JP3046776B2 - Driftwood and garbage disposal method - Google Patents
Driftwood and garbage disposal methodInfo
- Publication number
- JP3046776B2 JP3046776B2 JP9043113A JP4311397A JP3046776B2 JP 3046776 B2 JP3046776 B2 JP 3046776B2 JP 9043113 A JP9043113 A JP 9043113A JP 4311397 A JP4311397 A JP 4311397A JP 3046776 B2 JP3046776 B2 JP 3046776B2
- Authority
- JP
- Japan
- Prior art keywords
- driftwood
- combustion
- rotary furnace
- refuse
- oxygen
- 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 - Fee Related
Links
Classifications
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02E—REDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
- Y02E50/00—Technologies for the production of fuel of non-fossil origin
- Y02E50/30—Fuel from waste, e.g. synthetic alcohol or diesel
Landscapes
- Incineration Of Waste (AREA)
- Processing Of Solid Wastes (AREA)
Description
【0001】[0001]
【発明の属する技術分野】本発明は、水力発電所のダム
等から回収される流木及び塵芥の処理方法に関するもの
である。BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method for treating driftwood and dust collected from a dam of a hydroelectric power plant.
【0002】[0002]
【従来の技術】水力発電所のダム等からは、上流からの
流木の他に、草木、ペットボトル、ゴミ等の塵芥が回収
される。従来、これらの回収物はすべて焼却炉で焼却し
ていたが、水分の多い回収物の焼却のために多くの燃料
が必要となり、また流木のような有価物もすべて焼却し
てしまうという問題があった。2. Description of the Related Art In addition to driftwood from upstream, trash such as vegetation, plastic bottles, and garbage are collected from dams and the like of hydroelectric power plants. Conventionally, all of these collected materials were incinerated in an incinerator.However, there is a problem in that a large amount of fuel is required for incineration of highly watery collected materials, and all valuable resources such as driftwood are also incinerated. there were.
【0003】[0003]
【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、塵芥は従来のように焼却する一方、
流木を炭化させて有価物として回収することができる経
済性に優れた流木及び塵芥の処理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 problems in the prior art.
The present invention has been made to provide a method for treating driftwood and garbage which is excellent in economical efficiency and can be recovered as valuable resources by carbonizing the driftwood.
【0004】[0004]
【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の流木及び塵芥の処理方法は、塵芥
焼却用の回転炉を酸素過剰燃焼と酸素抑制燃焼とに切り
換え可能な構造としておき、塵芥はこの回転炉で酸素過
剰燃焼により焼却する一方、流木は予め所定サイズに破
砕し更に所定水分まで乾燥したうえ前記回転炉に投入
し、酸素抑制燃焼により炭化することを特徴とするもの
である。なおこの場合、流木は一片が15〜50mmのサイズ
に破砕し、更に水分が40%以下となるまで乾燥させるこ
とが好ましく、また炭化の際に発生する可燃ガスを燃焼
させ、乾燥に利用することが好ましい。DISCLOSURE OF THE INVENTION In order to solve the above-mentioned problems, a method for treating driftwood and refuse according to the present invention has a structure in which a rotary furnace for refuse incineration can be switched between oxygen-excess combustion and oxygen-suppressed combustion. The waste is incinerated in this rotary furnace by excess oxygen combustion, while the driftwood is crushed to a predetermined size in advance, dried to a predetermined moisture, then put into the rotary furnace, and carbonized by oxygen-suppressed combustion. Things. In this case, it is preferable that a piece of the driftwood be crushed to a size of 15 to 50 mm and dried until the water content becomes 40% or less, and combustible gas generated during carbonization be burned and used for drying. Is preferred.
【0005】本発明の流木及び塵芥の処理方法によれ
ば、同一の回転炉を利用して塵芥の焼却と流木の炭化と
を行うことができ、流木を有価物として回収することが
できる。しかも炭化の際に発生する可燃ガスを乾燥に利
用することによって燃料の使用量を削減し、エネルギー
の無駄をなくすることができる。According to the method for treating driftwood and refuse of the present invention, refuse can be incinerated and driftwood carbonized using the same rotary furnace, and the driftwood can be collected as valuable resources. Moreover, by using the combustible gas generated at the time of carbonization for drying, the amount of fuel used can be reduced, and waste of energy can be eliminated.
