JPS58123017A - Incinerating treatment of sewage sludge - Google Patents
Incinerating treatment of sewage sludgeInfo
- Publication number
- JPS58123017A JPS58123017A JP496082A JP496082A JPS58123017A JP S58123017 A JPS58123017 A JP S58123017A JP 496082 A JP496082 A JP 496082A JP 496082 A JP496082 A JP 496082A JP S58123017 A JPS58123017 A JP S58123017A
- Authority
- JP
- Japan
- Prior art keywords
- heat
- cake
- sludge
- digested
- fluidized bed
- 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
Classifications
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23G—CREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
- F23G5/00—Incineration of waste; Incinerator constructions; Details, accessories or control therefor
- F23G5/02—Incineration of waste; Incinerator constructions; Details, accessories or control therefor with pretreatment
- F23G5/04—Incineration of waste; Incinerator constructions; Details, accessories or control therefor with pretreatment drying
Abstract
Description
【発明の詳細な説明】 本発明は下水汚泥の継部処理方法に関するものである。[Detailed description of the invention] The present invention relates to a joint treatment method for sewage sludge.
従来のこの種の方法は、図−1に示すように、消化汚泥
を脱水機で脱水したケーキを流動層炉1内で補助燃料な
連続的に供給しながら焼却していた。焼却の際Kii生
する燃焼ガスは、流動層炉l内に強制i風損マによって
供給される燃焼空気を予熱するための熱交換器2、燃焼
ガスの温度を一定値以下に制限する。ための熱交換器3
、電気集塵機4、排風機5を順次通過したのち、煙突6
から大気中和放出されていた、水は前記熱換器3で加温
され温水とり、温水タンク$で貯留されたのち、放出さ
れていた。しかし、その温水は消化槽(図中省略する)
K投入される生汚泥を加温するための熱源としては利用
されていなかった。In the conventional method of this kind, as shown in Figure 1, a cake obtained by dewatering digested sludge in a dehydrator is incinerated in a fluidized bed furnace 1 while continuously supplying auxiliary fuel. The combustion gas generated during incineration is supplied to the fluidized bed furnace 1 by a forced winding blower, and a heat exchanger 2 for preheating the combustion air is used to limit the temperature of the combustion gas to a certain value or less. Heat exchanger 3 for
, an electric precipitator 4, and an exhaust fan 5, and then the chimney 6.
The water that had been neutralized and released into the atmosphere was heated in the heat exchanger 3, collected into hot water, stored in the hot water tank, and then released. However, the hot water is in the digestion tank (omitted from the diagram).
It was not used as a heat source to heat the raw sludge that was fed into K.
そのため、従来の方法は、流動層炉で脱水ケーキを焼却
するための補助燃料を連続的に必要とする欠点を有して
いた他に、消化槽に投入される生汚泥を加温すれば、消
化槽で発生する消化ガスの発生量を増加することかでき
るにもかかわらず、生汚泥を加温していなかったから、
消化ガスの発生量が制限され、ひいては消化ガスを利用
した発電装置の効率を低下させる欠点を有していた。Therefore, the conventional method had the disadvantage of continuously requiring auxiliary fuel to incinerate the dehydrated cake in a fluidized bed furnace. Even though the amount of digestion gas generated in the digestion tank could be increased, the raw sludge was not heated.
This has the disadvantage that the amount of digestion gas generated is limited, which in turn reduces the efficiency of power generation devices that utilize digestion gas.
本発明は前記のような従来の方法のもつ欠点を排除して
、流動層炉で脱水ケーキを焼却する際に補助燃料を必要
とせず、しかも消化槽に投入される生汚泥を加温するこ
とKよって、消化ガスの発生量を増大させ、消化ガスを
利用した発電装置の効率を向上することのできる下水汚
泥の燃却処理方法を提供することを目的とするものであ
る。The present invention eliminates the drawbacks of the conventional methods as described above, does not require auxiliary fuel when incinerating the dehydrated cake in a fluidized bed furnace, and also heats the raw sludge introduced into the digester. Therefore, it is an object of the present invention to provide a sewage sludge combustion treatment method that can increase the amount of digestion gas generated and improve the efficiency of a power generation device using digestion gas.
以下、図面に基づいて本発明を説明する。Hereinafter, the present invention will be explained based on the drawings.
第2図は本発明の70−シートを示しており、消化槽1
1で消化された汚泥は脱水機12で脱水ケーキにされる
。この脱水ケーキ中の含水率は約70−であるから、更
に間接加熱式乾燥装置13で脱水し、脱水ケーキ中の含
水率を約48−程度まで低下させ、ケーキの低位発熱量
を増大させる。FIG. 2 shows the 70-sheet of the present invention, with digester 1
The sludge digested in step 1 is turned into a dehydrated cake in dehydrator 12. Since the moisture content in this dehydrated cake is about 70-, it is further dehydrated in the indirect heating type drying device 13 to reduce the moisture content in the dehydrated cake to about 48- and increase the lower calorific value of the cake.
