JPS6075399A - Drying and incinerating method of dehydrated sludge - Google Patents

Drying and incinerating method of dehydrated sludge

Info

Publication number
JPS6075399A
JPS6075399A JP58183548A JP18354883A JPS6075399A JP S6075399 A JPS6075399 A JP S6075399A JP 58183548 A JP58183548 A JP 58183548A JP 18354883 A JP18354883 A JP 18354883A JP S6075399 A JPS6075399 A JP S6075399A
Authority
JP
Japan
Prior art keywords
sludge
fluidized bed
drying
dehydrated sludge
fluidized
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.)
Pending
Application number
JP58183548A
Other languages
Japanese (ja)
Inventor
Yoshiyasu Terasaka
寺坂 善保
Kazuhiro Mimura
三村 和博
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.)
Chugai Ro Co Ltd
Original Assignee
Chugai Ro 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 Chugai Ro Co Ltd filed Critical Chugai Ro Co Ltd
Priority to JP58183548A priority Critical patent/JPS6075399A/en
Publication of JPS6075399A publication Critical patent/JPS6075399A/en
Pending legal-status Critical Current

Links

Classifications

    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F26DRYING
    • F26BDRYING SOLID MATERIALS OR OBJECTS BY REMOVING LIQUID THEREFROM
    • F26B3/00Drying solid materials or objects by processes involving the application of heat
    • F26B3/02Drying solid materials or objects by processes involving the application of heat by convection, i.e. heat being conveyed from a heat source to the materials or objects to be dried by a gas or vapour, e.g. air
    • F26B3/06Drying solid materials or objects by processes involving the application of heat by convection, i.e. heat being conveyed from a heat source to the materials or objects to be dried by a gas or vapour, e.g. air the gas or vapour flowing through the materials or objects to be dried
    • F26B3/08Drying solid materials or objects by processes involving the application of heat by convection, i.e. heat being conveyed from a heat source to the materials or objects to be dried by a gas or vapour, e.g. air the gas or vapour flowing through the materials or objects to be dried so as to loosen them, e.g. to form a fluidised bed

Landscapes

  • Engineering & Computer Science (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Microbiology (AREA)
  • Mechanical Engineering (AREA)
  • General Engineering & Computer Science (AREA)
  • Treatment Of Sludge (AREA)
  • Glanulating (AREA)
  • Devices And Processes Conducted In The Presence Of Fluids And Solid Particles (AREA)

Abstract

PURPOSE:To decrease the moisture of sludge and to decrease the ejecting pressure and flow rate of fluidized gas in a fluidized bed dryer by subjecting dehydrated sludge to preliminary drying and granulation by making use of the heat generated in an incineration furnace then supplying the sludge to a sandless type fluidized bed dryer. CONSTITUTION:Dehydrated sludge is charged into the casing 4 of a preliminary drying and granulating machine 1 and is mixed and agitated by a rotary blade 8, by which the sludge is dried and granulated. The granuated sludge is screened by a sieve 9 and is charged to a fluidized bed dryer 2 where the sludge is fluidized and is heated and dried by the steam with the heat generated in a fluidized bed incineration furnace 3 as a heat source. The sludge is then charged into the sandless type fluidized bed incineration furnace 3 and is incinerated in a fluidized bed 19. The granulated sludge except prescribed grain size is again returned to the machine 1. The casing 4 itself of the machine 1 is heated by utilizing the heat generated in the furnace 3 to improve the effect of preliminary heating.

Description

【発明の詳細な説明】 従来、脱水汚泥を乾燥焼却するには、一般に、脱水汚泥
を造粒機で造粒し、これを無砂式流動層乾燥機で乾燥し
たのち、無砂式流動層焼却炉で焼月1する方式が採用さ
れている。
[Detailed Description of the Invention] Conventionally, in order to dry and incinerate dehydrated sludge, the dehydrated sludge is generally granulated in a granulator, dried in a sandless fluidized bed dryer, and then granulated in a sandless fluidized bed dryer. A method is adopted in which the waste is burned in an incinerator.

