一旦タンクに落として通常の回転翼式攪拌器で攪拌
してもよく、また輸送配管中で渦巻きポンプ等を通して
攪拌作用を施してもよい。最も好ましくは、前記第1攪
拌器と同様、所謂オンラインミキサー或いはスタティッ
クミキサーとして知られる管路攪拌器11が適用される。
The sludge to which the flocculant has been added is then added to the second sludge.
The mixture is stirred by the stirrer 11 and homogenized. At this time, the sludge may be once dropped into a tank and agitated by an ordinary rotary blade type agitator, or may be agitated by a spiral pump or the like in the transportation pipe. Most preferably, like the first stirrer, a line stirrer 11 known as a so-called online mixer or static mixer is applied.

【0021】スラッジと凝集剤との混合物は第2攪拌器
で均質化して直ちに反応し、スラッジ中の懸濁固形分は
輸送配管中で急速に固形分のフロックを形成しさらに粗
大粒子に成長して沈降し始める。その状態で次の脱水/
疎質体分離手段に移行してもよいが、それに先立って固
形分凝集疎水手段を経ることが好ましい。かかる固形分
凝集疎水手段は、輸送配管の管径を例えば異径継ぎ手12
を用いて拡大して形成したリデューサー13を管路に介在
させることによって具体化される。リデューサー13によ
って、スラッジの液圧は減圧され、流速を減じるため、
フロックの凝集沈降が促進され、次工程の脱水分離を容
易化する。
The mixture of sludge and flocculant is homogenized in the second stirrer and immediately reacted, and the suspended solids in the sludge rapidly form flocs of solids in the transport pipe and further grow into coarse particles. Begins to settle. Next dehydration /
Although it may be transferred to the sparse body separating means, it is preferable to go through the solid content aggregating hydrophobic means prior to the transfer. Such a solid content aggregating hydrophobic means has a pipe diameter of the transport pipe, for example, a different diameter joint 12
It is embodied by interposing a reducer 13 enlarged and formed in the pipe. The liquid pressure of the sludge is reduced by the reducer 13 to reduce the flow velocity,
The flocculation and sedimentation are promoted, facilitating the dehydration separation in the next step.

【0022】輸送配管から吐出された沈殿物と遊離水と
は配管出口に配置された脱水/疎質体分離手段に移行す
る。脱水/疎質体分離手段は、従来公知の連続式または
回分式遠心濾過機或いは遠心脱水機を適用することがで
きる。また、公知のネットに収納した濾布を用いて懸吊
脱水してもよい。然し乍ら、最も効率的にして、工事現
場や作業区域の限られた場所、或いは山間僻地等で実施
するに適した汎用性に富み軽便且つ好適な手段は、直立
型有孔バスケット駆動式遠心脱水機と、該バスケット内
壁に添接し得る寸法を有し且つ上方が開口した袋状濾布
と、該袋状濾布を脱水ケーキごと吊り上げてバスケット
より取り出し、更に横方向に移送する搬送機構とよりな
る。
The precipitate and the free water discharged from the transportation pipe are transferred to the dehydration / sparse substance separating means arranged at the pipe outlet. A conventionally known continuous type or batch type centrifugal filter or centrifugal dehydrator can be applied to the dehydrating / sloppy substance separating means. Moreover, you may suspend and dehydrate using the filter cloth accommodated in the well-known net. However, the most efficient, versatile, convenient and suitable means suitable for carrying out at a construction site, a limited work area, or a remote mountain area is an upright perforated basket-driven centrifugal dehydrator. And a bag-shaped filter cloth having a size capable of being attached to the inner wall of the basket and having an opening at the upper side, and a transport mechanism for lifting the bag-shaped filter cloth together with the dehydrated cake, taking it out of the basket, and transferring it in the lateral direction. .

