JPS6238604B2 - - Google Patents

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Publication number
JPS6238604B2
JPS6238604B2 JP8479479A JP8479479A JPS6238604B2 JP S6238604 B2 JPS6238604 B2 JP S6238604B2 JP 8479479 A JP8479479 A JP 8479479A JP 8479479 A JP8479479 A JP 8479479A JP S6238604 B2 JPS6238604 B2 JP S6238604B2
Authority
JP
Japan
Prior art keywords
chamber
sludge
drying chamber
incineration
drying
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.)
Expired
Application number
JP8479479A
Other languages
Japanese (ja)
Other versions
JPS5610616A (en
Inventor
Hiroshi Shimizu
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.)
Kubota Corp
Original Assignee
Kubota Corp
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 Kubota Corp filed Critical Kubota Corp
Priority to JP8479479A priority Critical patent/JPS5610616A/en
Publication of JPS5610616A publication Critical patent/JPS5610616A/en
Publication of JPS6238604B2 publication Critical patent/JPS6238604B2/ja
Granted legal-status Critical Current

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  • Fluidized-Bed Combustion And Resonant Combustion (AREA)
  • Gasification And Melting Of Waste (AREA)

Description

【発明の詳細な説明】 この発明は、乾燥室と焼却室とを一体化した有
機性汚泥処理装置に関する。
DETAILED DESCRIPTION OF THE INVENTION The present invention relates to an organic sludge treatment apparatus that integrates a drying chamber and an incineration chamber.

流動層式焼却装置によつて脱水された下水、し
尿等の有機性汚泥を焼却する場合、汚泥中の含水
量が高いと汚泥が流動しにくいため、焼却炉を大
きく、かつ流動用空気量を多くせねばならず、装
置が大型化する。そこで、従来汚泥を脱水処理後
乾燥して焼却炉に送り込む装置が考案されている
が、乾燥装置と焼却装置を別体にしているため、
熱効率が悪いうえに設備も複雑大型化している。
When incinerating organic sludge such as sewage or human waste that has been dehydrated using a fluidized bed incinerator, the high water content of the sludge makes it difficult for the sludge to flow, so the incinerator must be large and the amount of air for fluidization must be increased. Therefore, the device becomes larger. Therefore, conventional equipment has been devised that dehydrates the sludge, dries it, and sends it to the incinerator, but since the drying equipment and incinerator are separate,
In addition to poor thermal efficiency, the equipment is also complex and large.

この発明は、乾燥と焼却とを1つの炉内で行な
い、熱効率が高くかつコンパクトな有機性汚泥処
理装置を提供することを目的とする。
An object of the present invention is to provide a compact organic sludge treatment apparatus that performs drying and incineration in one furnace and has high thermal efficiency.

この目的を達成するため、この発明にあつて
は、脱水された有機性汚泥が送り込まれる乾燥室
と乾燥室からの汚泥が送り込まれる焼却室と、乾
燥室への給気と焼却室からの排気とを熱交換する
熱交換部とを炉内に形成し、上記乾燥室は熱交換
部を介し焼却部の上側に連続して位置し、乾燥室
の上部から焼却室の下部に噴流用空気ダクトを設
け、焼却室と乾燥室とを熱交換部を通つて連通す
る汚泥落下用第1オーバーフロー管を設けるとと
もに、焼却室内から炉下方に灰取出用第2オーバ
ーフロー管を設けた構成としたのである。
In order to achieve this purpose, the present invention includes a drying chamber into which dehydrated organic sludge is sent, an incineration chamber into which sludge from the drying room is sent, and air supply to the drying room and exhaust air from the incineration chamber. A heat exchange section for exchanging heat with the incineration chamber is formed in the furnace, and the drying chamber is located continuously above the incineration section via the heat exchange section, and a jet air duct is provided from the top of the drying chamber to the bottom of the incineration chamber. A first overflow pipe for dropping sludge was provided to communicate the incineration chamber and drying chamber through the heat exchange section, and a second overflow pipe for removing ash was provided below the furnace from the incineration chamber. .