しかしながら、造粒機は高速回転で駆動する必要があり
、そのため回転翼やケーシングの寿命が短いとともに、
所要動力が大きく消費ミノ〕が大きいという欠点がある
However, the granulator needs to be driven at high speed, which shortens the lifespan of the rotor blades and casing.
The drawback is that it requires a large amount of power and consumes a large amount of energy.

また、このようにして造粒された脱水汚泥は水分が多(
て重いため、流動層乾燥機の流動気体の噴出圧力を大と
づる必要上、消費電力の大なる大能力の流動ブロワを必
要とするという欠点を有していた。
In addition, the dehydrated sludge granulated in this way has a high water content (
Since the fluidized bed dryer is heavy, it is necessary to increase the jetting pressure of the fluidized gas from the fluidized bed dryer, and it has the disadvantage that it requires a fluidized blower with high power consumption and high capacity.

本発明は、前記従来法の欠点を除去りるために種々検討
の結果、乾燥しながら造粒を行えば、造粒機の回転を低
速としても容易に造粒することができるという点に着目
してなされたもので、脱水汚泥を焼却炉で発生した熱を
利用した予備乾燥造粒機により造粒するとともに、予備
乾燥して無砂式流動層乾燥機に供給す′るようにして前
記欠点を除去した脱水汚泥の乾燥焼却法を提供しようと
するものである。
As a result of various studies to eliminate the drawbacks of the conventional method, the present invention focuses on the fact that if granulation is performed while drying, granulation can be easily performed even if the rotation speed of the granulator is low. The dehydrated sludge is granulated by a pre-drying granulator that utilizes heat generated in an incinerator, and the pre-dried sludge is supplied to a sandless fluidized bed dryer. The present invention aims to provide a method for drying and incinerating dehydrated sludge that eliminates drawbacks.

次に、本発明を添付図面に従って説明づる。Next, the present invention will be explained with reference to the accompanying drawings.

図面ば本発明の乾燥焼却法の概略を示し、大略、予備乾
燥造粒機1と流動層乾燥機2および流動層焼却炉3とか
らなる。前記予備乾燥造粒機1は−端に投入口5を、J
、た他端に排出口6を備えlζケーシング4内に、多数
の回転翼8を右する回転軸7を備えた構成からなる。ま
た前記回転軸7は中空構造どなっているとともに、回転
翼8も中空構)責どなっており、各回転翼8の内部と回
転軸の内部とは連通している。
The drawings schematically show the drying and incineration method of the present invention, which generally includes a pre-drying granulator 1, a fluidized bed dryer 2, and a fluidized bed incinerator 3. The pre-drying granulator 1 has an input port 5 at the negative end, and a J
, and has a discharge port 6 at the other end, and a rotary shaft 7 on which a large number of rotary blades 8 are mounted inside a casing 4 . The rotary shaft 7 has a hollow structure, and the rotor blades 8 also have a hollow structure, and the inside of each rotor blade 8 and the inside of the rotary shaft are in communication.

前記流動層乾燥機2は上方に前記排出口6と対向りる投
入口11を、上方に乾燥粒状物を排出JるjJI出口1
2を備えたクーラング10内に熱交換器14を備えた構
成からなる。そして、図示しない流動気体がケーシング
10の下方部から噴出し、投入口11から投入された粒
状汚泥を流動させ流動層13を形成するにうになってい
る。
The fluidized bed dryer 2 has an input port 11 facing the discharge port 6 upwardly, and an outlet 1 for discharging dry granules upwardly.
The heat exchanger 14 is provided in a coolant 10 having a heat exchanger 14. Fluidized gas (not shown) is ejected from the lower part of the casing 10 to fluidize the granular sludge introduced from the inlet 11 to form a fluidized bed 13.

