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JPS621483B2 - - Google Patents
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JPS621483B2 - - Google Patents

Info

Publication number
JPS621483B2
JPS621483B2 JP10011882A JP10011882A JPS621483B2 JP S621483 B2 JPS621483 B2 JP S621483B2 JP 10011882 A JP10011882 A JP 10011882A JP 10011882 A JP10011882 A JP 10011882A JP S621483 B2 JPS621483 B2 JP S621483B2
Authority
JP
Japan
Prior art keywords
combustibles
calorie
waste
melting
incinerator
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
Application number
JP10011882A
Other languages
Japanese (ja)
Other versions
JPS58217111A (en
Inventor
Yotaro Taniguchi
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.)
Kubota Corp
Original Assignee
Kubota Corp
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 Kubota Corp filed Critical Kubota Corp
Priority to JP10011882A priority Critical patent/JPS58217111A/en
Publication of JPS58217111A publication Critical patent/JPS58217111A/en
Publication of JPS621483B2 publication Critical patent/JPS621483B2/ja
Granted legal-status Critical Current

Links

Classifications

    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23GCREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
    • F23G5/00Incineration of waste; Incinerator constructions; Details, accessories or control therefor
    • F23G5/02Incineration of waste; Incinerator constructions; Details, accessories or control therefor with pretreatment

Landscapes

  • Engineering & Computer Science (AREA)
  • Mechanical Engineering (AREA)
  • General Engineering & Computer Science (AREA)
  • Gasification And Melting Of Waste (AREA)

Description

【発明の詳細な説明】 本発明は廃棄物の焼却・溶融処理方法に関し、
詳細には都市廃棄物等の廃棄物中に含まれる低カ
ロリー可燃物、高カロリー可燃物及び不燃物を予
め分離した後、適当に分流させることによつて燃
焼効率及び溶融処理効率を高める方法に関するも
のである。
[Detailed description of the invention] The present invention relates to a method for incinerating and melting waste,
In detail, it relates to a method for increasing combustion efficiency and melting efficiency by separating low-calorie combustibles, high-calorie combustibles, and non-combustibles contained in waste such as municipal waste in advance and then appropriately dividing the flow. It is something.

都市廃棄物には、紙、木材等の低カロリー可燃
物;ゴム、プラスチツク等の高カロリー可燃物;
厨芥等と共に、灰、瓦礫、ガラス等の可燃物が含
まれる為、その燃焼性は常に良好とは言えず、焼
却処理に当つては種々の工夫が必要になる。殊に
可燃物(特に灰分)を多量に含む廃棄物は発熱量
が低く混合された状態での焼却処理は難しいの
で、焼却炉へ投入するに先立つて可燃物から分離
除去する必要がある。
Municipal waste includes low-calorie combustibles such as paper and wood; high-calorie combustibles such as rubber and plastic;
Since it contains combustible materials such as ash, rubble, and glass along with kitchen waste, its combustibility is not always good, and various measures are required for incineration. In particular, waste containing a large amount of combustible materials (particularly ash) has a low calorific value and is difficult to incinerate in a mixed state, so it is necessary to separate it from the combustible materials before feeding it into an incinerator.

即ち該不燃物はそれ自身発熱力を持たず燃焼に
何ら寄与しないと共に、特に灰分については吸水
性が強く団塊状となつて焼却炉に投入されるの
で、その時、水分を炉内に持ち込み低位発熱量を
低下させる原因になる他、炉内の燃焼熱を受けて
乾燥すると、再び微粉に戻つて、ごみ同士の間隙
をうずめ、あるいは更に進んで融着物となつて通
気性を阻害することにより、ごみの燃焼を妨げ
る。
In other words, the non-combustibles themselves do not have heat generating power and do not contribute to combustion, and the ash in particular has strong water absorption and is put into the incinerator in the form of lumps, so at that time, water is brought into the furnace and produces low-level heat generation. In addition to causing a decrease in the amount of dust, when it dries due to the heat of combustion in the furnace, it returns to fine powder and fills the gaps between dust, or it progresses further and becomes a fused substance that obstructs air permeability. Prevents the combustion of garbage.

一方石油情勢の悪化は益々進み、工業的には例
えばボイラー燃料として石炭が利用され、又地域
によつては家庭の暖房用等として練炭や豆炭が広
く利用される様になつてきた。その為都市ごみの
組成が表われて灰分比率が大きくなる傾向にあ
り、焼却炉内へ灰分が持ち込まれることによる前
述の様な幣害が地域によつて無視できなくなつて
きた。
On the other hand, the oil situation has continued to deteriorate, and coal has come to be used industrially as boiler fuel, and in some regions, charcoal briquettes and charcoal have come to be widely used for home heating. As a result, the composition of municipal waste has changed and the ash content has tended to increase, and the above-mentioned damage caused by ash being brought into the incinerator has become impossible to ignore in some regions.

