JPH06257731A - Sludge incinerating method - Google Patents
Sludge incinerating methodInfo
- Publication number
- JPH06257731A JPH06257731A JP5048113A JP4811393A JPH06257731A JP H06257731 A JPH06257731 A JP H06257731A JP 5048113 A JP5048113 A JP 5048113A JP 4811393 A JP4811393 A JP 4811393A JP H06257731 A JPH06257731 A JP H06257731A
- Authority
- JP
- Japan
- Prior art keywords
- sludge
- fluidized bed
- sewage sludge
- kiln
- bed kiln
- 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)
- Treatment Of Sludge (AREA)
Abstract
Description
【0001】[0001]
【産業上の利用分野】本発明は、流動炉を用いた下水汚
泥等の汚泥の焼却方法に関するものである。BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method for incinerating sludge such as sewage sludge using a fluidized furnace.
【0002】[0002]
【従来の技術】下水汚泥等の汚泥の処理方法として、流
動炉による焼却が広く知られている。ところでこの下水
汚泥焼却用の流動炉には、炉内に下水汚泥を直接投入す
るタイプと、水蒸気等の熱源を利用したスクリュー式の
間接加熱型乾燥機によって下水汚泥を所定水分まで乾燥
させたうえで炉内に投入するタイプとがある。しかし直
接投入タイプは炉内で乾燥を行う必要があるために処理
能力が低いという問題がある。一方、間接加熱型乾燥機
と流動炉を組み合わせた場合には、間接加熱型乾燥機の
ための広いスペースや熱源が必要となるという問題があ
る。2. Description of the Related Art Incineration in a fluidized furnace is widely known as a method for treating sludge such as sewage sludge. By the way, in the fluidized furnace for incinerating sewage sludge, after the sewage sludge is dried to a predetermined moisture by a type that directly inputs the sewage sludge into the furnace and a screw type indirect heating dryer that uses a heat source such as steam, There is a type to put in the furnace. However, the direct charging type has a problem that the processing capacity is low because it needs to be dried in the furnace. On the other hand, when the indirect heating dryer and the fluidized furnace are combined, there is a problem that a large space and a heat source for the indirect heating dryer are required.
【0003】また流動炉自体も通常の流動炉の他に、ガ
ス速度を高速化することにより粒子の外部循環を行わせ
るようにしたより高性能な循環流動炉が開発されてい
る。しかしこの循環流動炉では間接加熱型乾燥機により
下水汚泥を予め乾燥させたうえで投入しないと、下水汚
泥をガス流によって浮上させることができない。このた
め、高性能な循環流動炉を採用する場合には必然的に間
接加熱型乾燥機が必要となっていた。In addition to the ordinary fluidized-bed furnace, a higher-performance circulating fluidized-bed furnace has been developed, in which the gas velocity is increased to allow external circulation of particles. However, in this circulating fluidized furnace, the sewage sludge cannot be floated by the gas flow unless the sewage sludge is previously dried by an indirect heating type dryer and then added. Therefore, an indirect heating dryer is inevitably required when a high-performance circulating fluidized furnace is used.
【0004】[0004]
【発明が解決しようとする課題】本発明は上記した従来
の問題点を解決し、広いスペースや熱源を必要とせずに
流動炉による下水汚泥の焼却処理を可能とした汚泥の焼
却方法を提供するためになされたものである。DISCLOSURE OF THE INVENTION The present invention solves the above-mentioned conventional problems and provides a sludge incineration method capable of incinerating sewage sludge by a fluidized furnace without requiring a large space or a heat source. It was done for good.
【0005】[0005]
【課題を解決するための手段】上記の課題を解決するた
めになされた本発明は、流動炉の出口ガスから分離され
た高温の集塵灰を汚泥と混合し、汚泥を塊状あるいは粉
状としたうえ流動炉に投入することを特徴とするもので
ある。The present invention, which has been made to solve the above-mentioned problems, is to mix high temperature dust collecting ash separated from the outlet gas of a fluidized furnace with sludge to form sludge into a lump or a powder. In addition, it is characterized in that it is charged into a fluidized furnace.