前記流動層炉2JI炉3は流動層乾燥機2と大略同一構
成からなり、前記排出口12から排出された乾燥汚泥を
投入する投入口17と焼Mlされた焼却灰を排出Jる1
ノ1出ロ18とを備えるとともに熱交換器20をイjし
、ケーシング16の下部から噴出する流動気体により粒
状汚泥を流動しつつ焼却覆る流動層19を形成リ−るよ
うになっている。そして、前記熱交換器14と20とは
図示しないボイラを介して配管15で互いに連通ずると
ともに、ボイラによって生じた蒸気の一部は、配管15
から前記予(i^乾燥造粒機1の中空回転軸7を介して
各回転翼8内を循環し再度前記配管15に戻るようにな
っている。尚、9はふるいである。
The fluidized bed furnace 2JI furnace 3 has approximately the same configuration as the fluidized bed dryer 2, and includes an input port 17 for inputting the dried sludge discharged from the discharge port 12, and a discharge port 1 for discharging the incinerated ash.
A heat exchanger 20 is provided, and a fluidized bed 19 is formed in which the granular sludge is fluidized and incinerated by fluidized gas ejected from the lower part of the casing 16. The heat exchangers 14 and 20 communicate with each other via a piping 15 via a boiler (not shown), and a portion of the steam generated by the boiler is transferred to the piping 15.
From there, the precipitate is circulated through each of the rotary blades 8 via the hollow rotary shaft 7 of the drying granulator 1 and returns to the pipe 15 again. Note that 9 is a sieve.

従って、脱水汚泥は投入口5から予備乾燥造粒機1のケ
ーシング4内に投入され、図示しない駆動機により回転
する回転軸7によりその回転翼8で温合撹拌するとども
に乾燥し、造粒されることになる。このようにして造粒
された)lj泥は、排出口6からふるい9を経て所定粒
径範囲内のものが投入口11から流動層乾燥機2内に投
入される。一方、ふるいにより選別された小粒径および
大粒径の造粒汚泥は返送汚泥として再度投入口5から予
備乾燥造粒機1のケーシング4内に投入されることにな
る。流動層乾燥機2内に投入された予備乾燥した粒状汚
泥は流動気体により流動し、その間に流動層焼却炉3で
発生した熱を熱源とする蒸気により加熱乾燥され、やが
て排出口12から投入口17を経て流動層焼却炉3内に
投入される。この投入された乾燥粒状物は流動層19で
前記流動層乾燥機に揖フると同様流動するとともに焼却
さtし、その焼却1火はiJl出口18から排出される
ことになる。
Therefore, dehydrated sludge is introduced into the casing 4 of the pre-drying granulator 1 from the input port 5, heated and stirred by the rotary blades 8 of the rotary shaft 7 rotated by a drive machine (not shown), dried and granulated. will be done. The lj mud granulated in this manner passes through a sieve 9 from an outlet 6, and those within a predetermined particle size range are fed into a fluidized bed dryer 2 from an inlet 11. On the other hand, the granulated sludge of small particle size and large particle size that have been sorted by the sieve are fed back into the casing 4 of the pre-drying granulator 1 through the input port 5 as return sludge. The pre-dried granular sludge charged into the fluidized bed dryer 2 is fluidized by the fluidized gas, during which time it is heated and dried by steam using the heat generated in the fluidized bed incinerator 3 as a heat source, and is eventually transferred from the discharge port 12 to the input port. 17, and then put into the fluidized bed incinerator 3. The charged dry granules are fluidized in the fluidized bed 19 in the same way as they are in the fluidized bed dryer and are incinerated, and the incinerated fire is discharged from the iJl outlet 18.

尚、前記流動@19で乾燥汚泥が焼却される際に発生す
る熱は、熱交換器20により回収され、これを熱源とし
て前記ボイラで蒸気を発生させるものである。また場合
にJ−っては配管15からの蒸気にまって前記流動気体
を加熱するようにしてもよl、)。
The heat generated when the dried sludge is incinerated in the flow @ 19 is recovered by the heat exchanger 20, and is used as a heat source to generate steam in the boiler. In some cases, the flowing gas may be heated by being soaked in steam from the pipe 15).