【0023】かかる脱水/疎質体分離手段における遠心
脱水機は、直立型有孔バスケット14を内蔵し、このバス
ケット14を少なくとも毎分数千回転の速度で回転させる
モーター駆動の回転軸15を下方に備えるケーシング16よ
りなり、ケーシング16の底部には排水口17を有する。バ
スケット14は、その内壁面に内接する寸法を有し且つ濾
布で形成され上方が開口した袋体、即ち袋状濾布18を内
周面に添接して収納する。袋状濾布18は透水性ではある
が疎質体微粒子非透過性の布帛、例えば天然または合成
繊維よりなる緻密組織の織布または不織布よりなる濾布
で形成され、上方のフック19を含む搬送機構、例えば、
ホイスト、クレーン等により吊り上げられ、更に平行移
動することができる。布帛の素材としては、綿、麻、ビ
スコーススフ等のセルロース系繊維が、使用後の腐食分
解や焼却容易であり、また不織布が濾過性能および価額
の面で好ましい。この濾布は透水性であるが疎質体微粒
子を透過しない程度の目付で、且つ収容する処理スラッ
ジの荷重に充分耐え得る強度を保持するよう設計される
べきことは言うまでもない。
The centrifugal dehydrator in the dehydration / sparse substance separating means has a built-in upright type perforated basket 14 and a motor-driven rotating shaft 15 for rotating the basket 14 at a speed of at least several thousands of revolutions per minute. And a drainage port 17 at the bottom of the casing 16. The basket 14 has a size which is inscribed on the inner wall surface thereof, and is formed by a filter cloth and has an opening at the top, that is, a bag-shaped filter cloth 18 is attached to the inner peripheral surface and accommodated therein. The bag-like filter cloth 18 is formed of a cloth that is water-permeable but impervious to fine particles of sparse material, for example, a filter cloth made of a woven fabric or a non-woven fabric having a dense structure made of natural or synthetic fibers, and includes a hook 19 on the upper side. Mechanism, for example,
It can be lifted by a hoist, crane, etc., and further moved in parallel. As a material for the cloth, cellulosic fibers such as cotton, hemp, and viscose staple are easily decomposed by corrosion and incinerated after use, and non-woven fabric is preferable in terms of filtration performance and cost. It goes without saying that this filter cloth should be designed to be water-permeable but have a fabric weight that does not allow permeation of sparse particles, and to have sufficient strength to withstand the load of the treated sludge contained therein.

【0024】輸送配管出口末端の抑止弁20を開放して適
量のスラッジを遠心脱水機に注入し回転軸15を駆動する
と、スラッジは予め分離水と疎質体層とに別れているた
め、分離水は急速にケーシング16の底部排水口17より排
出され、更に運転を数分間継続することによって粒子外
液、即ち粒子表面付着液、ウェッジ液、毛管上昇液が実
質的に全て分離され、袋体18中には、粒子内液を抱水す
るが全体に体積の著しく減少した疎質体ケーキが残存す
るに至る。その状態に達した頃を見計らって、遠心脱水
機を停止すると同時にフック19によって袋状濾布18ごと
疎質体ケーキを吊り上げて更に適宜な貯留場所または運
搬手段まで移送する。遠心脱水機には新たな袋体を装填
して次回の運転に備える。
When the inhibition valve 20 at the end of the outlet of the transportation pipe is opened and a proper amount of sludge is injected into the centrifugal dehydrator and the rotary shaft 15 is driven, the sludge is separated into separated water and a sparse body layer in advance, Water is rapidly discharged from the bottom drainage port 17 of the casing 16, and by continuing the operation for several minutes, substantially all of the particle external liquid, that is, the liquid adhering to the particle surface, the wedge liquid, and the capillary rising liquid are separated, and the bag body In 18, the sparse material cake, which retains the liquid in the particles but whose volume is remarkably reduced, remains. When the state is reached, the centrifugal dehydrator is stopped, and at the same time, the bag-like filter cloth 18 and the sparse material cake are lifted by the hook 19 and further transferred to an appropriate storage place or a transportation means. The centrifugal dehydrator is loaded with a new bag to prepare for the next operation.

