JPS59166300A - Sludge drying incinerator - Google Patents
Sludge drying incineratorInfo
- Publication number
- JPS59166300A JPS59166300A JP58041128A JP4112883A JPS59166300A JP S59166300 A JPS59166300 A JP S59166300A JP 58041128 A JP58041128 A JP 58041128A JP 4112883 A JP4112883 A JP 4112883A JP S59166300 A JPS59166300 A JP S59166300A
- Authority
- JP
- Japan
- Prior art keywords
- sludge
- chamber
- heat exchanger
- drying
- drying chamber
- 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
Links
Landscapes
- Gasification And Melting Of Waste (AREA)
- Drying Of Solid Materials (AREA)
- Treatment Of Sludge (AREA)
Abstract
Description
【発明の詳細な説明】
この発明は、水処理設備で発生する汚泥の乾燥焼却装置
に関する。DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a drying and incineration device for sludge generated in water treatment equipment.
一般に、汚泥処理は、汚泥を自然条件下で安定させ、か
つ減量することを目的とするが、焼却すれば、汚泥中の
有機質はほとんど燃焼して炭酸ガスと水蒸気となり、外
気中に放出でき、残灰はCd等の有害、金属を含まなけ
れば、衛生的で安全かつ無害であるため処理が容易であ
る。Generally, the purpose of sludge treatment is to stabilize sludge under natural conditions and reduce its volume, but if it is incinerated, most of the organic matter in sludge will be burned and become carbon dioxide and water vapor, which can be released into the outside air. The remaining ash is hygienic, safe, and harmless as long as it does not contain harmful metals such as Cd, and is therefore easy to dispose of.
従って、汚泥の焼却処理は非常に好ましい処理手゛段と
いえる。Therefore, incineration of sludge can be said to be a very preferable treatment method.
ところで、水処理系統で発生する汚泥は、通常、濃縮沈
降槽による濃縮処理及び遠心分離機など(こよる機械的
脱水処理を行なうが、この場合でも汚泥の含水率は80
〜85%程度にしか低下せず、そのままで直接焼却する
ことは困難であるため、含水率が30〜50%になるま
で乾燥させる必要があり、一般に間接乾燥方式が採用さ
れている。By the way, sludge generated in water treatment systems is usually subjected to concentration treatment using a thickening sedimentation tank and mechanical dehydration treatment using a centrifuge, but even in this case, the water content of the sludge is 80%.
Since the moisture content decreases only to about 85% and it is difficult to directly incinerate it as it is, it is necessary to dry it until the moisture content reaches 30 to 50%, and an indirect drying method is generally adopted.
しかしながら、この方式は、乾燥用熱風が汚泥により汚
染されない利点をもつ反面、伝熱抵抗が大きい欠点があ
る。このため、通常、熱源の熱風として水蒸気を用い、
凝縮伝熱を行なわしめて熱貫流係数をあげるようにして
いる。However, although this method has the advantage that the hot air for drying is not contaminated with sludge, it has the disadvantage of high heat transfer resistance. For this reason, steam is usually used as the hot air source,
The heat transfer coefficient is increased by condensing heat transfer.
この水蒸気を熱源とした間接乾燥方式において、乾燥室
内は発生した水蒸気と高水分の汚泥が共存し、発生した
水蒸気は飽和状態であるか、或は過飽和の状態を呈して
いるのが普通である。このため、一度蒸発した水分はわ
ずかな温度降下で凝縮する。従って、乾燥機から焼却炉
への搬送経路において、その壁面に接触すること警こよ
り水蒸気が温度降下して凝縮し、乾燥した汚泥に再び吸
収されるという現象が発生している。この凝縮現象を防
止する手段として、通常、キャリヤ・エアと称する高温
空気を乾燥室内に吹き込んで未飽和状態とする方法が採
られている。その量は、大略絶対温度で0.7〜o、
s (Ky/Kp !空気)となる程度に調整しなけれ
ばならない。In this indirect drying method using steam as a heat source, the generated steam and high-moisture sludge coexist in the drying chamber, and the generated steam is usually saturated or supersaturated. . For this reason, once evaporated water condenses with a slight drop in temperature. Therefore, on the transport path from the dryer to the incinerator, a phenomenon occurs in which water vapor comes into contact with the wall surface, causes the temperature to drop, condenses, and is reabsorbed into the dried sludge. As a means to prevent this condensation phenomenon, a method is usually adopted in which high-temperature air called carrier air is blown into the drying chamber to create an unsaturated state. The amount is approximately 0.7 to o in absolute temperature,
It must be adjusted to the extent that s (Ky/Kp! air).