この様に構成される有機性汚泥処理装置は、脱
水された汚泥が乾燥室に送り込まれると、熱交換
部にて過熱された給気によつてその汚泥が流動さ
れて乾燥する。この流動乾燥時、汚泥は、徐々に
乾燥して粒形が小さく軽くなつて乾燥室の上方に
移動し、第1オーバーフロー管から焼却室に落下
する。
In the organic sludge treatment apparatus configured in this manner, when dehydrated sludge is sent into the drying chamber, the sludge is fluidized and dried by the supply air superheated in the heat exchange section. During this fluidized drying, the sludge gradually dries, becomes smaller and lighter, moves to the upper part of the drying chamber, and falls into the incineration chamber from the first overflow pipe.

一方、汚泥から水分を吸収して乾燥室の上部に
至つた排ガス(給気)は空気ダクトを通つて焼却
室の下部から内部に噴出する。この噴出により、
第1オーバーフロー管からの汚泥が流動するとと
もに、バーナ等により焼却され、この焼却された
汚泥灰は第2オーバーフロー管から炉外に排出さ
れる。
On the other hand, exhaust gas (supply air) that absorbs water from the sludge and reaches the upper part of the drying chamber passes through the air duct and is ejected from the lower part of the incineration chamber into the interior. This eruption causes
The sludge from the first overflow pipe flows and is incinerated by a burner or the like, and the incinerated sludge ash is discharged out of the furnace from the second overflow pipe.

以下、この発明の実施例を添付図面に基づいて
説明する。
Embodiments of the present invention will be described below with reference to the accompanying drawings.

図に示すように、この発明の処理装置Aは、炉
1内に形成した乾燥室2、焼却室3および熱交換
部4より成り、焼却室3の上に熱交換部4、熱交
換部4の上に乾燥室2が連続して位置している。
As shown in the figure, the processing apparatus A of the present invention consists of a drying chamber 2, an incineration chamber 3, and a heat exchange section 4 formed in a furnace 1; A drying chamber 2 is located continuously above.

上記乾燥室2には汚泥送り込み装置10が備え
られており、この送り込み装置10はスクリユー
コンベア11と脱水処理の終了した汚泥をスクリ
ユーコンベア11に供給するフイダー12とから
構成され、スクリユーコンベア11の作動によつ
て汚泥が乾燥室2の下部に送り込まれる。
The drying chamber 2 is equipped with a sludge feeding device 10, which is composed of a screw conveyor 11 and a feeder 12 that supplies the sludge that has been dehydrated to the screw conveyor 11. 11 causes the sludge to be sent to the lower part of the drying chamber 2.

乾燥室2と熱交換部4とは多孔板5によつて区
画され、熱交換部4は、一端が分散管23を介し
て給気ダクト24に接続され他端が乾燥室2に連
通された複数の熱交換管22によつて構成されて
おり、熱交換部4において送風機により送られて
きた給気と焼却室3からの排気とが熱交換して、
熱風が乾燥室2に噴出する。また、熱交換部4に
は、乾燥室2と焼却室3とに連通する複数の第1
オーバフロー管25が設けられ、乾燥室2から乾
燥した汚泥がこのオーバフロー管25を通つて焼
却室3に落下する。
The drying chamber 2 and the heat exchange section 4 are partitioned by a perforated plate 5, and the heat exchange section 4 has one end connected to an air supply duct 24 via a dispersion pipe 23 and the other end communicated with the drying chamber 2. It is composed of a plurality of heat exchange tubes 22, and in the heat exchange section 4, the supply air sent by the blower and the exhaust gas from the incineration chamber 3 exchange heat,
Hot air blows into the drying chamber 2. The heat exchange section 4 also includes a plurality of first
An overflow pipe 25 is provided through which dried sludge from the drying chamber 2 falls into the incineration chamber 3 .

一方、乾燥室2の上部と焼却室3の下部とは空
気ダクト30で連通されており、乾燥室2からの
排ガスがこの空気ダクト30通つて焼却室3内に
流入して汚泥を火格子33上で流動させる噴流用
空気となる。焼却室3には複数本の第2オーバフ
ロー管31が設けられており、この第2オーバフ
ロー管31の一端(下端)開口は炉1外の焼却灰
搬送用コンベヤ32に臨み、他端(上端)開口は
焼却室3内に突出して上向きになつている。な
お、両オーバーフロー管25と31は同一直線上
に位置しないように設定されており、落下する汚
泥が灰取出し管31に直接入らないようになつて
いる。なお図中20は熱交換部4を介して焼却室
3に連通された排気ダクト、34はバーナであ
る。
On the other hand, the upper part of the drying chamber 2 and the lower part of the incineration chamber 3 are communicated with each other by an air duct 30, and the exhaust gas from the drying chamber 2 flows into the incineration chamber 3 through this air duct 30, and the sludge is removed from the grate 33. This becomes the jet air that flows above. The incineration chamber 3 is provided with a plurality of second overflow pipes 31. One end (lower end) of the second overflow pipe 31 faces the incinerated ash conveyor 32 outside the furnace 1, and the other end (upper end) opens. The opening projects into the incineration chamber 3 and faces upward. Note that the overflow pipes 25 and 31 are set so as not to be located on the same straight line, so that falling sludge does not directly enter the ash removal pipe 31. In the figure, 20 is an exhaust duct that communicates with the incineration chamber 3 via the heat exchanger 4, and 34 is a burner.