【0025】従来の濾布などの濾過手段を備えた遠心濾
過機では、遠心脱水機に装備された濾布は反覆使用によ
る目詰まり等のため濾過効率の低減が著しく、また生成
するケーキの排出や取り出しに別途装置上の様々な工夫
や相当な労力を要するが、本発明の上記脱水/疎質体分
離手段によれば、袋状濾布は使い捨てであるから濾過効
率の低下は一切見られずに操作は短時間で完了し、また
遠心脱水機からの取り出し搬送も容易である。更に、前
記凝集剤を無機系の例えば「ムキフロックTM」とするか
或いはそれと「オートセット(登録商標)固化材」を併
用すれば、この工程で分離された疎質体ケーキは一切粘
着団塊化することなく容易に崩壊するから、通常の土壌
として取り扱うことができるという利点がある。更にま
た、前記従来の二重袋懸吊式の自重利用絞液法に比し、
頗る短時間で処分可能な状態の疎質体ケーキが得られ且
つ袋懸吊保管のための広い空間も不要である。
In a conventional centrifugal filter equipped with a filtering means such as a filter cloth, the filter cloth equipped in the centrifugal dehydrator has a significant decrease in filtration efficiency due to clogging caused by repeated use, and the cake produced is discharged. Although various efforts on the device and considerable labor are required for removing and removing the bag-like filter cloth, the bag-like filter cloth is disposable because the dehydrating / sparse body separating means of the present invention shows no reduction in filtration efficiency. Without this, the operation is completed in a short time, and it is easy to take out and convey from the centrifugal dehydrator. Furthermore, if the aggregating agent is an inorganic type such as "Mukifloc " or if it is used in combination with "Autoset (registered trademark) solidifying material", the sparse substance cake separated in this step will be cohesive nodule at all. It has the advantage that it can be treated as normal soil because it easily collapses without any treatment. Furthermore, compared to the conventional double bag suspension type self-weight-based squeezing method,
A sparse cake that can be disposed of in a short period of time can be obtained, and a large space for suspending and storing in a bag is not required.

【0026】本発明の最大の要点の一つは、分離水還流
手段を設けて、排水循環系を形成したことにある。即
ち、上記遠心脱水機の底部排水口17より排出される分離
水をタンク或いはピット等の貯留槽21に捕集して一旦貯
留し、送液ポンプ22により還流用配管23を経て、還流水
送入管4から含水率調整手段へ還流させると共に、スラ
ッジ発生源24に還流する。この場合、送液ポンプ22は、
前記の含水率調整手段における輸送配管への還流水圧入
ポンプとして或いは、スラッジ発生源への輸液ポンプと
して作用する。
One of the most important points of the present invention is that a drainage circulation system is formed by providing separated water recirculation means. That is, the separated water discharged from the bottom drainage port 17 of the centrifugal dehydrator is collected and temporarily stored in a storage tank 21 such as a tank or a pit, and is fed by a liquid feed pump 22 through a reflux pipe 23 to feed reflux water. The water is returned from the inlet pipe 4 to the water content adjusting means and also to the sludge generating source 24. In this case, the liquid feed pump 22 is
It functions as a reflux water injection pump to the transportation pipe in the water content adjusting means or as an infusion pump to the sludge generation source.

【0027】脱水/疎質体分離手段より排出される分離
水は、相当量の未反応凝集剤を含有しているので、これ
を含水率調整手段へ還流しスラッジに供給して含水率調
整用として用いると、凝集剤添加工程における凝集剤添
加量は消費分を補充するだけの僅かな量で足り、凝集剤
の著しい節減が達成される。
Since the separated water discharged from the dehydration / phobic substance separation means contains a considerable amount of unreacted coagulant, it is refluxed to the water content adjusting means and supplied to the sludge to adjust the water content. In this case, the amount of the coagulant added in the coagulant addition step may be a small amount for replenishing the consumed amount, and a significant saving of the coagulant is achieved.