【0006】[0006]
【実施例】以下に本発明を図示の下水汚泥についての実
施例のフローによって更に詳細に説明する。図1に示す
第1のフローにおいて、1は循環流動炉であり、その下
部の流動用空気吹き込み口2から吹き込まれる高速の流
動用空気により、炉内に循環流動を生じさせている。こ
の循環流動炉1の上部から取り出される高温の出口ガス
はサイクロン3に導かれ、気体(排ガス)と固体(集塵
灰)とに分離される。そして排ガスは排ガス処理装置へ
送られる。以上のプロセスは従来と同様である。EXAMPLES The present invention will be described in more detail below with reference to the flow chart of the examples of sewage sludge shown in the drawings. In the first flow shown in FIG. 1, reference numeral 1 is a circulating fluidized furnace, and high-speed fluidizing air blown from a fluidizing air blowing port 2 in the lower portion thereof causes a circulating flow in the furnace. The hot outlet gas taken out from the upper portion of the circulating fluidized furnace 1 is guided to the cyclone 3 and separated into gas (exhaust gas) and solid (dust collecting ash). Then, the exhaust gas is sent to the exhaust gas treatment device. The above process is similar to the conventional process.
【0007】一方、サイクロン3から回収された約800
℃の高温の集塵灰は混合機4へ送られ、ここで水分が約
80%の下水汚泥と混合される。この高温の集塵灰と混合
されることにより、下水汚泥は乾燥されて塊状あるいは
粉状となる。このため、集塵灰と混合後の下水汚泥を循
環流動炉1に投入すれば、流動層の圧損を増加させるこ
となく高速の流動用空気により吹き上げられ、効率よく
燃焼させることができる。On the other hand, about 800 recovered from cyclone 3
The high temperature dust collecting ash of ℃ is sent to the mixer 4, where the water content is about
Mixed with 80% sewage sludge. The sewage sludge is dried into a lump or a powder by being mixed with the high temperature collected ash. Therefore, when the sewage sludge mixed with the dust collecting ash is put into the circulating fluidized furnace 1, it can be blown up by the high-speed fluidizing air without increasing the pressure loss of the fluidized bed and efficiently combusted.
【0008】なお、集塵灰の混合率は下水汚泥等の汚泥
に対して重量比で100 〜200 %とする。この混合比が10
0 %未満であると汚泥の乾燥が不十分となり、循環流動
炉1に投入したときの循環や燃焼性が低下する。逆に混
合比が200 %を越えると、汚泥の投入量が相対的に減少
し、処理効率が低下することとなる。このように適当な
比率で両者を混合すれば、従来は無駄に廃棄されていた
集塵灰の保有熱を活用し、下水汚泥を乾燥させることが
できる。なお、本実施例においては循環流動炉について
説明したが、通常の流動炉でも相当の効果があることは
勿論である。The mixing ratio of the collected ash is 100 to 200% by weight with respect to sludge such as sewage sludge. This mixing ratio is 10
If it is less than 0%, the sludge is insufficiently dried, and the circulation and combustibility when charged into the circulating fluidized furnace 1 are deteriorated. On the other hand, if the mixing ratio exceeds 200%, the amount of sludge input will decrease relatively, and the treatment efficiency will decrease. If the two are mixed at an appropriate ratio in this way, it is possible to dry the sewage sludge by utilizing the retained heat of the dust ash that was conventionally wasted. Although the circulating fluidized furnace has been described in the present embodiment, it goes without saying that the ordinary fluidized furnace has a considerable effect.
【0009】図2に示す第2のフローにおいては、混合
機4から出た混合物が更に乾燥機5で乾燥されたうえ、
循環流動炉1に投入される。この乾燥機5は常温の空気
をブロアで吹き込み、水蒸気を除去するものであるが、
下水汚泥は混合機4において高温の集塵灰と混合される
ことにより塊状あるいは粉状とされているため、常温の
空気によっても容易に乾燥されることとなる。In the second flow shown in FIG. 2, the mixture discharged from the mixer 4 is further dried by the dryer 5, and
It is put into the circulating fluidized furnace 1. This dryer 5 blows air at room temperature with a blower to remove water vapor.
The sewage sludge is lumped or powdered by being mixed with high-temperature dust collecting ash in the mixer 4, so that it can be easily dried by air at room temperature.
