JPH094828A - Disposal method of incineration ash - Google Patents
Disposal method of incineration ashInfo
- Publication number
- JPH094828A JPH094828A JP15004195A JP15004195A JPH094828A JP H094828 A JPH094828 A JP H094828A JP 15004195 A JP15004195 A JP 15004195A JP 15004195 A JP15004195 A JP 15004195A JP H094828 A JPH094828 A JP H094828A
- Authority
- JP
- Japan
- Prior art keywords
- ash
- melting
- disposal
- heating
- incineration ash
- 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
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- Gasification And Melting Of Waste (AREA)
Abstract
(57)【要約】
【構成】廃棄物を焼却して生じた焼却灰を、焼却炉を構
築せずに加熱溶融し、冷却して固化スラグとして処分す
る方法であって、焼却灰を直接溶融しながら実質的に連
続に処分場所に供給し、冷却する処分方法、並びに処分
する焼却灰を、予め処分場所に堆積させた後、加熱溶融
し、続いて冷却により固化させる処分方法。
【効果】前記2つの焼却灰の処分方法では、通常廃棄物
最終処分場所においてそのまま埋設される焼却灰を更に
減容化して処分することができる。またこのような処分
を行うにあたって、溶融のための処分場所とは別の土地
や溶融炉を必要とせず、更に特別の冷却装置等をも必要
としないので、コスト的に有利に焼却灰を減容化でき、
処分場所の確保を同量処理するのに略半減させることが
できる。
(57) [Summary] [Structure] Incinerator ash produced by incinerating waste is heated and melted without constructing an incinerator, cooled and disposed of as solidified slag. However, a disposal method of supplying to the disposal site substantially continuously and cooling, and a disposal method of depositing the incineration ash to be disposed in advance at the disposal site, heating and melting, and then solidifying by cooling. [Effect] According to the above-mentioned two disposal methods for incinerated ash, the incinerated ash that is buried as it is at the final waste disposal site can be further reduced in volume and disposed of. In addition, such disposal does not require a land or melting furnace separate from the disposal site for melting, and does not require a special cooling device, etc. Can be stored,
Securing the disposal site can be cut in half to treat the same amount.
Description
【0001】[0001]
【産業上の利用分野】本発明は、都市ゴミ等の廃棄物を
焼却して生じた焼却灰を、処分場所において加熱溶融
し、冷却して固化スラグとすることにより焼却灰を容易
に減容化して処分する焼却灰の処分方法に関する。BACKGROUND OF THE INVENTION The present invention easily reduces the volume of incinerated ash by heating and melting the incinerated ash produced by incinerating waste such as municipal waste at the disposal site and cooling it to solidified slag. The present invention relates to a method of disposing of incinerated ash that is turned into waste.
【0002】[0002]
【従来の技術】都市ゴミ等の廃棄物は、最終処分地であ
る埋立地に埋め立てられるのが一般的である。しかし廃
棄物の量は年々増加しており、埋立地の確保等が問題に
なっているため、廃棄物の減容化が種々進められ実施さ
れている。この廃棄物の減容化としては、特に一般廃棄
物の場合、焼却炉等で焼却して減容し、この焼却により
生じた焼却灰を埋立地に運搬して埋設する方法が最も多
く採用されている。2. Description of the Related Art Waste such as municipal waste is generally landfilled in a landfill, which is the final disposal site. However, the amount of waste is increasing year by year, and securing landfills is becoming a problem, so various volume reductions of waste are being implemented. The most common method for reducing the volume of this waste is to incinerate it in an incinerator to reduce the volume and transport the incinerated ash generated by this incineration to a landfill site for burial. ing.
【0003】しかしながら、このような焼却処理により
生成する焼却灰は、気孔を多く含み極めて嵩高であるた
め、廃棄物の分別を徹底して不燃ゴミを完全に除去した
場合であっても排出される焼却灰容積を10%以下とす
ることは困難であり、更なる減容化方法の開発が進めら
れている。However, since the incinerated ash produced by such incineration process has a large number of pores and is extremely bulky, it is discharged even when the incombustible dust is completely removed by thoroughly separating the waste. It is difficult to reduce the volume of incinerated ash to 10% or less, and further volume reduction methods are being developed.