さらに、予備乾燥造粒+;l!1のケーシング自体をも
加熱し予備加熱を更に向上させるよう【こしてもよいこ
とは勿論である。
Furthermore, pre-dried granulation +;l! Of course, the casing of No. 1 may also be heated and strained to further improve the preheating.

以上の説明で明rうかなように、本発明に係る脱水汚泥
の乾燥焼J、II法によれば、11;2水汚泥を流動層
乾燥機2に投入りる前に、予備乾燥造粒機で乾燥造粒り
るため、汚泥はその水分が軽減されており、流動層乾燥
機にa5りる流動気体の噴出圧力を従来のしのより低く
でき、かつ、流動気体の風聞も少なくでき、そのため流
動ブロワは小型で消費電力の小さなもので済み、省電力
化を図ることができる。また、前記予備乾燥造粒機1の
乾燥用熱源(よ流動層焼却炉で発生した熱を利用するた
め安価である。さらに、この予備乾燥造粒機の運転は低
速回転で行うため、消費電力が小さいととしに騒音を発
生することがなく、しかも回転翼やケーシングの摩耗が
少なく寿命を長くすることができるという利点を有する
ものである。
As is clear from the above explanation, according to the drying method J and II of dehydrated sludge according to the present invention, 11; Because the sludge is dried and granulated in a drying machine, its water content is reduced, and the ejection pressure of the fluidized gas in the fluidized bed dryer can be lower than that of conventional methods, and the noise of the fluidized gas can also be reduced. Therefore, the flow blower can be small and consume little power, which can save power. In addition, since the drying heat source of the pre-drying granulator 1 (heat generated in the fluidized bed incinerator) is used, it is inexpensive.Furthermore, since the pre-drying granulator is operated at a low speed, it consumes less power. If the noise is small, it does not generate noise, and has the advantage that the rotor blades and casing have little wear and can have a long life.

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

第1図は本発明に係る脱水汚泥の乾燥焼Nj法を示づ゛
概略図である。 1・・・予備乾燥造粒機、2・・・流動層乾燥機、3・
・・流vJ層焼却炉、4・・・ケーシング、5・・・投
入口、6・・・排出口、7・・・回転軸(中空)、8・
・・回1i7. @、9・・・ふるい、10・・・ケー
シング、11・・・投入[l、12・・・+Jl出口、
13・・・流動層、14・・・熱交換器、15・・・配
管、1G・・・ケーシング、17・・・投入口、18・
・・排出[l、19・・・流動層、20・・・熱交換器
、21・・・分岐管。 特許出願人 中外炉工業株式会社
FIG. 1 is a schematic diagram showing the drying and burning Nj method for dewatered sludge according to the present invention. 1... Pre-drying granulator, 2... Fluidized bed dryer, 3...
...Flow VJ layer incinerator, 4...Casing, 5...Inlet, 6...Outlet, 7...Rotating shaft (hollow), 8...
...Time 1i7. @, 9...Sieve, 10...Casing, 11...Input [l, 12...+Jl outlet,
13... Fluidized bed, 14... Heat exchanger, 15... Piping, 1G... Casing, 17... Inlet, 18...
...Discharge [l, 19... Fluidized bed, 20... Heat exchanger, 21... Branch pipe. Patent applicant Chugai Roko Kogyo Co., Ltd.

