JPS6082198A - Heat dehydration method of sludge - Google Patents

Heat dehydration method of sludge

Info

Publication number
JPS6082198A
JPS6082198A JP58190144A JP19014483A JPS6082198A JP S6082198 A JPS6082198 A JP S6082198A JP 58190144 A JP58190144 A JP 58190144A JP 19014483 A JP19014483 A JP 19014483A JP S6082198 A JPS6082198 A JP S6082198A
Authority
JP
Japan
Prior art keywords
sludge
cake
dehydrated
heating
dehydration
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
JP58190144A
Other languages
Japanese (ja)
Other versions
JPH0310400B2 (en
Inventor
Masanobu Shigaki
志垣 政信
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.)
Takuma Co Ltd
Original Assignee
Takuma Co Ltd
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 Takuma Co Ltd filed Critical Takuma Co Ltd
Priority to JP58190144A priority Critical patent/JPS6082198A/en
Publication of JPS6082198A publication Critical patent/JPS6082198A/en
Publication of JPH0310400B2 publication Critical patent/JPH0310400B2/ja
Granted legal-status Critical Current

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  • Treatment Of Sludge (AREA)

Abstract

PURPOSE:To dehydrate easily and economically sludge with small energy consumption by heating primarily dehydrated cake with a heat treating device then supplying the cake in the state of the high temp. to a secondary dehydrating device in succession thereto and subjecting again the cake to a dehydration treatment. CONSTITUTION:The thickened sludge 1 charged through an inlet 5 is delivered into a filter cloth belt 10 by passing through a sludge mixing tank 6 and a sludge pool 7. The sludge is sandwiched between filter cloth belts 10 and 11 and is fed to a belt compression zone 12 where the sludge is compressed and dehydrated. The primarily dehydrated cake 2 contg. about 80% water is dripped between heating rollers 14 and heating jacket plates 15 constituting a heater (C) and is heated approximately to 70 deg.C while the cake falls between the rollers 14 and the plates 15. The heated and primarily dehydrated cake 3 is discharged into the spacing between a press rotor 19 of a secondary dehydrator 16 and an endless tracked filter cloth 18 and is compressed and dehydrated by the turning thereof, by which secondarily dehydrated cake contg. 50% water is obtd.

Description

【発明の詳細な説明】 本発明は、下水処理施設等より排出されるllテ泥の処
理方法の改良に関する。
DETAILED DESCRIPTION OF THE INVENTION The present invention relates to an improvement in a method for treating sludge discharged from sewage treatment facilities and the like.

近年、下水道の普及と共に下水処理施設から排出される
汚泥脅も急激に増加し、その処理に関して様々な問題が
生している。即ち、排出される汚泥の大部分は、単に脱
水処理をしただけで埋立処理されているため、環境汚染
、埋立地の後利用、埋立用地の確保等の点に多くの厄介
な問題が起生じている。
In recent years, with the spread of sewage systems, the amount of sludge discharged from sewage treatment facilities has increased rapidly, and various problems have arisen regarding its treatment. In other words, most of the discharged sludge is simply dehydrated and then disposed of in a landfill, which causes many troublesome problems such as environmental pollution, subsequent use of the landfill, and securing land for the landfill. ing.

一方、汚泥ケーキの埋立処理に代る方法として、脱水処
■(1シた後の汚泥ケーキを流動炉や多段炉を用いて焼
却したり、或いは排出されてきた濃縮llj泥を酊接1
70℃前後の高温度にまで加熱して脱水したあと、これ
を焼却するという処理方法が開発されている。例えば、
濃縮汚泥100 To nを焼却処理すれば、燃焼残滓
は約lT0nとなってその減容・↑くが’/100とな
り、その結果必要な埋立地面積が少なくなるうえ、汚泥
が完全に無機化されているため後地利用や環境汚染上の
問題も発生せす、極めて好都合である。
On the other hand, as an alternative to landfill treatment of sludge cake, there are methods such as incinerating the sludge cake after dehydration using a fluidized bed furnace or multistage furnace, or incinerating the concentrated sludge that has been discharged.
A treatment method has been developed in which water is heated to a high temperature of around 70°C to dehydrate it and then incinerated. for example,
If 100 Ton of thickened sludge is incinerated, the combustion residue will be approximately 1T0n, and its volume will be reduced to ↑Kuga'/100.As a result, not only will the required landfill area be reduced, but the sludge will be completely mineralized. This is extremely advantageous as it does not cause problems regarding land use or environmental pollution.