この様な可燃物と不燃物の分離手段としては例
えば形状、嵩比重、粒度等の違いを利用して行な
われるものがあるが、いずれの方法を利用するに
しても両者を完全に分離することは実質上不可能
であり、分離されたた不燃物の中には相当量の可
燃物が混入する。その為これをそのまま埋立地等
に投棄すると、混入した可燃物(有機物)の腐敗
によつて臭気や汚水が発生し環境保全上問題にな
る。
There are methods for separating combustibles and non-combustibles, such as by making use of differences in shape, bulk specific gravity, particle size, etc., but whichever method is used, it is important to completely separate the two. It is virtually impossible to do so, and a considerable amount of combustible materials will be mixed into the separated non-combustible materials. Therefore, if this is dumped as is in a landfill or the like, odors and sewage will be generated due to the decomposition of the combustible matter (organic matter) mixed in, which will pose a problem in terms of environmental conservation.

一方分離された可燃物は焼却処理によつて減容
されるが、その焼却残渣(灰、ダスト、汚泥等)
には多量の有害重金属が含まれているので、その
まま最終処分すると重金属溶出による環境破壊が
発生する。そこで焼却処理設備においては、重金
属を含む焼却灰や残渣に適当な固化剤(セメン
ト、アスフアルト等)を加えて固化処理した後、
埋立あるいは海洋投棄している。しかしながら固
化処理法は多大のコストを要し、又環境汚染を皆
無にできるという保証もない。
On the other hand, the separated combustibles are reduced in volume through incineration, but the incineration residue (ash, dust, sludge, etc.)
contains a large amount of toxic heavy metals, so if they are disposed of as is, they will cause environmental damage due to the elution of heavy metals. Therefore, in incineration equipment, after solidifying the incineration ash and residue containing heavy metals by adding an appropriate solidifying agent (cement, asphalt, etc.),
Landfill or ocean dumping. However, the solidification treatment method requires a large amount of cost, and there is no guarantee that environmental pollution can be completely eliminated.

本発明は、こうした事情に着目してなされたも
のであつて、その目的は焼却処理設備から排出さ
れる分離不燃物や燃焼残渣等を環境保全上無害な
性状となし得る様な廃棄物処理方法を提供しよう
とするものである。
The present invention has been made in view of these circumstances, and its purpose is to provide a waste treatment method that can make separated incombustibles, combustion residues, etc. discharged from incineration facilities harmless from an environmental perspective. This is what we are trying to provide.

しかして本発明の廃棄物焼却・溶融処理方法と
は、廃棄物を低カロリー可燃物、高カロリー可燃
物及び不燃物に分離し、低カロリー可燃物は焼却
炉に投入した燃焼・灰化させ、焼却炉からの排出
灰や残渣は鉄分を回収した後、前記不燃物及び高
カロリー可燃物と共に溶融炉へ投入し、助燃バー
ナで溶融・スラグ化させ、他方焼却炉及び溶融炉
からの排ガスを集じん装置に導いて集められるダ
ストも前記溶融炉に導いて溶融・スラグ化し、該
溶融スラグを冷却固化させる点に要旨が存在す
る。
Therefore, the waste incineration/melting treatment method of the present invention involves separating waste into low-calorie combustibles, high-calorie combustibles, and non-combustibles, and injecting the low-calorie combustibles into an incinerator for combustion and ashing. After recovering the iron content from the ash and residue discharged from the incinerator, they are put into a melting furnace together with the above-mentioned non-combustible materials and high-calorie combustible materials, where they are melted and turned into slag by an auxiliary combustion burner, while the exhaust gas from the incinerator and melting furnace is collected. The gist is that the dust collected by being guided to the dust device is also led to the melting furnace to be melted and turned into slag, and the molten slag is cooled and solidified.