一方、省エネルギーの観点から、汚泥の乾燥焼却処理に
おいては、乾燥機の乾燥室から発生する水蒸気を熱交換
器(こ送り込んで汚泥の燃焼排ガスにより加熱し、その
後、その水蒸気を乾燥機の加熱室に供給して汚泥を乾燥
するようにしている。On the other hand, from the viewpoint of energy saving, in the drying and incineration process of sludge, the water vapor generated from the drying chamber of the dryer is sent through a heat exchanger and heated by the sludge combustion exhaust gas, and then the steam is transferred to the heating chamber of the dryer. The sludge is dried.
このような方法に、前記キャリヤ・エアを適用すると、
乾燥室Iこ発生した水蒸気の中に空気が多量に混ざ、る
こととなり、このような空気温合の水蒸気を再び乾燥用
加熱源として用いることとなるため、間知の伝熱理論に
より、伝熱係数が大幅に低下することとなり、本来の水
蒸気の伝熱特性を失わしめるという欠点がある。When the carrier air is applied to such a method,
A large amount of air will be mixed into the water vapor generated in the drying chamber, and the water vapor at this air temperature will be used again as a heating source for drying. According to the known heat transfer theory, This has the disadvantage that the heat transfer coefficient is significantly reduced and the original heat transfer characteristics of water vapor are lost.
この発明は、以上の点に留意し、過熱水蒸気を加熱室の
みならず乾燥室にも供給して伝熱係数の低下を防ぐこと
を目的としている。The present invention takes the above points into consideration and aims to supply superheated steam not only to the heating chamber but also to the drying chamber to prevent a decrease in the heat transfer coefficient.
すなわち、この発明の乾燥焼却装置は、間接加熱式乾燥
機と、この乾燥機から乾燥汚泥が送り込まれる焼却炉と
、この焼却炉の燃焼排ガスが流通する熱交換器との組合
せから成り、前記乾燥機の乾燥室に前記熱交換器の熱交
換管の一端を接続して乾燥室から発生する水蒸気を熱交
換器にて燃焼排ガス(こより加熱し、熱交換管の他端を
乾燥機の加熱室及び乾燥室(こ接続して前記加熱された
水蒸気【こより汚泥を乾燥するようにしたものである。That is, the drying and incinerator of the present invention is composed of a combination of an indirect heating dryer, an incinerator into which dried sludge is sent from the dryer, and a heat exchanger through which the combustion exhaust gas of the incinerator flows. One end of the heat exchange tube of the heat exchanger is connected to the drying chamber of the dryer, and the water vapor generated from the drying chamber is heated by the combustion exhaust gas (this), and the other end of the heat exchange tube is connected to the heating chamber of the dryer. and a drying chamber (which is connected to the heated steam to dry the sludge).
このように構成すること(こより、熱交換器で加熱され
た過熱水蒸気が加熱室のみならず乾燥室(こも供給され
、その供給によって、乾燥室内の水蒸気が未飽和状態と
なり、わずかな温度降下では凝縮しなくなり、乾燥され
た汚泥に再び吸収されることもなくなる。従って、後工
程の焼却において汚泥の燃焼カ≧円滑(こ行なわれる。With this configuration, the superheated steam heated by the heat exchanger is supplied not only to the heating chamber but also to the drying chamber. It will not condense and will not be reabsorbed into the dried sludge.Therefore, in the subsequent incineration process, the combustion of the sludge will be carried out smoothly.