【0004】例えば、焼却灰を、1400℃程度の高温
で溶融処理し、金属分が含まれていても、溶融金属分を
比重分離し、スラグを連続的に排出できる溶融炉が開発
されている。このような高温での処理を可能とした特殊
な溶融炉を用いる方法では、廃棄物の減容化を5%程度
まで行なうことができ、しかも焼却灰に含有される金
属、更には生じるスラグ等を回収して資源の再利用をも
可能にすることができるという利点を有する。For example, a melting furnace has been developed which can incinerate incinerated ash at a high temperature of about 1400 ° C., separates the molten metal content by specific gravity and continuously discharges slag even if it contains a metal content. . With such a method using a special melting furnace capable of processing at a high temperature, the volume of the waste can be reduced to about 5%, and the metal contained in the incinerated ash and further the slag generated, etc. It has the advantage that it can be recovered and reuse of resources can be made possible.
【0005】しかしながら、このような特殊な溶融炉を
用いる方法では、高温に耐え得る溶融炉と、スラグ等を
回収するための特殊な冷却粉砕装置と、場合によっては
溶融金属の分離設備も必要であり、焼却施設建設のため
の広大な土地が必要である。しかも、前記高温に耐え得
る溶融炉の場合、炉自体に多額のコストがかかり、更に
前記特殊な冷却装置にも多大なコストを要する。このた
め前記特殊な溶融炉を用いる方法は、コスト的に簡易な
方法とは言い難い。またこのような高温における処理に
おいても、残渣のスラグは、最終処分場に運搬して埋め
立てる必要があり、廃棄物の運搬が、焼却施設への運搬
と、焼却後の最終処分場への運搬と最低2度の運搬作業
が軽減されるものではない。However, such a method using a special melting furnace requires a melting furnace capable of withstanding high temperatures, a special cooling and crushing device for recovering slag and the like, and in some cases, a facility for separating molten metal. Yes, it requires vast land for the construction of incineration facilities. Moreover, in the case of the melting furnace capable of withstanding the high temperature, the furnace itself requires a large amount of cost, and the special cooling device also requires a great cost. Therefore, the method using the special melting furnace cannot be said to be a simple method in terms of cost. Even in such high temperature treatment, the residual slag needs to be transported to the final disposal site and landfilled, and the transportation of waste involves transportation to the incineration facility and transportation to the final disposal site after incineration. It does not reduce the work of transporting at least twice.
【0006】[0006]
【発明が解決しようとする課題】従って本発明の目的
は、廃棄物を焼却処理した焼却灰を、処分場所で高価な
溶融炉や冷却装置等を構築することなく、容易に焼却灰
を減容化して処分することができる焼却灰の処理方法を
提供することにある。SUMMARY OF THE INVENTION Therefore, the object of the present invention is to easily reduce the volume of incinerated ash obtained by incinerating waste without constructing an expensive melting furnace or cooling device at the disposal site. It is intended to provide a method for treating incinerated ash that can be turned into waste.
【0007】[0007]
【課題を解決するための手段】本発明によれば、廃棄物
を焼却して生じた焼却灰を、焼却炉を構築せずに加熱溶
融し、冷却して固化スラグとして処分する方法であっ
て、焼却灰を直接溶融しながら実質的に連続に処分場所
に供給し、冷却により固化させることを特徴とする焼却
灰の処分方法(以下、第1の方法という)が提供され
る。また本発明によれば、廃棄物を焼却して生じた焼却
灰を、焼却炉を構築せずに加熱溶融し、冷却して固化ス
ラグとして処分する方法であって、処分する焼却灰を、
予め処分場所に堆積させた後、加熱溶融し、続いて冷却
により固化させることを特徴とする焼却灰の処分方法
(以下、第2の方法という)が提供される。According to the present invention, there is provided a method of incinerating ashes produced by incinerating waste by heating and melting without constructing an incinerator, cooling and disposing as solidified slag. Provided is a method for disposing of incinerated ash (hereinafter, referred to as a first method), which is characterized in that the incinerated ash is directly melted and supplied substantially continuously to a disposal site and solidified by cooling. Further, according to the present invention, incineration ash produced by incinerating waste is a method of heating and melting without constructing an incinerator, cooling and disposing as solidified slag, incineration ash to be disposed,
Provided is a method for disposing of incinerated ash (hereinafter referred to as a second method), which comprises depositing the material at a disposal site in advance, heating and melting, and subsequently solidifying by cooling.