間接加熱式乾燥装置13で脱水され低位発熱量の増大し
たケーキは流動層炉14 K送られ、そこで自己燃焼し
て焼却される。焼却の際に生じる燃焼ガスはボイラ!5
の熱源として利用されたのち、電気集塵機17、排風機
を順次通過し、煙央I8から大気中に放出される。前記
ボイラ1sで発生した蒸気は前記間接加熱式乾燥装置1
3の熱源として利用される。前記間接加熱式乾燥装置i
tgでケーキを脱水する際にケーキから生じる蒸気は空
気と共に循環ブロワ19で吸引されコンデンサ加に送ら
れ、そこで凝水し温水となる。その温水の一部はコンデ
ンサ加から熱交換器211C送られ、そこで放熱したの
ちコンデンサ2IC返る。熱交換器21と熱交換器22
との間には熱媒が循環し、そり熱媒は熱交換器22で放
熱することによって、消化槽11jC投入される生汚泥
を加温する、消化槽11で発生した消化ガスは発電装置
等(図中省略する)K供給されるよつになっている。The cake, which has been dehydrated in the indirect heating dryer 13 and has an increased lower calorific value, is sent to a fluidized bed furnace 14K, where it is self-combusted and incinerated. The combustion gas produced during incineration is a boiler! 5
After being used as a heat source, it passes through an electrostatic precipitator 17 and an exhaust fan, and is released into the atmosphere from a smoke center I8. The steam generated in the boiler 1s is transferred to the indirect heating type drying device 1.
It is used as a heat source for 3. The indirect heating type drying device i
When the cake is dehydrated at tg, steam generated from the cake is sucked together with air by a circulation blower 19 and sent to a condenser, where it condenses to become hot water. A portion of the hot water is sent from the condenser to the heat exchanger 211C, where it radiates heat and then returns to the condenser 2IC. Heat exchanger 21 and heat exchanger 22
A heating medium is circulated between the heating medium and the heat exchanger 22 to radiate heat, thereby warming the raw sludge that is input into the digestion tank 11jC. (Omitted from the figure) K is supplied.
ところで、表1は本発明の方法を実施するときの操作条
件の一例を示すものである。Incidentally, Table 1 shows an example of operating conditions when implementing the method of the present invention.
表1
表2は脱水機12での脱水前の濃縮生汚泥と脱水後の消
化汚泥脱水ケーキとの性状を示している。Table 1 Table 2 shows the properties of the concentrated raw sludge before dehydration in the dehydrator 12 and the dehydrated digested sludge cake after dehydration.
表 2
本有機分低位発熱童= 5500 kaa44VS表3
は間接加熱式乾燥装置13での脱水前の脱水ケーキと脱
水後の乾燥ケーキとの性状を示していム次K、間接加熱
式乾燥装置!3の性能は次の通りである。Table 2 This organic content low fever child = 5500 kaa44VS Table 3
shows the properties of the dehydrated cake before dehydration and the dried cake after dehydration in the indirect heating drying device 13.Indirect heating drying device! The performance of No. 3 is as follows.
■ケーキからの水分蒸発量・・・・・・740い■加熱
蒸気消費量 ・・・・・・1070い■加熱蒸気
圧力 ・・・・・・6 ke/j G飽和流動
層炉14の性能は次の通りである。■Amount of moisture evaporated from cake...740 ■Amount of heating steam consumed...1070 ■Heating steam pressure...6 ke/j Performance of G saturated fluidized bed furnace 14 is as follows.
■燃焼空気温度 ・・・・・・・・・20℃■燃焼
ガス炉出口温度・・・・・・・・・900℃■燃焼空気
量 ・・・・・・・・・1780 Nd/h■燃
焼ガス量 ・・・・・・・・・2490 Nl/
に■空気比 ・・・・・・・・・1.30熱
損失 ・・・・・・・・・81総人熱)■補
助燃料 ・・・・・・・・・なしボイラ15の
性能は次の通りである。■Combustion air temperature: 20℃■Combustion gas furnace outlet temperature: 900℃■Combustion air amount: 1780 Nd/h■ Combustion gas amount ・・・・・・・・・2490 Nl/
■ Air ratio ・・・・・・・・・1.30 Heat loss ・・・・・・・・・81 Total human heat) ■ Auxiliary fuel ・・・・・・・・・None The performance of boiler 15 is It is as follows.