また、水蒸気の混入であるため、1云熱係数も低下せず
、水蒸気の伝熱特性を失なうこともない。Furthermore, since water vapor is mixed in, the thermal coefficient does not decrease by even one inch, and the heat transfer characteristics of water vapor are not lost.
このため、効率のよい乾燥を行なうことができる。Therefore, efficient drying can be performed.
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(こ示すように、乾燥焼却装置は、乾燥機A、焼却炉
B及び熱交換器Cの組合せから成る。乾燥機Aは、密封
外筒1内に内筒2が挿通され、内筒2内に乾燥室3、内
外筒2と1の間(こ加熱室4が形成され、加熱室4の熱
が内筒2の壁を介して乾燥室3内に伝達され、その熱に
よって乾燥が行なわれる。内筒1の入口(こはスクリュ
ーコンベヤなどの汚泥供給機5がロータリーダンパー6
を介して設けられ、−この供給機5(こよりad的脱水
処理後の汚泥が乾燥室4内のコンベヤ7よ(こ送り込ま
れ、コンベヤ7によって乾燥室4内を搬送されながろ乾
燥される。(As shown in this figure, the drying and incineration device consists of a combination of a dryer A, an incinerator B, and a heat exchanger C. In the dryer A, an inner cylinder 2 is inserted into a sealed outer cylinder 1. A drying chamber 3 is formed between the inner and outer cylinders 2 and 1 (a heating chamber 4 is formed therein, and the heat of the heating chamber 4 is transmitted into the drying chamber 3 through the wall of the inner cylinder 2, and the drying is carried out by the heat. The entrance of the inner cylinder 1 (this is where the sludge feeder 5 such as a screw conveyor is connected to the rotary damper 6
- From this feeder 5, the sludge after the ad-hoc dehydration treatment is sent to the conveyor 7 in the drying chamber 4, and is dried while being conveyed inside the drying chamber 4 by the conveyor 7. .
乾燥室3には、排気口8が形成されている。この排気口
8はブロアー9を介して熱交換器Cの熱交換管10の一
端に接続され、熱交換管10の他端は、加熱室4の給気
口11に接続されるとともに、乾燥室3の排出側の給気
口121こ調節弁13を介して接続されている。な−お
、両給気口11 .12)こは、ノズルを設けて混入を
円滑に行なうよう(こするのがよい。An exhaust port 8 is formed in the drying chamber 3. This exhaust port 8 is connected to one end of a heat exchange tube 10 of the heat exchanger C via a blower 9, and the other end of the heat exchange tube 10 is connected to an air supply port 11 of the heating chamber 4, and the drying chamber The air supply port 121 on the discharge side of No. 3 is connected via the control valve 13. By the way, both air supply ports 11. 12) In this case, a nozzle should be provided to ensure smooth mixing (rubbing is recommended).
乾燥室3から熱交換器Cへの配管には、この配管内の水
蒸気温度を検出して乾燥室3内の水蒸気温度を測定する
温度測定器14が付設され、この測定器14により、前
記調節弁13の開閉度が調節されて熱交換器Cを通った
水蒸気の乾燥室3への供給量が調節される。また、加熱
室4(こは水蒸気放出口15が形成され、この放出口1
5は調節弁16を介して外気(こ連通され、調節弁16
により加熱室4内の圧力が一定(こ保たれる。A temperature measuring device 14 is attached to the piping from the drying chamber 3 to the heat exchanger C to detect the water vapor temperature in this piping and measure the water vapor temperature in the drying chamber 3. The degree of opening and closing of the valve 13 is adjusted to adjust the amount of water vapor that has passed through the heat exchanger C and is supplied to the drying chamber 3. In addition, the heating chamber 4 (in this case, a water vapor discharge port 15 is formed, and this discharge port 1
5 is communicated with outside air via the control valve 16, and the control valve 16
This keeps the pressure inside the heating chamber 4 constant.