【0008】本発明の方法において、廃棄物を焼却して
生じた焼却灰とは、通常一般廃棄物等を焼却施設におい
て焼却した後の残渣であって、最終処理場に通常埋め立
てられているものであれば特に限定されない。In the method of the present invention, incineration ash produced by incinerating waste is a residue after incineration of general waste in an incinerator, which is normally landfilled in the final disposal site. It is not particularly limited as long as it is.
【0009】本発明の方法において、焼却灰を処理する
処分場所は、通常の最終処分場に設けた穴のみに限定さ
れるものではなく、地上、谷、ケーソン基礎内等いずれ
であっても良い。特に穴の場合には周囲に連続壁を構築
する方法を採用すれば、あらゆる規模の穴とすることも
できる。In the method of the present invention, the disposal place for treating the incinerated ash is not limited to the hole provided in the usual final disposal site, and may be on the ground, in the valley, inside the caisson foundation, or the like. . Especially in the case of holes, holes of any size can be obtained by adopting a method of constructing a continuous wall around the holes.
【0010】本発明の方法において、焼却灰の加熱溶融
は、焼却灰が溶融する温度、好ましくは1300℃以上
に加熱可能な方法であれば特に限定されず、バーナー加
熱;アーク放電加熱、プラズマトーチ加熱等の電気的加
熱のいずれも採用することができる。この際本発明の方
法においては、焼却炉等を構築せずに加熱溶融を行なう
ため、焼却灰を直接溶融する必要がある。この直接溶融
とは、例えばバーナー加熱の場合、焼却灰をバーナー部
に直接導くようにすれば良く、またアーク放電加熱の場
合には、アーク放電させる領域を形成し、この領域を通
過させて溶融する方法、電極を離隔して焼却灰中に設置
し通電により溶融する方法等により行なうことができ
る。In the method of the present invention, the heating and melting of the incineration ash is not particularly limited as long as it can be heated to a temperature at which the incineration ash is melted, preferably 1300 ° C. or higher. Burner heating; arc discharge heating, plasma torch Any of electric heating such as heating can be adopted. At this time, in the method of the present invention, since heat melting is performed without constructing an incinerator or the like, it is necessary to directly melt the incineration ash. This direct melting means, for example, in the case of burner heating, the incineration ash may be directly guided to the burner portion, and in the case of arc discharge heating, a region for arc discharge is formed and melted by passing through this region. And a method in which the electrodes are separated from each other and placed in the incineration ash to be melted by applying an electric current.