【0028】大量の水を使用する工事現場、例えば所謂
ジェットグラウト工法、地中連続壁工法、ウラゴメール
工法等、大量の水をプロペラントとして用いる工事現場
から排出される膨大量のスライム、高含水ヘドロ又はベ
ントナイト排水等の処理に本発明装置を適用すると、分
離水を工事用水貯槽24に還流再利用するから、従来水道
水を使用していた工事用水の著しい節約を達成すること
ができる。また、スラッジが上記のような工事現場から
排出されるものである場合には、分離水がアルカリ性に
可成り偏倚することが多い。アルカリ性がある程度を越
して放流されると生活あるいは産業上に2次公害を齎す
虞れがあるが、本発明装置においては分離水を還流して
工事用水に再使用するというクローズドサイクルの処理
系としたから、分離水が一切放流されることなく2次公
害発生の危険は生じない。また、湖沼、河川、下水道な
どのスラッジ処理の場合には、清澄な分離水はもとのス
ラッジ発生源へ還流されるから、この場合もスラッジ発
生源以外の場所に放流されることによる環境汚染の虞れ
はない。
A huge amount of slime discharged from a construction site that uses a large amount of water as a propellant, such as a so-called jet grout construction method, an underground continuous wall construction method, and a Uragomer construction method, and a high water content sludge. Alternatively, when the apparatus of the present invention is applied to the treatment of bentonite wastewater and the like, the separated water is recirculated to the construction water storage tank 24 and reused, so that a significant saving of construction water, which conventionally used tap water, can be achieved. Further, when sludge is discharged from the construction site as described above, the separated water is often biased to be alkaline. If the alkalinity is released beyond a certain level, it may cause secondary pollution in life or industry, but in the device of the present invention, the separated water is recycled and reused as construction water. Therefore, the separated water is not discharged at all and there is no danger of secondary pollution. In addition, in the case of sludge treatment of lakes, rivers, sewers, etc., the clear separated water is returned to the original sludge source, and in this case also, environmental pollution caused by being discharged to a place other than the sludge source. There is no fear of.

【0029】上記本発明のスラッジ処理装置の好ましい
態様を要約すると、スラッジ輸送配管3に、その入り口
側から、スラッジ圧入ポンプ2、含水率を30重量%以上
に調整するための還流水送入管4、第1攪拌器8、好ま
しくは管路攪拌器、凝集剤供給管路9、第2攪拌器11、
好ましくは管路攪拌器、減圧のための大径リデューサー
13を順次配設し、その出口側に、脱水固形分分離手段、
好ましくは濾布袋体18を装脱自在に装填した遠心脱水機
と濾布を取り出し移送する搬送機構とよりなる脱水/疎
質体分離手段を設け、脱水/疎質体分離手段の排出する
分離水を前記還流水送入管4及びスラッジ発生源、例え
ば、プロペラント水を使用する工事の工事用水貯槽24へ
還流する還流用配管23を含む排水循環系を備えてなるス
ラッジ処理装置である。
To summarize the preferred embodiment of the sludge treatment apparatus of the present invention, the sludge transport pipe 3 is provided with an inlet side of the sludge press-fitting pump 2 and a reflux water inlet pipe for adjusting the water content to 30% by weight or more. 4, a first stirrer 8, preferably a line stirrer, a flocculant supply line 9, a second stirrer 11,
Pipe line stirrer, large diameter reducer for decompression
13 are sequentially arranged, and on the outlet side thereof, dehydrated solid content separation means,
It is preferable to provide a dehydrating / loose substance separating means including a centrifugal dehydrator in which the filter cloth bag body 18 is detachably loaded and a transport mechanism for taking out and transferring the filter cloth, and the separated water discharged from the dehydrating / loose body separating means. Is a sludge treatment device comprising a reflux water inlet pipe 4 and a sludge generation source, for example, a drainage circulation system including a reflux pipe 23 for returning the sludge to a construction water storage tank 24 for construction using propellant water.