加熱室4の下部にはドレン口17が形成され、このドレ
ン口17から加熱室4下部に溜ったドレンがドレントラ
ップ18を介して適宜排出される。A drain port 17 is formed in the lower part of the heating chamber 4, and the drain collected in the lower part of the heating chamber 4 is appropriately discharged from the drain port 17 via a drain trap 18.
焼却炉Bの入口にはスクリューコンベヤなどの乾燥汚泥
供給機19が設けられ、この供給機19は、ロータリダ
ンパー20を介して乾燥室3の出口に接続され、ロータ
リダンパー20及び供給機19により例えば含水率30
%に乾燥された汚泥が焼却炉Bに送り込まれる。焼却炉
Bにはバーナ21が設けられ、このバーナ21によって
汚泥は焼却され、その残灰は排出口22から適宜緋色さ
れるとともに、燃焼排ガスは熱交換器Cが介設された排
気管23を通って排出される。A dry sludge feeder 19 such as a screw conveyor is provided at the inlet of the incinerator B, and this feeder 19 is connected to the outlet of the drying chamber 3 via a rotary damper 20. Moisture content 30
% dried sludge is sent to incinerator B. The incinerator B is provided with a burner 21, the sludge is incinerated by the burner 21, the residual ash is appropriately turned scarlet from the discharge port 22, and the combustion exhaust gas is passed through the exhaust pipe 23 in which the heat exchanger C is interposed. It passes through and is discharged.
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。The embodiment is configured as described above, and its operation will be explained next.
まず、水分を含んだ汚泥は、矢印aのごとく汚泥供給機
5fこ投入され、この供給機5により、乾燥室3に送り
込まれ、コンベヤ7により乾燥室3の入口(右端)から
出口(左端)に向って移動され・ながら、加熱室4から
の熱によって乾燥され、矢印すのごとく、出口から排出
される。この排出された乾燥汚泥は、ロータリダンパー
20により、矢印CQごとく適時に汚泥供給機19に送
り込まれ、この供給機19により矢印dのごとく焼却炉
Bに投入されて焼却され、残灰は矢印eのごとく排出口
22から排出される。First, the sludge containing moisture is fed into the sludge feeder 5f as shown by arrow a, and is sent to the drying chamber 3 by the feeder 5, and is conveyed from the inlet (right end) to the outlet (left end) of the drying chamber 3 by the conveyor 7. It is dried by the heat from the heating chamber 4 while being moved towards it, and is discharged from the outlet as shown by the arrow. This discharged dry sludge is fed by the rotary damper 20 to the sludge feeder 19 in a timely manner as shown by the arrow CQ, and by this feeder 19 is fed into the incinerator B as shown by the arrow d to be incinerated, and the remaining ash is left behind by the arrow e. It is discharged from the discharge port 22 as shown in FIG.
一方、焼却炉B内で発生した燃焼排ガスは、矢印イ11
ロ、ハごとく排気管23によって熱交換器Cに導びかれ
たのち、外気に排出される。On the other hand, the combustion exhaust gas generated in incinerator B is
After being led to the heat exchanger C through the exhaust pipe 23 as in b and c, it is discharged to the outside air.
乾燥室3内の汚泥から発生した水蒸気は、ブロアー9(
こより熱交換器Cに送り込まれて加熱され、過熱状態と
な・つて加熱室4及び乾燥室3に送り込まれる。加熱室
4(こ送り込まれた水蒸気は内筒2を介して放熱し、大
部分がドレンとなってドレン口17、ドレントラップ1
日を通って排出される。The water vapor generated from the sludge in the drying chamber 3 is transferred to the blower 9 (
From there, it is fed into the heat exchanger C, where it is heated, becomes superheated, and then sent into the heating chamber 4 and the drying chamber 3. The steam sent into the heating chamber 4 radiates heat through the inner cylinder 2, and most of it becomes drain, draining into the drain port 17 and drain trap 1.