■燃焼ガス入口温度 ・・・・・・・・・900℃■燃
焼ガス出口温度 −・・・・・・・250℃■燃焼ガス
量 ・・・・・・・・・2490 Nd/に■蒸
発量 ・・・・・・・・・110い■蒸気圧
力 ・・・・・・・・・6略4G飽和■給水温
度 −・・・・・・80℃本発明は前記のよう
な構成をしているので、間接加熱式乾燥装置で脱水され
たケーキの含水率は低下し、ケーキの低位発熱量が高く
なくなって、ケーキが流動層炉内で自己燃焼するように
なるから、補助燃料を流動層炉に供給することが不要と
なり、更に流動層炉で発生した燃焼ガスの排熱なボイラ
で回収し、回収した熱を終局的には消化槽に投入される
生汚泥の加温に利用することがでとるから、消化ガスの
発生量を増大することがでと、消化ガスを利用した発電
装置等の効率を向上することかできる効果を有している
。■Combustion gas inlet temperature ・・・・・・900℃ ■Combustion gas outlet temperature -・・・・250℃ ■Combustion gas amount ・・・・・・・・・2490 Nd/■ Evaporation Amount: 110 ■ Steam pressure: 6 approximately 4 G saturation ■ Feed water temperature: - 80°C The present invention has the above-mentioned configuration. Therefore, the moisture content of the cake dehydrated in the indirect heating dryer decreases, the lower heating value of the cake is no longer high, and the cake self-combusts in the fluidized bed furnace. There is no need to supply it to the bed furnace, and the waste heat of the combustion gas generated in the fluidized bed furnace is recovered in the boiler, and the recovered heat is ultimately used to heat the raw sludge that is fed into the digester. This has the effect of increasing the amount of digestion gas generated and improving the efficiency of power generation devices and the like that utilize digestion gas.
第1図は従来の方法のフローシート、第2図は本発明に
係る方法のフローシートである。
11・・・消化槽、 1!!・・・間接加熱式乾燥装置
、 14・・・流動層炉。
代理人 弁理士 佐 藤 正 年FIG. 1 is a flow sheet of a conventional method, and FIG. 2 is a flow sheet of a method according to the present invention. 11...Digestion tank, 1! ! ...Indirect heating type drying device, 14...Fluidized bed furnace. Agent Patent Attorney Masatoshi Sato
Claims (1)
水したのち、流動層炉で焼却し、前記間接加熱式乾燥装
置で脱水ケーキなさらに脱水する際に生じる排熱を消化
ImK投入される生汚泥の加温用に使用し、発電装置等
に供給される消化ガスの発生量を増大させることを特徴
とする下水汚泥の焼却地理方法。The dehydrated cake of digested sludge is further dehydrated in an indirect heating dryer, then incinerated in a fluidized bed furnace, and the waste heat generated during further dewatering of the dehydrated cake in the indirect heating dryer is used to digest the raw sludge that is input into ImK. 1. A method for incinerating sewage sludge, which is used for heating water and increasing the amount of digestive gas generated to be supplied to power generation equipment, etc.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP496082A JPS58123017A (en) | 1982-01-18 | 1982-01-18 | Incinerating treatment of sewage sludge |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP496082A JPS58123017A (en) | 1982-01-18 | 1982-01-18 | Incinerating treatment of sewage sludge |
Publications (1)
Publication Number | Publication Date |
---|---|
JPS58123017A true JPS58123017A (en) | 1983-07-22 |
Family
ID=11598144
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP496082A Pending JPS58123017A (en) | 1982-01-18 | 1982-01-18 | Incinerating treatment of sewage sludge |
Country Status (1)
Country | Link |
---|---|
JP (1) | JPS58123017A (en) |
Cited By (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
WO2000060287A1 (en) * | 1999-04-06 | 2000-10-12 | Compagnie Generale D'entreprises Automobile | Method and installation for treating the effluents of waste storage in an incineration plant |
CN103244957A (en) * | 2012-02-28 | 2013-08-14 | 四川宇阳环境工程有限公司 | Integral treatment method for drying and incinerating sludge |
Citations (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPS5553619A (en) * | 1978-10-10 | 1980-04-19 | Modo Chemetics Ab | Method of drying and burning waterrcontained solid fuel |
-
1982
- 1982-01-18 JP JP496082A patent/JPS58123017A/en active Pending
Patent Citations (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPS5553619A (en) * | 1978-10-10 | 1980-04-19 | Modo Chemetics Ab | Method of drying and burning waterrcontained solid fuel |
Cited By (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
WO2000060287A1 (en) * | 1999-04-06 | 2000-10-12 | Compagnie Generale D'entreprises Automobile | Method and installation for treating the effluents of waste storage in an incineration plant |
FR2792061A1 (en) * | 1999-04-06 | 2000-10-13 | D Entreprises Automobiles Comp | METHOD AND APPARATUS FOR PROCESSING JUICES OF WASTE STORAGE PITS INTENDED TO BE INCINERATED IN AN INCINERATION PLANT |
CN103244957A (en) * | 2012-02-28 | 2013-08-14 | 四川宇阳环境工程有限公司 | Integral treatment method for drying and incinerating sludge |
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