この実施例は以上のように構成されており、つ
ぎにその作用について説明する。
This embodiment is constructed as described above, and its operation will be explained next.

いま、この処理装置が動作している状態におい
て、脱水された汚泥がスクリユーコンベア11に
よつて乾燥室2に送り込まれると、熱交換部4に
て加熱された給気(通常約400〜500℃)によつて
汚泥が流動して乾燥する。その際、汚泥は粒子が
大きいため、激しい流動もしないし、また必要で
ない。流動している汚泥は、徐々に乾燥して粒形
が小さく軽くなり、乾燥室2の上方に移動し、オ
ーバフロー管25の上端に達すると、第1オーバ
フロー管25を通つて焼却室3に落下する。
Now, when this treatment device is in operation, when the dehydrated sludge is sent to the drying chamber 2 by the screw conveyor 11, the heated supply air (usually about 400 to 500 ℃), the sludge is fluidized and dried. At this time, since the sludge has large particles, vigorous flow is not required and is not required. The flowing sludge gradually dries and becomes smaller and lighter in particle size, moves above the drying chamber 2, and when it reaches the upper end of the overflow pipe 25, falls through the first overflow pipe 25 into the incineration chamber 3. do.

一方、汚泥から水分を吸収して乾燥室2の上部
に至つた排ガス(通常150〜200℃)は空気ダクト
30を通つて焼却室3の下部から内部に噴出す
る。この乾燥室2の排ガスの噴出によつて第1オ
ーバフロー管25から落下した汚泥が流動すると
ともに、バーナ34によつて汚泥が焼却される。
焼却された汚泥灰は、第2オーバフロー管31か
ら搬送コンベヤ32上に落下し、所望の場所に搬
送される。
On the other hand, the exhaust gas (usually 150 to 200°C) that has absorbed water from the sludge and reached the upper part of the drying chamber 2 passes through the air duct 30 and is ejected from the lower part of the incineration chamber 3 into the interior. This ejection of exhaust gas from the drying chamber 2 causes the sludge that has fallen from the first overflow pipe 25 to flow, and the sludge is incinerated by the burner 34 .
The incinerated sludge ash falls onto the conveyor 32 from the second overflow pipe 31 and is conveyed to a desired location.

なお、乾燥室2、焼却室3および熱交換部4の
第1図におけるX−X断面が矩形状となるように
設計すれば、その幅を拡縮するだけで容易に乾燥
室2等の容量を変化できる。
Note that if the drying chamber 2, incineration chamber 3, and heat exchange section 4 are designed so that the X-X cross section in FIG. It can change.

以上のように、この発明の有機性汚泥処理装置
によると、乾燥室、焼却室および熱交換部を炉内
に一体に形成し、乾燥室の噴流用空気となる給気
の加熱を、焼却室からの排ガスとの熱交換によつ
て行なうようにしたので、熱の有効利用が図られ
て熱効率がよい。また、乾燥処理後の乾燥排ガス
を焼却室の噴流用として燃焼させるため、乾燥排
ガスの悪臭がなくなり、臭気に対する処理装置を
必要としない。さらに、乾燥および焼却を流動層
式としたので高水分の汚泥を効率よく焼却でき
る。
As described above, according to the organic sludge treatment apparatus of the present invention, the drying chamber, the incineration chamber, and the heat exchange section are integrally formed in the furnace, and the heating of the supply air that becomes the jet air of the drying chamber is carried out in the incineration chamber. Since this is done through heat exchange with the exhaust gas from the exhaust gas, effective use of heat is achieved and thermal efficiency is high. Furthermore, since the dried exhaust gas after the drying process is burned as a jet in the incineration chamber, the foul odor of the dried exhaust gas is eliminated and no odor treatment device is required. Furthermore, since drying and incineration are carried out using a fluidized bed method, high moisture sludge can be incinerated efficiently.