Claims (2)

【特許請求の範囲】[Claims] (1)脱水汚泥を無砂式流動層乾燥機で乾燥したのち、
無砂式流動層焼却炉で焼却する脱水汚泥の゛乾燥焼却法
において、前記乾燥機での乾燥工程の前処理どして脱水
汚泥を前記焼却炉の発生熱を利用した予備乾燥造粒機で
乾燥造粒することを特徴とする脱水汚泥の乾燥焼却法。
(1) After drying the dehydrated sludge in a sandless fluidized bed dryer,
In the dry incineration method for dehydrated sludge that is incinerated in a sandless fluidized bed incinerator, the dehydrated sludge is pretreated in the drying process in the dryer and then processed in a pre-drying granulator that utilizes the heat generated by the incinerator. A method for drying and incinerating dehydrated sludge, which is characterized by drying and granulating it.
(2)前記予備乾燥造粒機に所定粒径範囲外の予備乾燥
潜記を返送することを特徴とする特許請求の範囲第1項
記載の脱水汚泥の乾燥焼却法。
(2) The method for drying and incinerating dehydrated sludge according to claim 1, characterized in that pre-drying particles outside a predetermined particle size range are returned to the pre-drying granulator.
JP58183548A 1983-09-30 1983-09-30 Drying and incinerating method of dehydrated sludge Pending JPS6075399A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP58183548A JPS6075399A (en) 1983-09-30 1983-09-30 Drying and incinerating method of dehydrated sludge

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP58183548A JPS6075399A (en) 1983-09-30 1983-09-30 Drying and incinerating method of dehydrated sludge

Publications (1)

Publication Number Publication Date
JPS6075399A true JPS6075399A (en) 1985-04-27

Family

ID=16137731

Family Applications (1)

Application Number Title Priority Date Filing Date
JP58183548A Pending JPS6075399A (en) 1983-09-30 1983-09-30 Drying and incinerating method of dehydrated sludge

Country Status (1)

Country Link
JP (1) JPS6075399A (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS61272698A (en) * 1985-05-29 1986-12-02 株式会社日立製作所 Dry granulation processor for waste liquor

Citations (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5621700A (en) * 1979-05-28 1981-02-28 Escher Wyss Ag Method of treating deposited sludge

Patent Citations (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5621700A (en) * 1979-05-28 1981-02-28 Escher Wyss Ag Method of treating deposited sludge

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS61272698A (en) * 1985-05-29 1986-12-02 株式会社日立製作所 Dry granulation processor for waste liquor

Similar Documents

Publication Publication Date Title
US5010830A (en) Process and apparatus for incinerating wet refuse
CN108072033A (en) A kind of device for increasing incineration firing efficiency
CN214501257U (en) Sludge drying and incinerating system
JPS6075399A (en) Drying and incinerating method of dehydrated sludge
JP4306334B2 (en) Carbide processing method and apparatus
KR100437874B1 (en) System for treating waste materials
KR200226144Y1 (en) Device for drying and incinerating the sludge of incinerating furnace
JP3609636B2 (en) Sludge drying equipment
CN212222785U (en) Sludge drying device
KR20000054505A (en) Device for drying and incinerating the sludge of incinerating furnace
JP2975011B1 (en) Activated carbon for dioxin adsorption, method and apparatus for producing the same, and dioxin adsorption treatment method
CN208791451U (en) Indirect heating type sludge drying charing mechanism
JPH105799A (en) Sludge treatment and device therefor
JP2004025152A (en) Treatment method of incineration ash
JPS6152883B2 (en)
JPH0324972Y2 (en)
CN111256153A (en) Sludge pre-drying direct-charging mixed combustion system suitable for circulating fluidized bed boiler
JPH04327706A (en) Drying and incinerating method for water-containing solid
KR200342621Y1 (en) Combined drying system of sludge
KR200290021Y1 (en) System for treating waste materials
JPS60174418A (en) Fluidized bed type incinerator for sewage or excretion dirt
CN216408989U (en) Sludge incinerator flue gas recirculation device
JPH08271148A (en) Garbage disposal equipment
CN215288491U (en) Wet sludge integrated treatment system based on flue gas waste heat is recycled
CN220537680U (en) System for improve cement manufacture line and deal with municipal sludge volume in coordination