【0030】[0030]

【発明の効果】以上説明したように、本発明のスラッジ
処理装置は、分離水還流手段を設け、脱水/疎質体分離
手段より排出される分離水を含水率調整手段へ還流しス
ラッジに供給して含水率調整用として再利用するように
したから、凝集剤添加工程における凝集剤の著しい節減
が達成される。更に、所謂ジェットグラウト工法、地中
連続壁工法、ウラゴメール工法等の大量の水をプロペラ
ントとして利用する工事現場から排出される膨大量のス
ライム、高含水ヘドロ、ベントナイト排液等の処理に本
発明装置を適用する場合には、従来のバキューム車によ
る運搬のための莫大な輸送経費を節約し得るのみなら
ず、本発明装置の排水循環系により分離水を更に工事用
水として再利用し得るから、従来水道水を費消していた
工事用水の著しい節約を達成することができる。更にま
た、本発明装置はこのように水をクローズドサイクルと
したから、分離水が作業場外へ一切放流されることな
く、放流による2次公害発生の危険が皆無となるという
大きな利点がある。本発明装置の最も好ましい態様にお
いては、スラッジの汲み上げから脱水/疎質体分離工程
に移すまでのスラッジの移送並びに処理を全て輸送配管
系において連続的に行うと共に、脱水/疎質体分離手段
における濾布の目詰まり等による濾過効率の低下は一切
見られず、操作は僅か10数分以内の短時間で完了し、ま
た脱水された疎質体ケーキは嵩および重量が著しく減少
した状態にあるから、遠心脱水機からの取り出し搬送も
容易である。更に、凝集剤を適宜に選択することにより
分離された疎質体ケーキは粘着団塊化することなく容易
に崩壊するから、通常の土壌として取り扱うことがで
き、処分が容易であるという利点がある。このように、
従来の大型の固定化したスラッジ処理装置に比して頗る
小型化され軽便であるにも拘わらず、大量のスラッジを
随所において随時に頗る効率的に且つ経済的に処理する
ことができ、所謂小回りの利く汎用性に富み、大きい処
理空間を必要とせず、工事現場や作業区域の限られた場
所、或いは山間僻地等で実施するに適する。
As described above, the sludge treatment apparatus of the present invention is provided with the separated water recirculation means, and the separated water discharged from the dewatering / mesophobic body separation means is recirculated to the water content adjusting means and supplied to the sludge. Since it is reused for adjusting the water content, a significant reduction of the coagulant in the coagulant addition step is achieved. Further, the present invention is applied to the treatment of a huge amount of slime, high water content sludge, bentonite drainage, etc. discharged from a construction site that uses a large amount of water as a propellant such as the so-called jet grout method, underground continuous wall method, and Uragomer method. When the device is applied, not only can the huge transportation cost for transportation by the conventional vacuum vehicle be saved, but also the separated water can be reused as construction water by the drainage circulation system of the device of the present invention, Significant savings can be achieved on construction water, which previously cost tap water. Furthermore, since the apparatus of the present invention uses water as a closed cycle in this way, there is a great advantage that the separated water is not discharged to the outside of the work site at all and there is no risk of secondary pollution due to the discharge. In the most preferred embodiment of the device of the present invention, all of the sludge transfer and treatment from pumping of sludge to transfer to the dehydration / sparse body separation step are continuously carried out in the transport piping system, and in the dehydration / sparse body separation means. No decrease in filtration efficiency due to clogging of the filter cloth was observed, the operation was completed within a short time of less than 10 minutes, and the dehydrated sparsely-dispersed cake was in a state where the bulk and weight were significantly reduced. Therefore, it is easy to take out and convey from the centrifugal dehydrator. Further, since the sparse substance cake separated by appropriately selecting the flocculant is easily collapsed without causing cohesive agglomeration, there is an advantage that it can be handled as normal soil and is easily disposed. in this way,
Despite being smaller and lighter than conventional large-scale fixed sludge treatment equipment, it is possible to efficiently and economically treat large amounts of sludge everywhere, so-called small turning It is highly versatile, does not require a large processing space, and is suitable for use in construction sites, limited work areas, or in remote mountain areas.