而して、前者の場合には、通常汚水処理施設等′から排
出されて来た濃縮汚泥(水分約97%)を脱水機にかけ
て脱水し、水分が75〜80%の脱水ケーキとしたあと
流動炉等によりこれを焼却するようにしている。
In the former case, the concentrated sludge (approximately 97% water content) discharged from sewage treatment facilities is dehydrated using a dehydrator to form a dehydrated cake with a water content of 75 to 80%, and then the fluidized sludge is dehydrated. This is incinerated using a furnace or the like.

然し乍ら、75〜80%の水分を有する脱水ケーキをそ
のまま焼却するためには、多量の浦等による助燃を必要
とし、処理コストか著しく高くつくという問題がある。
However, in order to incinerate the dehydrated cake having a water content of 75 to 80% as it is, a large amount of auxiliary combustion is required, which raises the problem of extremely high processing costs.

尚、前記脱水ケーキを直接焼却せずに予備乾燥をし、そ
の後焼却炉で自燃させる方法も採られているが、脱水ケ
ーキの水分が70〜80%もあると何れにしても絶対熱
量が不足し、相当の油等による助燃を必要とすることに
なる。
In addition, a method has been adopted in which the dehydrated cake is not directly incinerated, but is pre-dried and then self-combusted in an incinerator, but if the moisture content of the dehydrated cake is 70 to 80%, the absolute amount of heat is insufficient in any case. However, it requires a considerable amount of auxiliary combustion with oil, etc.

一方、後者の所謂汚泥熱処理方式に於いては、通常汚水
処理施設等から排出されてくる濃縮汚泥(水分約97%
)を約160〜175℃の温度に加熱して脱水した後、
更にこの汚泥を脱水機にかけて脱水し、水分か略50%
程度の脱水ケーキとしたうえこ′A1を焼却するように
している。
On the other hand, in the latter so-called sludge heat treatment method, concentrated sludge (water content approximately 97%
) to a temperature of about 160-175°C to dehydrate it,
Furthermore, this sludge is dehydrated by a dehydrator, and the water content is approximately 50%.
Ueko'A1 is incinerated as a dehydrated cake.

しかし、水分が97%もある濃縮汚泥を約160℃〜1
75℃の温度に加熱するためには相当の熱量を必要とす
るうえ、反応器を中心にして第一熱交換器、第二熱交換
器、蒸発器、熱処理lljl濃泥槽、熱処理汚泥貯留槽
及びフィルタープレス型脱水機等を必要とし、処理装置
か複雑となって設備費や運転費の低減を図り難いという
問題がある。
However, when thickened sludge with a moisture content of 97% is heated to about 160°C
In order to heat to a temperature of 75℃, a considerable amount of heat is required, and around the reactor, there are a first heat exchanger, a second heat exchanger, an evaporator, a heat treatment thick sludge tank, and a heat treatment sludge storage tank. This method requires a filter press type dehydrator and the like, making the processing equipment complicated and making it difficult to reduce equipment costs and operating costs.

本発明は゛、従前の汚泥の焼却処理に於ける上述の如き
問題の解決を課題とするものであり、より少ないエネル
ギー消費でもって最も簡単且つ経済的に汚泥を脱水し、
汚泥焼却処理費の大幅な削減を可能とした汚泥の加熱脱
水方法の提供を目的とするものである。
The present invention aims to solve the above-mentioned problems in the conventional sludge incineration process, and dewaters sludge in the simplest and most economical way with less energy consumption.
The purpose of this invention is to provide a method for heating and dewatering sludge that enables a significant reduction in sludge incineration processing costs.