【0010】[0010]
【発明の効果】以上のように、本発明の下水汚泥の焼却
方法によれば、従来はむだに廃棄されていた集塵灰の顕
熱を利用して下水汚泥を乾燥させることができ、下水汚
泥を高性能な流動炉によって燃焼性よく焼却することが
できる。また従来の間接加熱型乾燥機とは異なり、混合
機は小型のものでよいのでスペースの削減が可能とな
り、また余分の熱源を不用である。よって本発明は従来
の問題点を解消した下水汚泥等の汚泥の焼却方法とし
て、産業の発展に寄与するところは大である。As described above, according to the method for incinerating sewage sludge of the present invention, the sewage sludge can be dried by utilizing the sensible heat of the dust ash that was conventionally discarded in vain. Sludge can be incinerated with good combustibility in a high-performance fluidized furnace. Further, unlike the conventional indirect heating type dryer, the mixer can be small in size, so that the space can be reduced and an extra heat source is unnecessary. Therefore, the present invention greatly contributes to industrial development as a method for incinerating sludge such as sewage sludge that solves the conventional problems.
【図1】本発明の第1のフローを説明するフローシート
である。FIG. 1 is a flow sheet illustrating a first flow of the present invention.
【図2】本発明の第2のフローを説明するフローシート
である。FIG. 2 is a flow sheet illustrating a second flow of the present invention.
1 循環流動炉 3 サイクロン 4 混合機 5 乾燥機 1 Circulating flow furnace 3 Cyclone 4 Mixer 5 Dryer
Claims (2)
集塵灰を汚泥と混合し、汚泥を塊状あるいは粉状とした
うえ流動炉に投入することを特徴とする汚泥の焼却方
法。1. A method for incinerating sludge, which comprises mixing hot dust ash separated from the outlet gas of a fluidized furnace with sludge, making the sludge into a lump or a powder, and charging the sludge into the fluidized furnace.
気でさらに乾燥したうえ、流動炉に投入することを特徴
とする請求項1記載の汚泥の焼却方法。2. The method for incinerating sludge according to claim 1, wherein the sludge in the form of lumps or powder is further dried with air at room temperature and then put into a fluidized-bed furnace.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP5048113A JPH06257731A (en) | 1993-03-09 | 1993-03-09 | Sludge incinerating method |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP5048113A JPH06257731A (en) | 1993-03-09 | 1993-03-09 | Sludge incinerating method |
Publications (1)
Publication Number | Publication Date |
---|---|
JPH06257731A true JPH06257731A (en) | 1994-09-16 |
Family
ID=12794267
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP5048113A Pending JPH06257731A (en) | 1993-03-09 | 1993-03-09 | Sludge incinerating method |
Country Status (1)
Country | Link |
---|---|
JP (1) | JPH06257731A (en) |
Cited By (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP2007127386A (en) * | 2005-11-07 | 2007-05-24 | Mitsubishi Materials Techno Corp | Preprocessing method of powder to be processed, and preprocessing method of incinerated ash to be processed |
CN105258134A (en) * | 2015-10-20 | 2016-01-20 | 上海理工大学 | Coal-sludge composite firing system based on dual-medium flue gas drying and circulating fluidized bed boiler |
WO2019193671A1 (en) * | 2018-04-04 | 2019-10-10 | 太平洋エンジニアリング株式会社 | Apparatus and method for treating organic sludge |
Citations (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPH02229587A (en) * | 1989-03-01 | 1990-09-12 | Miike Tekkosho:Kk | Fermenting device for organic waste |
JPH03221183A (en) * | 1990-01-26 | 1991-09-30 | Hiroshi Shimizu | Apparatus for fermentation treatment of garbage |
-
1993
- 1993-03-09 JP JP5048113A patent/JPH06257731A/en active Pending
Patent Citations (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPH02229587A (en) * | 1989-03-01 | 1990-09-12 | Miike Tekkosho:Kk | Fermenting device for organic waste |
JPH03221183A (en) * | 1990-01-26 | 1991-09-30 | Hiroshi Shimizu | Apparatus for fermentation treatment of garbage |
Cited By (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP2007127386A (en) * | 2005-11-07 | 2007-05-24 | Mitsubishi Materials Techno Corp | Preprocessing method of powder to be processed, and preprocessing method of incinerated ash to be processed |
CN105258134A (en) * | 2015-10-20 | 2016-01-20 | 上海理工大学 | Coal-sludge composite firing system based on dual-medium flue gas drying and circulating fluidized bed boiler |
WO2019193671A1 (en) * | 2018-04-04 | 2019-10-10 | 太平洋エンジニアリング株式会社 | Apparatus and method for treating organic sludge |
US11591246B2 (en) | 2018-04-04 | 2023-02-28 | Taiheiyo Engineering Corporation | Organic sludge treatment device and treatment method |
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Legal Events
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A02 | Decision of refusal |
Free format text: JAPANESE INTERMEDIATE CODE: A02 Effective date: 19990402 |