前述の様な不燃物殊に燃焼灰を主成分とするも
のには相当量の有害重金属が含まれると共に、可
燃物との分離工程で混入する有機物等も相当量含
まれている。これらを無害化処理する方法として
は溶融処理方法が最も有効と考えられる。その理
由は溶融処理を行なうと前記混入有機物は焼失し
て腐敗等の問題を生じなくなると共に有害重金属
は他の不燃物と共にスラグ化して、その溶出も防
止されるからである。ところが不燃物は発熱源を
全く有していないので、これを溶融処理する為に
は大量の熱を与えなければならず燃料費がかさ
む。従つてこの様な技術を実用化する為には、少
ない燃料費で溶融処理を行ない得る様な技術を確
立しなければならない。そこで本発明者は廃棄物
中の可燃分を溶融処理の為の熱源として利用すれ
ば、上記の目的が達成できるのではないかと考
え、検討を進めた結果、可燃物中の高カロリー成
分を熱源として利用する本発明の方法に想到した
ものである。尚高カロリー可燃物は燃焼によつて
炉内温度を過度に高め、燃焼炉の寿命を短くする
という問題も指摘されているが、本発明ではこれ
を低カロリー可燃物と分離して低カロリー可燃物
のみを焼却処理する様にしているから焼却炉の寿
命を延長するという効果も得ることができる。し
かも高温加熱を要する溶融処理用の熱源として高
カロリー可燃物を利用する方法があるから、処理
設備全体としての熱的バランスも著しく改善され
る。
The above-mentioned non-combustible materials, especially those whose main component is combustion ash, contain not only a considerable amount of harmful heavy metals, but also a considerable amount of organic matter mixed in during the separation process from combustible materials. Melting treatment is considered to be the most effective method for rendering these materials harmless. The reason for this is that when the melting process is performed, the mixed organic matter is burned away and no longer causes problems such as spoilage, and the harmful heavy metals are turned into slag along with other incombustible materials, and their elution is also prevented. However, since non-combustible materials have no heat generation source, a large amount of heat must be applied to melt them, which increases fuel costs. Therefore, in order to put such technology into practical use, it is necessary to establish a technology that can perform melting processing with low fuel costs. Therefore, the inventor of the present invention thought that the above purpose could be achieved by using the combustible components in the waste as a heat source for melting processing, and after further investigation, the inventor found that the high calorie components in the combustible material could be used as a heat source for melting. This is the result of the idea of the method of the present invention, which is used as a. It has also been pointed out that high calorie combustible materials excessively raise the temperature inside the furnace when burned, shortening the life of the combustion furnace.However, in the present invention, this is separated from low calorie combustible materials. Since only the materials are incinerated, the lifespan of the incinerator can be extended. Moreover, since there is a method of using a high-calorie combustible material as a heat source for melting processing that requires high-temperature heating, the thermal balance of the processing equipment as a whole is also significantly improved.

以下実施例図面に沿つて本発明の構成及び作用
効果を説明するが、該実施例は本発明を制限する
性質のものではなく、前・後記の趣旨に徴して適
宜設計変更を加えること等は全て本発明の技術的
範囲に含まれる。
The configuration and effects of the present invention will be explained below with reference to the drawings, but the examples are not intended to limit the present invention, and design changes may be made as appropriate in keeping with the spirit of the above and below. All are included within the technical scope of the present invention.

第1図は本発明方法を適用した廃棄物処理シス
テムを例示するフロー説明図であり、収集されて
きた廃棄物Gは、まず貯留ピツトに投入される。
貯留ピツト内で堆積圧等によつて団塊状となつた
廃棄物は続いて破砕装置によつて小粒に破砕され
た後、分離装置に供給され低カロリー可燃物A、
高カロリー可燃物B、不燃物に分別される。尚破
砕装置及び分離装置の構成に特定の制限はない
が、前者としては機械的振動あるいは衝撃を与え
て団塊状物の結合を解放して殊に灰分等を小粒若
しくは粉状とする破砕装置を挙げることができ
る。又後者としては、例えば始めに粒度差を利用
して廃棄物を可燃物と不燃物(主に灰分)に分別
し、次いで比重差を利用して可燃物を低カロリー
の可燃物A(低比重)と高カロリー可燃物B(高
比重)に分別する装置が例示される。尚これらの
分別は可及的完全であることが望ましいが、実際
には相当の混入は避けることができず、又本発明
においては若干の混入は許される。分別された低
カロリーの不燃物Aは焼却炉(例えばストーカ式
焼却炉)に導入され焼却処理される。そして焼却
炉から排出される焼却残渣G1を鉄分回収装置
(例えば磁選器)に供給してFeを回収すると共
に、主に灰分からなる回収残渣G2は溶融炉へ供
給し、以下に示す如く不燃物と共に溶融処理す
る。
FIG. 1 is a flow diagram illustrating a waste treatment system to which the method of the present invention is applied. The collected waste G is first put into a storage pit.
The waste that has become agglomerated in the storage pit due to the accumulation pressure, etc. is then crushed into small particles by a crushing device, and then supplied to a separator to produce low-calorie combustibles A,
Separated into high calorie combustibles B and non-combustibles. Although there are no particular restrictions on the configuration of the crushing device and separation device, the former includes a crushing device that applies mechanical vibration or shock to release the bonds of nodules, especially ash, etc., into small particles or powder. can be mentioned. For the latter, for example, waste is first separated into combustibles and non-combustibles (mainly ash) using particle size differences, and then combustibles are separated into low-calorie combustibles A (low specific gravity) using differences in specific gravity. ) and high-calorie combustibles B (high specific gravity). Although it is desirable that these separations be as complete as possible, in reality, a considerable amount of contamination cannot be avoided, and some contamination is permitted in the present invention. The separated low-calorie incombustible materials A are introduced into an incinerator (for example, a stoker-type incinerator) and are incinerated. Then, the incineration residue G1 discharged from the incinerator is supplied to an iron recovery device (for example, a magnetic separator) to recover Fe, and the recovered residue G2 , which mainly consists of ash, is supplied to the melting furnace, as shown below. Melt it together with non-combustible materials.