ところで、汚泥の焼却処理に於いて、その経済性に最も
深く関係する因子は汚泥の脱水率である。
By the way, in the incineration treatment of sludge, the factor most closely related to the economic efficiency is the dewatering rate of the sludge.

汚泥は一般に有機質と無機質とから成立っており、通常
有機質が50〜80%を占めている。又、11,7泥内
の有機質や無機質は、水と親和性の極めて強い才0子径
が帆1〜0.001μのコロイド状となっており、個々
の粒子の繋りの中に水分を包含したゲル構造を呈してい
る。その結果、前記粒子と水分との分離が著しく困難と
なり、脱水機のみては経済的な脱水が難かしい。
Sludge is generally composed of organic matter and inorganic matter, with organic matter usually accounting for 50 to 80%. In addition, the organic and inorganic substances in the 11,7 mud are in the form of a colloid with a grain diameter of 1 to 0.001 μm, which has an extremely strong affinity for water. It exhibits an enclosed gel structure. As a result, it becomes extremely difficult to separate the particles from water, making it difficult to perform economical dehydration using only a dehydrator.

一方、汚泥を加熱した場合には、汚泥内蛋白質の熱変形
により、卵白が加熱されると固まる現象に類似して前記
各粒子が粗大化すると共に、加熱によって前記ゲル構造
が破壊されて汚泥粒子に囲まれていた水分が抜は出し易
くなり、脱水性が著しく向上することになる。
On the other hand, when sludge is heated, the particles in the sludge become coarse due to thermal deformation of the proteins in the sludge, similar to the phenomenon in which egg white solidifies when heated, and the gel structure is destroyed by heating, causing the sludge particles to become coarse. This makes it easier for the water that was surrounded by the water to come out, resulting in a marked improvement in dehydration performance.

の組合せ並ひに加熱処理温度条件について数多く解析を
繰返し、その結果から汚泥を焼却処理する際の最も簡単
且つ経済的な汚泥の加熱脱水方法を見出したものである
After repeated analysis of various combinations of sludge and heat treatment temperature conditions, the authors discovered the simplest and most economical method for heating and dehydrating sludge when incinerating sludge.

本願発明は、?’j水処理施設等から排出されてくる濃
縮汚泥を先ず一次脱水機により脱水して減量し、次に一
次脱水機からの脱水ケーキを加熱装置により加熱処理し
て〆η泥のゲル状構造を破壊すると共に汚泥の粘度を低
下させ、更に前記高温低粘度状態の一次脱水ケーキを二
次脱水機によって脱水することを発明の基本構成とする
ものである。
What is the claimed invention? 'j Thickened sludge discharged from water treatment facilities, etc. is first dehydrated using a primary dehydrator to reduce its weight, and then the dehydrated cake from the primary dehydrator is heat-treated using a heating device to remove the gel-like structure of the mud. The basic structure of the invention is to destroy the sludge and lower the viscosity of the sludge, and further dewater the primary dewatered cake in the high temperature, low viscosity state using a secondary dehydrator.

以下、第1図及び第2図に基づいて本発明を詳説する。Hereinafter, the present invention will be explained in detail based on FIGS. 1 and 2.

第1図は本発明に係る汚泥の加熱脱水方法の処理系統図
であり、11ノ水処理施設八より排出されてきた濃縮汚
泥1は先ず一次脱水処理装置B”C脱水処理される。通
常前記濃縮汚泥1は水分含有率が97%位いであり、ベ
ルトプレス型脱水機等により脱水処理された一次脱水ケ
ーキ2の水分含有率は、約80%位いに低下する。即ち
、例えばIQQ tonの濃縮汚泥1は水分97 to
nと固形分3L l)+1から成り立っており、−次脱
水処理された後の一次脱水ケーキ2の成分は固形分3 
LOllと水分12、Lonとなり、総重量は略15 
Lonとなる。
FIG. 1 is a treatment system diagram of the sludge heating dehydration method according to the present invention, in which the thickened sludge 1 discharged from water treatment facility No. The water content of the thickened sludge 1 is about 97%, and the water content of the primary dehydrated cake 2 that has been dehydrated using a belt press type dehydrator or the like decreases to about 80%. Thickened sludge 1 has 97 to
n and solid content 3L l) + 1, and the components of the primary dehydrated cake 2 after the -stage dehydration treatment are solid content 3L + 1.
LOll, moisture 12, Lon, total weight is approximately 15
It becomes Lon.