【図面の簡単な説明】[Brief description of drawings]

【図1】本発明スラッジ処理装置のフローシートであ
る。
FIG. 1 is a flow sheet of a sludge treatment device of the present invention.

【図2】従来公知のスラッジ処理装置のフローシートで
ある。
FIG. 2 is a flow sheet of a conventionally known sludge treatment device.

【符号の説明】 1 スラッジ 2 スラッジ圧入ポンプ 3 輸送配管 4 還流水送入管 5 含水率検知手段 6 演算回路 7 自動調節弁 8 第1攪拌器 9 凝集剤供給管路 10 ポンプ 11 第2攪拌器 12 異径継ぎ手 13 リデューサー 14 直立型有孔バスケット 15 回転軸 16 ケーシング 17 排水口 18 袋状濾布 19 フック 20 抑止弁 21 貯留槽 22 送液ポンプ 23 還流用配管 24 工事用貯水槽[Explanation of symbols] 1 sludge 2 sludge press-fitting pump 3 transportation piping 4 reflux water feeding pipe 5 water content detection means 6 arithmetic circuit 7 automatic control valve 8 first stirrer 9 coagulant supply pipeline 10 pump 11 second stirrer 12 Different diameter joint 13 Reducer 14 Upright type perforated basket 15 Rotating shaft 16 Casing 17 Drainage port 18 Bag-like filter cloth 19 Hook 20 Suppression valve 21 Storage tank 22 Liquid feed pump 23 Reflux pipe 24 Construction water tank

Claims (10)