【0006】[0006]
【発明の実施の形態】次に、本発明の好ましい実施の形
態を示す。図1は本発明に用いられる機器の構成を示す
フローシートであり、1は塵芥の焼却と流木の炭化とに
用いられる回転炉である。この回転炉1は図2に示すよ
うにローラ2によって支持された円筒状の炉体3と、酸
素過剰燃焼と酸素抑制燃焼とができるバーナ4とを備え
ている。また炉体3は漏込空気が少ない構造となってお
り、炉体3の端部から投入された塵芥を回転させつつ酸
素過剰燃焼により焼却することができるのみならず、バ
ーナ4を酸素抑制燃焼に切り換えて炉体3の端部から投
入された流木の炭化を行わせることも可能となってい
る。なお、炉体3の上部には炭化の際に発生する可燃ガ
ス(乾留ガス)を燃焼させるアフターバーナー5が設け
られている。以下に図1のフローシートに沿って、本発
明の流木及び塵芥の処理方法を説明する。Next, preferred embodiments of the present invention will be described. FIG. 1 is a flow sheet showing the configuration of equipment used in the present invention, and 1 is a rotary furnace used for incineration of garbage and carbonization of driftwood. As shown in FIG. 2, the rotary furnace 1 includes a cylindrical furnace body 3 supported by rollers 2 and a burner 4 capable of performing oxygen excess combustion and oxygen suppression combustion. Further, the furnace body 3 has a structure in which the amount of leaked air is small, so that not only can the refuse introduced from the end of the furnace body 3 be incinerated by the excessive oxygen combustion while rotating, but also the burner 4 can be burned by the oxygen-suppressed combustion. And carbonization of driftwood introduced from the end of the furnace body 3 is also possible. In addition, an afterburner 5 that burns combustible gas (carbonized gas) generated during carbonization is provided on the upper part of the furnace body 3. The method for treating driftwood and dust according to the present invention will be described below with reference to the flow sheet of FIG.
【0007】まず水力発電所のダム等から回収された流
木や塵芥は仮置き場に集められ、流木と塵芥とに分離し
ておく。一般に流木は見掛け比重が0.2 〜0.3 、水分が
50〜60%であり、塵芥は見掛け比重が0.2 程度、水分が
60〜70%のものである。塵芥は必要に応じて破砕機6で
破砕し、回転式の乾燥機7で乾燥させたうえで回転炉1
に投入され、バーナ4を酸素過剰燃焼として通常通り焼
却される。このとき、回転炉1のバーナ4には燃料タン
ク8から重油が供給され、燃焼空気ファン9から燃焼空
気が供給される。焼却灰は灰移送コンベヤ10を経由して
灰ホッパ11に取り出される。First, driftwood and dust collected from a dam of a hydroelectric power plant are collected in a temporary storage place and separated into driftwood and dust. Generally, driftwood has an apparent specific gravity of 0.2 to 0.3 and moisture
Garbage has an apparent specific gravity of about 0.2,
60-70%. The garbage is crushed by a crusher 6 if necessary, dried by a rotary dryer 7 and then
And burner 4 is burned as usual with excess oxygen combustion. At this time, heavy oil is supplied to the burner 4 of the rotary furnace 1 from the fuel tank 8, and combustion air is supplied from the combustion air fan 9. The incinerated ash is taken out to the ash hopper 11 via the ash transfer conveyor 10.
【0008】一方、流木は均一に炭化させるとともに炭
化時間の短縮化を図るため、破砕機6で所定サイズに破
砕する。破砕機6としては例えば2軸のロールクラッシ
ュ方式のものが用いられ、後記するように一片が15〜50
mmのサイズに破砕することが好ましい。その後更に、回
転式の乾燥機7で好ましくは水分が40%以下となるまで
乾燥させる。乾燥機7には熱風発生機12から熱風が送ら
れる。On the other hand, the driftwood is crushed to a predetermined size by the crusher 6 in order to uniformly carbonize and shorten the carbonization time. As the crusher 6, for example, a two-axis roll crush type is used, and one piece is 15 to 50 as described later.