脱水処理された後の一次脱水ケーキ2は、引き続き加熱
処理装置Cへ移送され、ここで略60℃〜90℃の温度
に加熱される。例えば、水分含有率が80%位いの一次
脱水ケーキ2を略70℃に加熱すると、低温状態に於い
て完全なゲル状を呈していた6泥のゲル構造が略完全に
破壊され、−次脱水ケーキ2の粘度が著しく低下する。
The primary dehydrated cake 2 that has been subjected to the dehydration treatment is subsequently transferred to a heat treatment device C, where it is heated to a temperature of approximately 60°C to 90°C. For example, when primary dehydrated cake 2 with a water content of about 80% is heated to about 70°C, the gel structure of mud 6, which had a perfect gelatinous state at low temperatures, is almost completely destroyed, and - The viscosity of the dehydrated cake 2 is significantly reduced.

尚、−次脱水ケーギ2の加熱温度は略60℃以上の温度
を必要とし、それ以下の温度では前記汚泥のゲル構造が
十分に破壊されず、その結果汚泥粒子間に包み込まれて
いる水分の放出が不十分となって、二次脱水処理に於け
る脱水率の向上か著しく困難になる。
The heating temperature of the secondary dehydration cage 2 needs to be approximately 60°C or higher; if the temperature is lower than that, the gel structure of the sludge will not be sufficiently destroyed, and as a result, the water trapped between the sludge particles will be removed. The release becomes insufficient, making it extremely difficult to improve the dehydration rate in the secondary dehydration process.

加熱処理装置Cで略60℃〜90℃の温度に加熱された
高温の一次脱水ケーキ3は、引き続き高温状態を保った
まま二次脱水処理装置りへ送られ、ここで更に脱水処理
される。例えば、略70℃に加熱された水分含有率80
%の一次脱水ケーキ3は、キャタピラ−プレス型脱水機
等によって水分含有率が50%位いにまで容易に脱水さ
れることになり、二次脱水ケーキ4の総重量は6ton
 (水分3【On、固形分3 ron )となる。
The high-temperature primary dehydrated cake 3 heated to a temperature of approximately 60° C. to 90° C. in the heat treatment device C is then sent to the secondary dehydration treatment device while maintaining the high temperature state, where it is further dehydrated. For example, water content 80% heated to approximately 70°C
% primary dehydrated cake 3 can be easily dehydrated to a water content of about 50% using a caterpillar press dehydrator or the like, and the total weight of the secondary dehydrated cake 4 is 6 tons.
(Moisture 3 [On, solid content 3 ron).

二次脱水処理袋cIDから排出される二次脱水ケーキ4
は、前述の如く水分が50%位いにまで低下しているた
め、ストーカ炉等ても高温自燃か可能てあり、相当量の
熱回収が可能となって、汚泥焼却発電等を行なうことも
できる。
Secondary dehydration cake 4 discharged from secondary dehydration treatment bag cID
As mentioned above, since the water content has been reduced to about 50%, high-temperature self-combustion is possible even in stoker furnaces, and a considerable amount of heat can be recovered, making it possible to generate electricity by sludge incineration. can.