It is excreted throughout the day.
一方、その放熱によって乾燥室3内の汚泥が加熱されて
乾燥される。On the other hand, the sludge in the drying chamber 3 is heated and dried by the heat radiation.
また、測定器14(こより調節弁13が適宜開閉されて
過熱状態の水蒸気が乾燥室3に送り込まれ、乾燥室3内
の水蒸気が未飽和状態にされて、わずかの温度降下では
凝縮しないようiこ調節される。In addition, the control valve 13 is opened and closed as appropriate from the measuring instrument 14, and superheated water vapor is sent into the drying chamber 3, and the water vapor in the drying chamber 3 is brought into an unsaturated state so that it will not condense even with a slight temperature drop. This is adjusted.
従って、乾燥汚泥に再び含水させることがないため十分
に乾燥−された汚泥が焼却炉Bに送り込まれる。また、
乾燥室3に送り込まれるのが水蒸気であるため、乾燥室
3内の水蒸気を加熱源としても、前記のキャリヤ・エア
を吹き込む場合のように伝熱係数の低下を招くことがな
く、効率のよい乾燥が行なわれる。Therefore, since the dried sludge does not contain water again, sufficiently dried sludge is sent to the incinerator B. Also,
Since it is water vapor that is sent into the drying chamber 3, even if the water vapor in the drying chamber 3 is used as a heating source, the heat transfer coefficient does not decrease as in the case of blowing carrier air, which is efficient. Drying takes place.
【図面の簡単な説明】
図面はこの発明の乾燥焼却装置の一実施例の概略配管図
である。
A・・・乾燥機、B・・・焼却炉、C・・・熱交換器、
3・・・乾燥室、4・・・加熱室。
特許出願人 久保田鉄工株式会社
同 代理人 鎌 1) 文 二622BRIEF DESCRIPTION OF THE DRAWINGS The drawing is a schematic piping diagram of an embodiment of the drying and incinerator of the present invention. A... Dryer, B... Incinerator, C... Heat exchanger,
3...Drying room, 4...Heating room. Patent applicant Kubota Iron Works Co., Ltd. Agent Kama 1) Text 2622
Claims (1)
まれる焼却炉と、この焼却炉の燃焼排ガスが流通する熱
交換器との・組合せから成り、前記乾燥機の乾燥室に、
前記熱交換器の熱交換管の一端を接続して乾燥室から発
、生する水蒸気を熱交換器にて燃焼排ガスにより加熱し
、熱交換管の他端を乾燥機の加熱室及び乾燥室に接続し
て前記加熱された水蒸気により汚泥を乾燥するようにし
たことを特徴とする汚泥の乾燥焼却装置。It consists of a combination of an indirect heating dryer, an incinerator into which dried sludge is sent from the dryer, and a heat exchanger through which combustion exhaust gas from the incinerator flows, and in the drying chamber of the dryer,
One end of the heat exchange tube of the heat exchanger is connected to heat the steam generated from the drying chamber with combustion exhaust gas in the heat exchanger, and the other end of the heat exchange tube is connected to the heating chamber and drying chamber of the dryer. A sludge drying and incineration apparatus characterized in that the sludge is connected to dry the sludge using the heated water vapor.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP58041128A JPS59166300A (en) | 1983-03-10 | 1983-03-10 | Sludge drying incinerator |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP58041128A JPS59166300A (en) | 1983-03-10 | 1983-03-10 | Sludge drying incinerator |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| JPS59166300A true JPS59166300A (en) | 1984-09-19 |
Family
ID=12599799
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP58041128A Pending JPS59166300A (en) | 1983-03-10 | 1983-03-10 | Sludge drying incinerator |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPS59166300A (en) |