Crushing to a size of mm is preferred. Thereafter, drying is further performed by a rotary drier 7 until the water content becomes preferably 40% or less. Hot air is sent from the hot air generator 12 to the dryer 7.
【0009】このように予め破砕され乾燥された流木は
回転炉1に投入され、バーナ4を酸素抑制燃焼として炭
化される。このとき流木は回転されながら均一に加熱さ
れ、表面から炭化が進行する。その後、炭化物は灰移送
コンベヤ10に取り出されて水噴霧を受け、炭化の進行を
停止させたうえで灰ホッパ11に取り出される。この炭化
の際に発生する可燃ガスは前述したようにアフターバー
ナー5で燃焼され、得られた高温の燃焼ガスは乾燥機7
に供給されて乾燥に利用される。またアフターバーナー
5及び乾燥機7の排ガスはサイクロン13、14で処理され
たうえ、排気筒15から排気される。The driftwood thus crushed and dried in advance is put into the rotary furnace 1, and the burner 4 is carbonized as oxygen-suppressed combustion. At this time, the driftwood is uniformly heated while being rotated, and carbonization proceeds from the surface. Thereafter, the carbide is taken out to the ash transfer conveyor 10 and subjected to water spray. The progress of the carbonization is stopped, and the carbide is taken out to the ash hopper 11. The combustible gas generated during the carbonization is burned by the afterburner 5 as described above, and the obtained high-temperature combustion gas is dried by the dryer 7.
And used for drying. The exhaust gas from the afterburner 5 and the dryer 7 is processed by the cyclones 13 and 14 and then exhausted from the exhaust pipe 15.
【0010】上記の通り、本発明によれば同一の回転炉
1によって塵芥の焼却と流木の炭化とを行い、有価物で
ある炭を得ることができる。次の表1は流木の破砕サイ
ズが炭化に及ぼす影響を示すものであり、表2は含水率
が炭化に及ぼす影響を示すものである。これらのデータ
から、流木の破砕サイズは15〜50mmが好ましく、水分は
40%以下とすることが好ましいことが分かる。As described above, according to the present invention, refuse is incinerated and driftwood is carbonized by the same rotary furnace 1 to obtain valuable charcoal. Table 1 below shows the effect of the size of the driftwood on carbonization, and Table 2 shows the effect of the water content on carbonization. From these data, the crush size of driftwood is preferably 15 to 50 mm,
It is understood that the content is preferably set to 40% or less.
【0011】[0011]
【表1】 [Table 1]
【0012】[0012]
【表2】 [Table 2]
【0013】[0013]
【発明の効果】以上に説明したように、本発明の流木及
び塵芥の処理方法によれば、水力発電所のダム等から回
収される塵芥を焼却するとともに、同一の回転炉を用い
て流木を炭化させ、有用な炭を得ることができる。この
ため全てを一律に焼却していた従来の処理方法に比較し
て経済性に優れ、また炭化の際に発生する可燃ガスを乾
燥に利用すればエネルギーも削減できる利点がある。As described above, according to the method for treating driftwood and refuse of the present invention, refuse collected from a dam of a hydroelectric power plant is incinerated, and the driftwood is removed using the same rotary furnace. It can be carbonized to obtain useful charcoal. For this reason, there is an advantage in that it is more economical than a conventional treatment method in which all of them are uniformly incinerated, and energy can be reduced by using a combustible gas generated during carbonization for drying.
【図面の簡単な説明】[Brief description of the drawings]
【図1】本発明に用いられる機器の構成を示すフローシ
ートである。FIG. 1 is a flow sheet showing a configuration of a device used in the present invention.
【図2】本発明に用いられる回転炉の斜視図である。FIG. 2 is a perspective view of a rotary furnace used in the present invention.