第2図は、本発明の実施に使用する汚泥加熱脱水処理装
置の縦断面図であり、図に於いて5は汚泥人「1.6は
汚泥混和槽、7はスラッジプール、8は排水口、9はベ
ルトプレス型−次脱水機、10゜11は圧縮用炉布ベル
ト、12はベルト圧縮ゾーン、13はP布洗浄装置、1
4は加熱ローラ、15は加熱ジャケットプレート、16
はキャタピラ−プレス型二次脱水機ζ17は加圧キャタ
ピラ−118はキャタピラ−炉布、19はロータ、20
はロータル布、21は排水口、22は二次脱水ケーキの
出口である。
FIG. 2 is a longitudinal cross-sectional view of the sludge heating and dewatering equipment used in the implementation of the present invention. , 9 is a belt press-type secondary dehydrator, 10° 11 is a compression furnace cloth belt, 12 is a belt compression zone, 13 is a P cloth cleaning device, 1
4 is a heating roller, 15 is a heating jacket plate, 16
17 is a caterpillar press type secondary dehydrator, 118 is a caterpillar furnace cloth, 19 is a rotor, 20
21 is a rotary cloth, 21 is a drain port, and 22 is an outlet for the secondary dewatering cake.

入口5から投入された濃縮汚泥1は、汚泥混和4311
5及びスラッジプール7を通してp布ベルト1゜上へ繰
り出され、F布ベル) 10 、11の間に挾まれた状
態でベルト圧縮ゾーン12へ送られ、ここで圧縮脱水が
行なわれる。ベルト圧縮ゾーン12で水分含有率が80
%位いにまで脱水された一次脱水ケーキ2は、引き続き
加熱装置Cを構成する加熱ローラ14と加熱ジャケット
プレー目5の間へ落下され、ローラ14とプレート15
間を落下する間に略7o℃位いに加熱される。加熱され
た高温の一次脱水ケーキ3は、引き続き二次脱水機16
のプレスロータ19とキャタピラ−F布18間へ排出さ
れ、キャタピラ−17とロータ19の回動により圧縮脱
水されたあと、略水分含有率が50%の二次脱水ケーキ
4となってケーキ出口22より排出される。
The thickened sludge 1 introduced from the inlet 5 is mixed with sludge 4311
5 and sludge pool 7 onto the P fabric belt 1°, and is sent to the belt compression zone 12 while being sandwiched between the F fabric belts 10 and 11, where it is compressed and dewatered. Moisture content in belt compression zone 12 is 80
The primary dehydrated cake 2, which has been dehydrated to approximately
While falling through the gap, it is heated to about 7oC. The heated high-temperature primary dehydration cake 3 is then sent to the secondary dehydration machine 16.
is discharged between the press rotor 19 and the caterpillar F cloth 18, and after being compressed and dehydrated by the rotation of the caterpillar 17 and rotor 19, it becomes a secondary dehydrated cake 4 with a water content of approximately 50% and is delivered to the cake outlet 22. more excreted.

本発明に於いては、前述の通り濃縮汚泥1を一次脱水処
理装置Bで脱水し、その−次脱水ケーキ2を加熱装置C
で60℃〜90℃に加熱したあと。
In the present invention, as described above, the concentrated sludge 1 is dehydrated in the primary dehydration treatment device B, and the dehydrated cake 2 is then transferred to the heating device C.
After heating to 60℃~90℃.

二次脱水処理袋UDで脱水するようにしているため、多
くの秀れた効用を発揮することができる。
Since the water is dehydrated in the secondary dehydration treatment bag UD, it can exhibit many excellent effects.

先ず、濃縮汚泥1を一次脱水処理したあと、その−次脱
水ケーキ2を加熱するようにしているため、加熱に要す
る熱■を著しく低減することができる。例えば、濃縮汚
泥(水分97%)1が100tonの場合、−次脱水ケ
ーキ(水分80%)2の総1−11は15Lonとなり
、これを70℃に加熱するのに必要な熱量は約9QQ、
QQQ Kcal (15X 103u/、 X (7
O−10)℃)となる。これに対して、100 ton
の濃縮汚泥1を直接70℃まで加熱する場合には、約6
.000,000Kcal (100X 10”J’/
HX (7010)℃)の熱量を必要とすることになり
、−次局水処理を行なうことにより加熱に要する熱量を
略1/6.7に減少せしめ得る。
First, after the concentrated sludge 1 is subjected to primary dehydration treatment, the secondary dehydration cake 2 is heated, so that the heat required for heating can be significantly reduced. For example, if the concentrated sludge (moisture 97%) 1 is 100 tons, the total 1-11 of the secondary dehydration cake (moisture 80%) 2 is 15Lon, and the amount of heat required to heat this to 70℃ is approximately 9QQ,
QQQ Kcal (15X 103u/, X (7
O-10)°C). On the other hand, 100 tons
When directly heating the thickened sludge 1 to 70℃, approximately 6
.. 000,000Kcal (100X 10"J'/
The amount of heat required for heating can be reduced to about 1/6.7 by performing subsequent water treatment.