Cited By (9)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS61209099A (en) * | 1985-03-09 | 1986-09-17 | Kawasaki Heavy Ind Ltd | Method and apparatus for drying and incinerating sludge |
| JPS63231111A (en) * | 1987-03-09 | 1988-09-27 | 郭 ▲聰▼賢 | Waste incinerating method |
| WO2002049973A3 (en) * | 2000-12-20 | 2002-10-10 | Vincent Promuto | Method and apparatus for drying and incineration of sewage sludge |
| JP2011137613A (en) * | 2009-12-28 | 2011-07-14 | Kenki Kk | Drying device |
| JP2013534180A (en) * | 2010-08-06 | 2013-09-02 | コミッサリア ア レネルジー アトミーク エ オ ゼネルジ ザルタナテイヴ | Sludge drying method and sludge drying equipment |
| CN107976055A (en) * | 2017-11-17 | 2018-05-01 | 芜湖县宏大机械设备制造有限公司 | A kind of helical feed drying device |
| CN109059522A (en) * | 2018-08-01 | 2018-12-21 | 刘风强 | A kind of chemical industry hot steam recycling device |
| CN110092565A (en) * | 2019-05-07 | 2019-08-06 | 杭州小橙工业设计有限公司 | A kind of intelligentized sludge drier |
| CN110127983A (en) * | 2019-04-24 | 2019-08-16 | 杭州小橙工业设计有限公司 | A kind of sludge drier |
Citations (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS5618213A (en) * | 1979-07-23 | 1981-02-20 | Ebara Infilco Co Ltd | High-temperature melting treatment |
| JPS56119416A (en) * | 1980-02-25 | 1981-09-19 | Tsukishima Kikai Co Ltd | Sludge drying and incinerating appatatus |
-
1983
- 1983-03-10 JP JP58041128A patent/JPS59166300A/en active Pending
Patent Citations (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS5618213A (en) * | 1979-07-23 | 1981-02-20 | Ebara Infilco Co Ltd | High-temperature melting treatment |
| JPS56119416A (en) * | 1980-02-25 | 1981-09-19 | Tsukishima Kikai Co Ltd | Sludge drying and incinerating appatatus |
Cited By (10)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS61209099A (en) * | 1985-03-09 | 1986-09-17 | Kawasaki Heavy Ind Ltd | Method and apparatus for drying and incinerating sludge |
| JPS63231111A (en) * | 1987-03-09 | 1988-09-27 | 郭 ▲聰▼賢 | Waste incinerating method |
| WO2002049973A3 (en) * | 2000-12-20 | 2002-10-10 | Vincent Promuto | Method and apparatus for drying and incineration of sewage sludge |
| US6532880B2 (en) | 2000-12-20 | 2003-03-18 | Vincent Promuto | Method and apparatus for drying and incineration of sewage sludge |
| JP2011137613A (en) * | 2009-12-28 | 2011-07-14 | Kenki Kk | Drying device |
| JP2013534180A (en) * | 2010-08-06 | 2013-09-02 | コミッサリア ア レネルジー アトミーク エ オ ゼネルジ ザルタナテイヴ | Sludge drying method and sludge drying equipment |
| CN107976055A (en) * | 2017-11-17 | 2018-05-01 | 芜湖县宏大机械设备制造有限公司 | A kind of helical feed drying device |
| CN109059522A (en) * | 2018-08-01 | 2018-12-21 | 刘风强 | A kind of chemical industry hot steam recycling device |
| CN110127983A (en) * | 2019-04-24 | 2019-08-16 | 杭州小橙工业设计有限公司 | A kind of sludge drier |
| CN110092565A (en) * | 2019-05-07 | 2019-08-06 | 杭州小橙工业设计有限公司 | A kind of intelligentized sludge drier |
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