【0011】本発明の第1の方法では、焼却灰を直接溶
融しながら実質的に連続に処分場所に供給するが、この
方法としては、例えば瞬時に溶融し得る量の焼却灰を、
処分場所に実質的に連続に落下させ、処分場所に落下す
る前に、前記加熱溶融法により直接溶融させる方法(電
極を用いる方法を除く)等により行なうことができる。
この際落下する焼却灰を加熱溶融する位置は、加熱溶融
された溶融物が処分場所に到達する前に空気冷却によっ
て固化しない位置であれば特に限定されず、加熱溶融方
法、焼却灰の供給量、気温等に応じて適宜選択すること
ができるが、好ましくは処分場所に落下する直前の位置
が望ましい。またこの加熱溶融は、溶融炉等を設けずに
行なうため、好ましくは風等の空気の流れ、雨等を遮断
する簡易な遮蔽手段を設けるのが望ましい。この遮蔽手
段としては、焼却灰が瞬時に高温にさらされるのみで溶
融し、それ以外は高温にさらされることがないため、耐
火シート等の簡易のもので十分である。更にこのような
焼却灰の溶融と処分場所への供給は、実質的に連続に行
なう必要がある。実質的に連続とは、例えば処理場所の
容量に応じて、一度の作業で処理場所への供給が満たさ
れる程度の容積の場合、連続的に行なえうるが、処理場
所の容量が大きく、処理すべき焼却灰を何回にも分けて
処理する必要がある場合には途中で中断して、また再開
する場合も包含する意味である。このように実質的に連
続に行なうことにより、溶融時の熱効率を良好に保持す
ることができ、作業が煩雑化する恐れもない。In the first method of the present invention, the incineration ash is directly melted and supplied substantially continuously to the disposal site. In this method, for example, an amount of incineration ash that can be instantly melted is used.
It can be carried out by a method of dropping it substantially continuously to the disposal site, and directly melting it by the heating and melting method (excluding the method using an electrode) before dropping it to the disposal site.
The position at which the incinerated ash that falls at this time is heated and melted is not particularly limited as long as the heated and melted melt does not solidify by air cooling before reaching the disposal site. Although it can be appropriately selected depending on the temperature, etc., the position immediately before dropping to the disposal site is preferable. Further, since this heating and melting is carried out without providing a melting furnace or the like, it is preferable to provide a simple shielding means for blocking the flow of air such as wind and rain. As the shielding means, a simple refractory sheet or the like is sufficient because the incinerated ash is instantly exposed to a high temperature only to be melted and is not exposed to a high temperature otherwise. Furthermore, such incineration ash must be melted and supplied to the disposal site substantially continuously. Substantially continuous means, for example, that the volume is such that the supply to the processing place is satisfied in one operation depending on the capacity of the processing place, it can be performed continuously, but the capacity of the processing place is large and the processing is performed. When it is necessary to treat the incinerated ash in multiple steps, it is meant to include the case of being interrupted and restarted. By carrying out substantially continuously as described above, the thermal efficiency at the time of melting can be favorably maintained, and there is no fear that the work will be complicated.
【0012】前記処分場所に落下した焼却灰の加熱溶融
物は、自然冷却されるか、また処理場所に水、泥水等が
存在する場合には水冷され、固化スラグとして処分場所
に堆積する。この際例えばケーソン基礎の内部に水を充
填しておき、このケーソン内部に前記加熱溶融物を供給
しながら充填された水を順次置換することにより生成す
る固化スラグをケーソン基礎の内部構造とすることがで
きる。The heated melt of the incineration ash that has fallen to the disposal site is naturally cooled or, if water, muddy water, etc. are present at the processing site, cooled and deposited as solidified slag at the disposal site. At this time, for example, the inside of the caisson foundation is filled with water, and the solidified slag generated by sequentially replacing the filled water while supplying the heating melt inside the caisson has an internal structure of the caisson foundation. You can
【0013】一方本発明の第2の方法では、まず処分す
る焼却灰を予め処分場所に堆積させる。この際堆積させ
る量は、本発明の技術的・経済的効率を損なうほど少量
でなければ特に限定されない。On the other hand, in the second method of the present invention, first, the incineration ash to be disposed is deposited in advance at the disposal site. At this time, the amount to be deposited is not particularly limited as long as it is so small as to impair the technical and economic efficiency of the present invention.