また、−次脱水ケーキ(水分80%、総重量15ron
 ) 2を70℃に加熱したあと、二次脱水処理を行な
って水分50%の二次脱水ケーキ4を得る場合には、必
要な熱量は前述の如く約900.000 Kcalとな
る。どれに対して、従前の如く加熱乾燥方式により一次
脱水ケーキ2(水分80%、総量15 【on )の水
分を蒸発させ、その含水率を50%とする場合には、9
 LOn (12t−3L ’)の水分を蒸発させる必
要があり、必要とする熱量は約s 、940.000 
Kca l(9000’P X 600 ””l/EP
 +(3000+ 3000 ) Ky7cx(100
−1,0)℃)となり、本発明に比較して約6.6倍の
熱量を要することになる。
In addition, - dehydrated cake (moisture 80%, total weight 15ron)
) 2 to 70° C. and then perform a secondary dehydration treatment to obtain the secondary dehydrated cake 4 with a water content of 50%, the required amount of heat is approximately 900.000 Kcal as described above. On the other hand, if the water content of the primary dehydrated cake 2 (80% moisture, total amount 15 on) is evaporated by the conventional heating drying method and the water content is 50%, 9
It is necessary to evaporate the moisture of LOn (12t-3L'), and the amount of heat required is approximately s, 940.000
Kcal (9000'P x 600 ""l/EP
+(3000+3000) Ky7cx(100
-1.0)°C), which means that approximately 6.6 times as much heat is required as compared to the present invention.

この様に、本発明に於いては一次脱水と加熱と二次脱水
の紹み合せとすることにより、従前の他の如何なる脱水
方式よりも脱水に要する熱間が少なくなり、熱経済性に
秀れている。
As described above, in the present invention, by combining primary dehydration, heating, and secondary dehydration, the hot time required for dehydration is smaller than any other conventional dehydration method, and it has excellent thermoeconomic efficiency. It is.

更に本発明に於いては、−次局水処理したあとの一次脱
水ケーキを60℃〜90℃に加熱し、そのゲル構造を破
壊すると同時に約60℃〜90℃の高温のままで二次脱
水を行なうようにしているため、汚泥の粘度も著しく低
下して水分と固形分の分離が容易となり、通常のキャタ
ピラ−プレス型脱水機等によって極めて簡単に、脱水ケ
ーキの水分含有率を約50%程度にまで落すことができ
る。
Furthermore, in the present invention, the primary dehydration cake after the secondary water treatment is heated to 60°C to 90°C to destroy its gel structure, and at the same time, the secondary dehydration is carried out at a high temperature of approximately 60°C to 90°C. As a result, the viscosity of the sludge is significantly reduced, making it easy to separate water and solids, and the moisture content of the dehydrated cake can be reduced to approximately 50% using a regular caterpillar press type dehydrator. It can be reduced to a certain extent.

そのうえ、本発明では加熱した−次脱水ケーキを高Wu
’+のままで二次脱水処理するようlこしているため、
処理装置自体も必然的に一次脱水機と加熱器と二次脱水
機を一体化した構成とする方が望ましく、その結果処理
装置を極めてコンパクトなものにすることができ、設備
費の大幅な削減が可能となる。
Moreover, in the present invention, the heated -sub-dehydrated cake has a high Wu
Because it is filtered as it is for secondary dehydration treatment,
It is naturally desirable for the processing equipment itself to have a configuration that integrates the primary dehydrator, heater, and secondary dehydrator, and as a result, the processing equipment can be made extremely compact, resulting in a significant reduction in equipment costs. becomes possible.