一方高カロリーの可燃物B及び不燃物は溶融炉
へ投入され、重油焚き等の助燃バーナの加熱を受
けるが、この補助加熱によつて可燃物Bが着火・
燃焼し、その燃焼熱によつて炉内温度は1250〜
1500℃程度まで昇温するのに、前記不燃物及び焼
却残渣を容易に溶融状態とすることができる。尚
溶融炉内へ供給する不燃物の比率が多くなりすぎ
ると可燃物Bによる発熱量が不十分になつて助燃
材量を増加しなければならなくなり、一方可燃物
Bの量が相対的に多くなりすぎると発熱量が過度
になるので、溶融に必要な最適熱量を考慮して両
者の投入比率を調整するのがよい。尚このとき、
不燃物あるいは回収残渣G2に含まれる可燃物あ
るいは未燃物は燃焼し、生成する灰分は不燃物等
と共に溶融する。
On the other hand, high-calorie combustible material B and non-combustible material are put into a melting furnace and heated by an auxiliary combustion burner such as heavy oil firing, but this auxiliary heating causes combustible material B to ignite.
The temperature inside the furnace is 1250~ due to the heat of combustion.
Even though the temperature is raised to about 1500°C, the incombustible materials and incineration residue can be easily brought into a molten state. If the ratio of non-combustibles fed into the melting furnace becomes too large, the amount of heat generated by combustibles B will become insufficient and the amount of combustion aid will have to be increased, while the amount of combustibles B will be relatively large. If it becomes too much, the amount of heat generated will become excessive, so it is better to adjust the ratio of both inputs in consideration of the optimum amount of heat required for melting. Furthermore, at this time,
The combustibles or unburnt materials contained in the uncombustible materials or recovered residue G2 are burned, and the generated ash is melted together with the noncombustible materials.

他方焼却炉あるいは溶融炉から発生する排ガス
は、排ガス処理設備へ送つて処理されるが、該処
理設備の一部である集じん装置で集められたダス
トG4も、不燃物等と共に溶融処理してもかまわ
ない。溶融スラグG3は次いで溶融炉からスラグ
冷却装置へ導いて冷却固化されるが、有害重金属
は固化スラグと一体になつて内部に封入されるの
で、そのまま投棄しても溶出する恐れはない。尚
得られる固化スラグは安定な金属酸化物よりなる
硬質物であるので、骨材等として有効に利用する
ことができる。この場合急冷スラグは嵩比重が小
さいので路盤用バラスやコンクリート用軽量骨材
等として有用であり、徐冷スラグは硬度が高いの
で補強用骨材等として有用である。
On the other hand, exhaust gas generated from incinerators or melting furnaces is sent to exhaust gas treatment equipment for treatment, and the dust G 4 collected by the dust collector, which is part of the treatment equipment, is also melted and treated together with incombustible materials. It doesn't matter. The molten slag G3 is then led from the melting furnace to a slag cooling device where it is cooled and solidified, but the harmful heavy metals are sealed inside together with the solidified slag, so there is no risk of them leaching out even if the slag is dumped as is. Since the obtained solidified slag is a hard material made of stable metal oxide, it can be effectively used as an aggregate or the like. In this case, the rapidly cooled slag has a small bulk specific gravity, so it is useful as a ballast for roadbeds, a lightweight aggregate for concrete, etc., and the slowly cooled slag has a high hardness, so it is useful as a reinforcing aggregate, etc.