1 回転炉、2 ローラ、3 炉体、4 バーナ、5
アフターバーナー、6破砕機、7 回転式の乾燥機、8
燃料タンク、9 燃焼空気ファン、10 灰移送コンベ
ヤ、11 灰ホッパ、12 熱風発生機、13 サイクロン、
14 サイクロン、15 排気筒1 rotary furnace, 2 rollers, 3 furnaces, 4 burners, 5
Afterburner, 6 crusher, 7 tumble dryer, 8
Fuel tank, 9 combustion air fan, 10 ash transfer conveyor, 11 ash hopper, 12 hot air generator, 13 cyclone,
14 cyclones, 15 exhaust stacks
───────────────────────────────────────────────────── フロントページの続き (51)Int.Cl.7 識別記号 FI B09B 3/00 303M (58)調査した分野(Int.Cl.7,DB名) F23G 5/033 ZAB B09B 3/00 ZAB F23G 5/04 ZAB F23G 5/20 ZAB ──────────────────────────────────────────────────続 き Continued on the front page (51) Int.Cl. 7 identification code FI B09B 3/00 303M (58) Fields investigated (Int. Cl. 7 , DB name) F23G 5/033 ZAB B09B 3/00 ZAB F23G 5/04 ZAB F23G 5/20 ZAB
Claims (3)
素抑制燃焼とに切り換え可能な構造としておき、塵芥は
この回転炉で酸素過剰燃焼により焼却する一方、流木は
予め所定サイズに破砕し更に所定水分まで乾燥したうえ
前記回転炉に投入し、酸素抑制燃焼により炭化すること
を特徴とする流木及び塵芥の処理方法。A rotary furnace for incineration of refuse is provided with a structure capable of switching between excess oxygen combustion and oxygen-suppressed combustion. Dust is incinerated in this rotary furnace by excess oxygen combustion, while the driftwood is crushed to a predetermined size in advance. A method for treating driftwood and refuse, further comprising drying the water to a predetermined moisture, charging the water into the rotary furnace, and carbonizing by oxygen-suppressed combustion.
し、更に水分が40%以下となるまで乾燥させる請求項1
に記載の流木及び塵芥の処理方法。2. A driftwood piece is crushed to a size of 15 to 50 mm and further dried until the water content becomes 40% or less.
The method for treating driftwood and garbage according to the above.
せ、乾燥に利用する請求項1に記載の流木及び塵芥の処
理方法。3. The method for treating driftwood and refuse according to claim 1, wherein the combustible gas generated during carbonization is burned and used for drying.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP9043113A JP3046776B2 (en) | 1997-02-27 | 1997-02-27 | Driftwood and garbage disposal method |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP9043113A JP3046776B2 (en) | 1997-02-27 | 1997-02-27 | Driftwood and garbage disposal method |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPH10238729A JPH10238729A (en) | 1998-09-08 |
| JP3046776B2 true JP3046776B2 (en) | 2000-05-29 |
Family
ID=12654786
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP9043113A Expired - Fee Related JP3046776B2 (en) | 1997-02-27 | 1997-02-27 | Driftwood and garbage disposal method |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JP3046776B2 (en) |
Families Citing this family (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| FR2870154B1 (en) * | 2004-05-13 | 2012-12-14 | Bio 3D Applic | BIO-THERMAL METHOD AND SYSTEM FOR STABILIZING LUMBER |
| CN104428843B (en) * | 2012-06-29 | 2017-05-17 | 太平洋水泥株式会社 | Radioactive cesium removal device |
| CN110006045A (en) * | 2019-03-08 | 2019-07-12 | 广州清风环保科技有限公司 | A kind of solid waste minimizing incineration pretreatment device |
-
1997
- 1997-02-27 JP JP9043113A patent/JP3046776B2/en not_active Expired - Fee Related
Also Published As
| Publication number | Publication date |
|---|---|
| JPH10238729A (en) | 1998-09-08 |
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Legal Events
| Date | Code | Title | Description |
|---|---|---|---|
| A01 | Written decision to grant a patent or to grant a registration (utility model) |
Free format text: JAPANESE INTERMEDIATE CODE: A01 Effective date: 20000303 |
|
| LAPS | Cancellation because of no payment of annual fees |