【図面の簡単な説明】[Brief explanation of the drawing]

第1図は本発明による汚泥の加熱脱水処理の系統図であ
る。 第2図は、本発明の実施に使用する汚泥の加熱脱水処理
装置の縦断面図である。 13 −次局水処理装置 C加熱処理装置 D 二次脱水処理装置 1 濃縮汚泥 2−次脱水ケーキ 3 高温−次脱水ケーキ 4 二次脱水ケーキ 特許出願人 株式会社 タ り マ 代表者 福 1)順 吉
FIG. 1 is a system diagram of the heating dehydration treatment of sludge according to the present invention. FIG. 2 is a longitudinal cross-sectional view of a sludge heating dehydration treatment apparatus used in the implementation of the present invention. 13 - Secondary water treatment device C Heat treatment device D Secondary dehydration treatment device 1 Concentrated sludge secondary dehydration cake 3 High temperature secondary dehydration cake 4 Secondary dehydration cake Patent applicant Tarima Co., Ltd. Representative Fuku 1) Order Kichi

Claims (1)

【特許請求の範囲】[Claims] 汚水処理施設(Δ)等から排出された汚泥(1)を先ず
一次脱水処理装置(B)によって脱水処理し、次に前記
脱水処理により減量せしめた一次脱水ケーキ(2)を加
熱処理装置(C)によって加熱し、加熱により昇温ぜし
めた一次脱水ケーキ(3)を引き続き高温のまま二次脱
水処理装置(D)へ供給し、m度脱水処理することを特
徴とする汚泥の加熱脱水 カン犬 。
Sludge (1) discharged from a sewage treatment facility (Δ), etc. is first dehydrated in a primary dehydration treatment device (B), and then the primary dehydration cake (2) whose weight has been reduced through the dehydration treatment is transferred to a heat treatment device (C). ), and the primary dehydration cake (3), whose temperature has been raised by heating, is then supplied to the secondary dehydration treatment device (D) while still at high temperature, and is subjected to m-degree dehydration treatment. dog .
JP58190144A 1983-10-11 1983-10-11 Heat dehydration method of sludge Granted JPS6082198A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP58190144A JPS6082198A (en) 1983-10-11 1983-10-11 Heat dehydration method of sludge

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP58190144A JPS6082198A (en) 1983-10-11 1983-10-11 Heat dehydration method of sludge

Publications (2)

Publication Number Publication Date
JPS6082198A true JPS6082198A (en) 1985-05-10
JPH0310400B2 JPH0310400B2 (en) 1991-02-13

Family

ID=16253132

Family Applications (1)

Application Number Title Priority Date Filing Date
JP58190144A Granted JPS6082198A (en) 1983-10-11 1983-10-11 Heat dehydration method of sludge

Country Status (1)

Country Link
JP (1) JPS6082198A (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR20010047226A (en) * 1999-11-18 2001-06-15 박재황 A sludge drying machine of washing system for inductrial
KR101103625B1 (en) 2010-05-19 2012-01-09 강영범 Industry dehydration device of two-stage both sides dry method

Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS501547A (en) * 1973-05-11 1975-01-09
JPS55116500A (en) * 1979-03-02 1980-09-08 Kogyo Kaihatsu Kenkyusho Treating method for sludge
JPS5710398A (en) * 1980-06-23 1982-01-19 Ebara Infilco Co Ltd Treatment of muddy substance

Patent Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS501547A (en) * 1973-05-11 1975-01-09
JPS55116500A (en) * 1979-03-02 1980-09-08 Kogyo Kaihatsu Kenkyusho Treating method for sludge
JPS5710398A (en) * 1980-06-23 1982-01-19 Ebara Infilco Co Ltd Treatment of muddy substance

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR20010047226A (en) * 1999-11-18 2001-06-15 박재황 A sludge drying machine of washing system for inductrial
KR101103625B1 (en) 2010-05-19 2012-01-09 강영범 Industry dehydration device of two-stage both sides dry method

Also Published As

Publication number Publication date
JPH0310400B2 (en) 1991-02-13

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