また、炉内に、上方に向かつて、焼却室、熱交
換部、乾燥室を順々に設けるとともに、第1、第
2オーバフロー管を介し、汚泥(灰)を落下によ
り乾燥室から焼却室へ及び焼却室から外部に移動
するようにしたので、従来のごとく乾燥装置と焼
却装置を別体にしたもののように、コンベアなど
のその両装置間及び外部への特別な汚泥移動装置
を必要としないうえに、焼却室、熱交換部、乾燥
室が連続しているため、処理装置全体がコンパク
トなものとなる。
In addition, an incinerator, a heat exchange section, and a drying chamber are installed in the upward direction in the furnace, and the sludge (ash) is dropped from the drying chamber to the incineration chamber through the first and second overflow pipes. Since the sludge is moved from the incineration chamber to the outside, there is no need for special equipment such as conveyors to move the sludge between the two devices or to the outside, unlike conventional systems in which the drying device and incineration device are separate. Furthermore, since the incineration chamber, heat exchange section, and drying chamber are connected, the entire processing device becomes compact.

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

第1図はこの発明の有機性汚泥物処理装置の実
施例の概略切断正面図、第2図は第1図の熱交換
部の切断平面図である。 1…炉、2…乾燥室、3…焼却室、4…熱交換
部、25…第1オーバフロー管、30…空気ダク
ト、31…第2オーバフロー管。
FIG. 1 is a schematic cutaway front view of an embodiment of the organic sludge treatment apparatus of the present invention, and FIG. 2 is a cutaway plan view of the heat exchange section of FIG. 1. DESCRIPTION OF SYMBOLS 1... Furnace, 2... Drying chamber, 3... Incineration chamber, 4... Heat exchange part, 25... First overflow pipe, 30... Air duct, 31... Second overflow pipe.

Claims (1)

【特許請求の範囲】[Claims] 1 脱水された有機性汚泥が送り込まれる乾燥室
2と、乾燥室2からの汚泥が送り込まれる焼却室
3と、乾燥室2への給気と焼却室3からの排気と
を熱交換する熱交換部4とを炉1内に形成し、上
記乾燥室2は熱交換部4を介し焼却室3の上側に
連続して位置し、乾燥室2の上部から焼却室3の
下部に噴流用空気ダクト30を設け、焼却室3と
乾燥室2とを熱交換部4を通つて連通する汚泥落
下用第1オーバフロー管25を設けるとともに、
焼却室3内から炉1下方に灰取出用第2オーバフ
ロー管31を設けたことを特徴とする有機性汚泥
処理装置。
1. A drying chamber 2 into which dehydrated organic sludge is sent, an incineration chamber 3 into which sludge from the drying chamber 2 is sent, and a heat exchanger that exchanges heat between the air supplied to the drying chamber 2 and the exhaust air from the incineration chamber 3. The drying chamber 2 is continuously located above the incineration chamber 3 via the heat exchange section 4, and a jet air duct is provided from the upper part of the drying chamber 2 to the lower part of the incineration chamber 3. 30, and a first overflow pipe 25 for dropping sludge that communicates the incineration chamber 3 and the drying chamber 2 through the heat exchange section 4,
An organic sludge treatment device characterized in that a second overflow pipe 31 for removing ash is provided below the furnace 1 from inside the incineration chamber 3.
JP8479479A 1979-07-03 1979-07-03 Processing device for organic sludge Granted JPS5610616A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP8479479A JPS5610616A (en) 1979-07-03 1979-07-03 Processing device for organic sludge

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP8479479A JPS5610616A (en) 1979-07-03 1979-07-03 Processing device for organic sludge

Publications (2)

Publication Number Publication Date
JPS5610616A JPS5610616A (en) 1981-02-03
JPS6238604B2 true JPS6238604B2 (en) 1987-08-19

Family

ID=13840597

Family Applications (1)

Application Number Title Priority Date Filing Date
JP8479479A Granted JPS5610616A (en) 1979-07-03 1979-07-03 Processing device for organic sludge

Country Status (1)

Country Link
JP (1) JPS5610616A (en)

Also Published As

Publication number Publication date
JPS5610616A (en) 1981-02-03

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