本考案の基本構成は上記の通りであるが、処理
設備に持ち込まれる廃棄物には可燃物及び不燃物
を個別に収集した物であり、この場合は、前記貯
留ピツトからのラインに代えて、破砕装置分別収
集された可燃物廃棄物S1を投入し、破砕装置以
降、前記と同様に処理すると共に、別途収集され
た不燃物S2を不燃物ラインに導入して溶融炉にお
いて前記と同様に焼却・溶融処理する方法を採る
こともできる。更に分別収集物と一括収集物を適
当に合流させて焼却・溶融処理することも可能で
ある。
The basic configuration of the present invention is as described above, but the waste brought into the treatment facility includes combustible and non-combustible materials collected separately, and in this case, instead of the line from the storage pit, The combustible waste S1 , which has been collected separately, is input into the crushing device and processed in the same way as described above, and the separately collected non-combustible waste S2 is introduced into the non-combustible line and processed in the melting furnace in the same manner as above. Alternatively, a method of incineration or melting may be adopted. Furthermore, it is also possible to appropriately combine the separated collection materials and the bulk collection materials for incineration and melting treatment.

本発明は概略以上の通り構成されており、不燃
物溶融用熱源として廃棄物中の高カロリー成分を
利用することよつて溶融に要する補給燃量を大幅
に節減し得ると共に、焼却炉の過熱による熱劣下
を抑制してその寿命を延長し得ることになつた。
The present invention is roughly configured as described above, and by using high-calorie components in waste as a heat source for melting noncombustibles, it is possible to significantly reduce the amount of supplementary fuel required for melting, and also to prevent overheating of the incinerator. It has become possible to suppress thermal deterioration and extend its life.

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

第1図は本発明に係る廃棄物溶融処理システム
のフロー図である。 G……廃棄物、G1……焼却残渣、G2……回収
残渣、G3……溶融スラグ、G4……ダスト、S1
…分別収集可燃性廃棄物、S2……分別収集不燃性
廃棄物。
FIG. 1 is a flow diagram of a waste melting treatment system according to the present invention. G...Waste, G1 ...Incineration residue, G2 ...Recovered residue, G3 ...Melted slag, G4 ...Dust, S1 ...
...separately collected combustible waste, S 2 ...separately collected non-combustible waste.

Claims (1)

【特許請求の範囲】[Claims] 1 都市廃棄物等を焼却並びに溶融処理する方法
であつて、廃棄物を低カロリーの可燃物、高カロ
リーの可燃物及び不燃物に分離し、低カロリー可
燃物は焼却炉に投入して燃焼・灰化させ、焼却炉
からの排出灰や残渣は鉄分を回収した後、前記不
燃物及び高カロリー可燃物と共に溶融炉へ投入
し、助燃バーナで溶融・スラグ化させ、他方焼却
炉及び溶融炉からの排ガスを、集じん装置に導い
て集められるダストも前記溶融炉に導いて溶融・
スラグ化し、該溶融スラグを冷却固化させること
を特徴とする廃棄物焼却・溶融処理方法。
1. A method of incinerating and melting municipal waste, etc., in which waste is separated into low-calorie combustibles, high-calorie combustibles, and non-combustibles, and the low-calorie combustibles are put into an incinerator and burned. After collecting the iron content from the ash and residue discharged from the incinerator, they are put into a melting furnace together with the above-mentioned non-combustible materials and high-calorie combustible materials, where they are melted and turned into slag by an auxiliary combustion burner, and then removed from the incinerator and melting furnace. The exhaust gas is led to the dust collector and the dust collected is also led to the melting furnace and melted.
A method for incinerating and melting waste, characterized by converting it into slag, and cooling and solidifying the molten slag.
JP10011882A 1982-06-10 1982-06-10 Waste incineration/melting treatment method Granted JPS58217111A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP10011882A JPS58217111A (en) 1982-06-10 1982-06-10 Waste incineration/melting treatment method

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP10011882A JPS58217111A (en) 1982-06-10 1982-06-10 Waste incineration/melting treatment method

Publications (2)

Publication Number Publication Date
JPS58217111A JPS58217111A (en) 1983-12-17
JPS621483B2 true JPS621483B2 (en) 1987-01-13

Family

ID=14265431

Family Applications (1)

Application Number Title Priority Date Filing Date
JP10011882A Granted JPS58217111A (en) 1982-06-10 1982-06-10 Waste incineration/melting treatment method

Country Status (1)

Country Link
JP (1) JPS58217111A (en)

Families Citing this family (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS6433416A (en) * 1987-07-29 1989-02-03 Hitachi Shipbuilding Eng Co Disposal method for dioxine-containing ash in incineration of solid waste
JPH02261588A (en) * 1989-03-31 1990-10-24 Katsumi Takao Method for utilizing waste

Also Published As

Publication number Publication date
JPS58217111A (en) 1983-12-17

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