【特許請求の範囲】[Claims] 【請求項1】 スラッジ移送経路の入り口側から、スラ
ッジ圧入ポンプ、含水率調整手段、第1攪拌器、凝集剤
添加手段、第2攪拌器をこの順序で下流側へ向かって連
設してなり、上記移送経路の出口側に、脱水/疎質体分
離手段を配設し、該脱水/疎質体分離手段よりの分離水
を含水率調整手段及びスラッジ発生源へ還流させる排水
循環系を備えたことを特徴とするスラッジ処理装置。
1. A sludge injection pump, a water content adjusting means, a first stirrer, a coagulant adding means, and a second stirrer are connected in this order from the inlet side of the sludge transfer path toward the downstream side. A drainage circulation system is provided on the outlet side of the transfer path, wherein dewatering / mesophobic material separating means is disposed, and water separated from the dewatering / mesophilic material separating means is circulated to the water content adjusting means and the sludge generation source. A sludge treatment device characterized in that
【請求項2】 上記スラッジ移送経路が輸送配管よりな
り、上記含水率調整手段が圧入されるスラッジの含水率
に応じてスラッジ全重量基準で少なくとも30%の含水率
となるよう還流水を輸送配管中へ送入する送液機構を含
んでなる請求項1のスラッジ処理装置。
2. The sludge transfer path is constituted by a transportation pipe, and the reflux water is transported by a piping so that the water content adjusting means has a water content of at least 30% based on the total weight of the sludge according to the water content of the sludge to be press-fitted. The sludge treatment device according to claim 1, further comprising a liquid feeding mechanism for feeding into the sludge.
【請求項3】 上記含水率調整手段が圧入されるスラッ
ジの含水率を検出し、検出信号により作動する自動調節
弁を還流水送入管に設けてなる請求項2のスラッジ処理
装置。
3. The sludge treatment device according to claim 2, wherein the water content adjusting means detects the water content of the sludge to be press-fitted, and an automatic control valve which operates according to a detection signal is provided in the reflux water inlet pipe.
【請求項4】 上記第1および第2攪拌器が輸送配管途
中に組み込まれたスタティックミキサーである請求項2
または3のスラッジ処理装置。
4. The static mixer in which the first and second agitators are incorporated in the middle of the transportation pipe.
Or 3 sludge treatment device.
【請求項5】 上記凝集剤添加手段が凝集剤を流体と共
に輸送配管中へ圧入するための圧入機構を含んでなる請
求項2、3または4のスラッジ処理装置。
5. The sludge treatment device according to claim 2, wherein the coagulant addition means includes a press-fitting mechanism for press-fitting the coagulant together with the fluid into the transportation pipe.
【請求項6】 第2攪拌器に続いて前記輸送配管中の液
圧を減圧するための機構よりなる固形分凝集疎水手段を
更に含んでなる請求項2、3、4または5のスラッジ処
理装置。
6. The sludge treatment device according to claim 2, further comprising a solid content aggregating hydrophobic means comprising a mechanism for reducing the liquid pressure in the transportation pipe, following the second stirrer. .
【請求項7】 上記脱水/疎質体分離手段が直立型有孔
バスケット駆動式遠心脱水機と、該バスケット内壁に添
接される寸法を有し且つ上方が開口した袋状濾布と、該
袋状濾布を取り出して移送する運搬機構とよりなる請求
項1、2、3、4、5または6のスラッジ処理装置。
7. The dehydration / mesophilic material separating means comprises an upright basket driving centrifugal dehydrator having a hole, a bag-like filter cloth having a size to be attached to the inner wall of the basket and having an upper opening. The sludge treatment device according to claim 1, comprising a carrying mechanism for taking out and transferring the bag-shaped filter cloth.
【請求項8】 上記排水循環系が前記脱水/疎質体分離
手段より排出される分離水を捕集して前記含水率調整手
段及びスラッジ発生源へ還流させるための還流用配管と
送液ポンプとを含んでなる請求項1、2、3、4、5、
6または7のスラッジ処理装置。
8. A recirculation pipe and a liquid feed pump for collecting the separated water discharged from the dehydration / lysate separation means by the drainage circulation system and returning it to the water content adjusting means and the sludge generation source. Claims 1, 2, 3, 4, 5, comprising
6 or 7 sludge treatment device.
【請求項9】 スラッジが大量の水をプロペラントとし
て用いる土木工事現場より排出されるスライム、高含水
ヘドロ又はベントナイト排液であり、分離水を還流させ
る上記スラッジ発生源が工事用水タンクである請求項8
のスラッジ処理装置。
9. The sludge is a slime, a high water content sludge or a bentonite drainage discharged from a civil engineering construction site using a large amount of water as a propellant, and the sludge generation source for refluxing the separated water is a construction water tank. Item 8
Sludge treatment equipment.
【請求項10】 スラッジ輸送配管に、その入り口側か
ら、スラッジ圧入ポンプ、含水率を30重量%以上に調整
するための還流水送入管、第1管路攪拌器、凝集剤供給
管路、第2管路攪拌器、大径のリデューサーを順次配設
し、その出口側に、濾布袋体を装脱自在に装填した遠心
脱水機と濾布袋体を取り出し運搬する搬送機構とよりな
る脱水/疎質体分離手段を設け、脱水/疎質体分離手段
の排出する分離水を前記還流水送入管およびスラッジ発
生源へ還流する還流用配管を含む排水循環系を備えてな
ることを特徴とするスラッジ処理装置。
10. A sludge transport pipe, a sludge press-fitting pump, a reflux water inlet pipe for adjusting the water content to 30% by weight or more, a first pipe agitator, a flocculant supply pipe, from the inlet side thereof. A second pipe line stirrer and a large-diameter reducer are sequentially arranged, and at the outlet side thereof, a centrifugal dehydrator in which a filter cloth bag is detachably loaded and a transport mechanism for taking out and carrying the filter cloth bag are carried out. A sparse substance separating means is provided, and a drainage circulation system is provided which includes the reflux water inlet pipe and the return pipe for returning the separated water discharged from the dehydrating / sparse substance separating means to the sludge generation source. Sludge treatment equipment that does.
JP06507194A 1994-04-01 1994-04-01 Sludge treatment equipment Expired - Lifetime JP3234710B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP06507194A JP3234710B2 (en) 1994-04-01 1994-04-01 Sludge treatment equipment

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP06507194A JP3234710B2 (en) 1994-04-01 1994-04-01 Sludge treatment equipment

Publications (2)

Publication Number Publication Date
JPH07265900A true JPH07265900A (en) 1995-10-17
JP3234710B2 JP3234710B2 (en) 2001-12-04

Family

ID=13276361

Family Applications (1)

Application Number Title Priority Date Filing Date
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Country Link
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WO1998049108A1 (en) * 1997-04-30 1998-11-05 Ciba Specialty Chemicals Water Treatments Limited Dewatering of sewage sludge
FR2844784A1 (en) * 2002-09-24 2004-03-26 Ondeo Degremont Wastewater treatment comprises contacting sludge from a membrane bioreactor with water from a dewatering unit to transfer polyelectrolyte from the water to the sludge before recycling the water
JP2007190523A (en) * 2006-01-20 2007-08-02 Ps Mitsubishi Construction Co Ltd Bagging and dewatering method and its equipment
JP2010201309A (en) * 2009-03-02 2010-09-16 Daiyanitorikkusu Kk Treatment method of water to be treated containing inorganic sludge
ITCE20090010A1 (en) * 2009-10-28 2011-04-29 Luigi Antonio Pezone AUTOBOTTE FOR ESPURGHI WITH DEHYDRATION AND CHEMICAL STABILIZATION OF SLUDGE WITH SOCCER POWDERS
JP2013017960A (en) * 2011-07-12 2013-01-31 Kowa:Kk Bag body for dehydration
JP2015112515A (en) * 2013-12-10 2015-06-22 中国電力株式会社 Sludge recycling method
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Cited By (15)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO1998049108A1 (en) * 1997-04-30 1998-11-05 Ciba Specialty Chemicals Water Treatments Limited Dewatering of sewage sludge
AU733771B2 (en) * 1997-04-30 2001-05-24 Ciba Specialty Chemicals Water Treatments Limited Dewatering of sewage sludge
US6447687B1 (en) * 1997-04-30 2002-09-10 Ciba Specialty Chemcials Water Treatments Ltd. Dewatering of sewage sludge
FR2844784A1 (en) * 2002-09-24 2004-03-26 Ondeo Degremont Wastewater treatment comprises contacting sludge from a membrane bioreactor with water from a dewatering unit to transfer polyelectrolyte from the water to the sludge before recycling the water
WO2004028986A3 (en) * 2002-09-24 2004-05-13 Degremont Membrane bioreactor waste water treatment method
US7135115B2 (en) 2002-09-24 2006-11-14 Degremont Membrane bioreactor waste water treatment method
CN1293001C (en) * 2002-09-24 2007-01-03 底格里蒙公司 Wastewater treatment method by membrane bioreactor
JP2007190523A (en) * 2006-01-20 2007-08-02 Ps Mitsubishi Construction Co Ltd Bagging and dewatering method and its equipment
JP2010201309A (en) * 2009-03-02 2010-09-16 Daiyanitorikkusu Kk Treatment method of water to be treated containing inorganic sludge
ITCE20090010A1 (en) * 2009-10-28 2011-04-29 Luigi Antonio Pezone AUTOBOTTE FOR ESPURGHI WITH DEHYDRATION AND CHEMICAL STABILIZATION OF SLUDGE WITH SOCCER POWDERS
JP2013017960A (en) * 2011-07-12 2013-01-31 Kowa:Kk Bag body for dehydration
JP2015112515A (en) * 2013-12-10 2015-06-22 中国電力株式会社 Sludge recycling method
JP2016036798A (en) * 2014-08-11 2016-03-22 志郎 中村 Dewatering bag and dewatering apparatus using the same
CN106927661A (en) * 2017-04-26 2017-07-07 湖州中呈科技有限公司 A kind of riverway sludge dehydrating and curing device
CN107226598A (en) * 2017-08-03 2017-10-03 福建润土工程科技有限公司 One-stop mud disposal system

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