【0014】次に堆積された焼却灰を加熱溶融するに
は、前記バーナー加熱又は電気的加熱等により行なうこ
とができるが、電気抵抗線通電加熱、溶融灰通電加熱等
の電気的加熱が容易で好ましい。具体的には例えば、少
なくとも一組の電極を互いに隔置して、前記堆積させた
焼却灰中に挿入し、通電により溶融する方法、予め処理
場所の底部に平面状の電極を載置し、その上に前記焼却
灰の堆積を行ない、堆積された焼却灰の上部表面に、網
板状等の適当な形状の電極を設置して溶融する方法等に
より行なうことができる。The deposited incineration ash can be heated and melted by the above-mentioned burner heating or electric heating, but electric heating such as electric resistance wire energization heating and molten ash energization heating is easy. preferable. Specifically, for example, at least one set of electrodes are separated from each other, inserted into the deposited incinerated ash, a method of melting by energization, a flat electrode is placed on the bottom of the treatment place in advance, The incineration ash may be deposited thereon, and an electrode having an appropriate shape such as a mesh plate may be placed on the upper surface of the deposited incinerator ash to melt the ash.
【0015】このような加熱溶融操作を一回で修了させ
ても良いし、また処理する焼却灰の量が多い場合には、
堆積させた焼却灰の特定区域を加熱溶融させた後、隣接
する区域から順次加熱溶融して最終的に堆積させた焼却
灰の全てを加熱溶融させることができる。また加熱溶融
処理した焼却灰の上に、更に追加の焼却灰を前記第1の
方法と同様に加熱溶融しながら供給することもでき、あ
るいは追加の焼却灰を堆積させた後、前述と同様に堆積
された焼却灰を加熱溶融する操作を繰り返しても良い。
これら追加の焼却灰を処理する場合には、最初又は前回
に加熱溶融させた溶融灰が既に完全冷却された後に実施
することもできるが、熱効率等を勘案して、最初又は前
回の溶融灰が完全に冷却しない状態の時に次の追加の焼
却灰を加熱溶融させるのが好ましい。The above heating and melting operation may be completed once, or when the amount of incinerated ash to be treated is large,
After heating and melting a specific area of the deposited incineration ash, it is possible to sequentially heat and melt from adjacent areas to heat and melt all of the finally deposited incineration ash. Further, on the incineration ash that has been subjected to the heat melting treatment, additional incineration ash can be supplied while heating and melting in the same manner as in the first method, or after depositing the additional incineration ash, as described above. The operation of heating and melting the accumulated incineration ash may be repeated.
When treating these additional incinerated ash, it may be carried out first or after the molten ash that has been heated and melted in the previous time is already completely cooled, but considering the thermal efficiency etc., the first or previous molten ash is It is preferable to heat and melt the following additional incinerated ash when it is not completely cooled.
【0016】前記加熱溶融に続く冷却は、自然冷却で十
分であり、この冷却によって所望の減容化した固化スラ
グが処分場所に堆積する。Natural cooling is sufficient as the cooling following the heating and melting, and the desired volume-reduced solidified slag is deposited at the disposal site.
【0017】本発明の焼却灰の処分方法では、処分場所
において焼却灰を固化スラグに減容化して処理するが、
得られた固化スラグは、そのまま地盤改良として作用す
る他、掘り出して、通常のスラグ材として利用すること
ができる。また処分場所を前述のケーソン基礎内部とす
ることによって、ケーソン基礎とすることもできる。In the method for disposing of incinerated ash of the present invention, the volume of incinerated ash is reduced to solidified slag for disposal at the disposal site.
The solidified slag thus obtained not only acts as a ground improvement, but can also be dug out and used as a normal slag material. Also, by disposing the disposal place inside the above-mentioned caisson foundation, the caisson foundation can also be used.
【0018】[0018]
【実施例】以下図面を参照して、本発明の実施例を説明
するが、本発明はこれらに限定されるものではない。Embodiments of the present invention will be described below with reference to the drawings, but the present invention is not limited thereto.
【0019】図1は、本発明の第1の方法の一実施態様
を示す概略図であって、10は焼却灰を加熱溶融するた
めの溶融システムである。溶融システム10は、処理す
べき多孔質の焼却灰12が充填されたホッパー部11
と、このホッパー部11下部に備えられた焼却灰12の
降下量を制御する制御装置13と、ホッパー部11の下
端部開口から降下してくる焼却灰12を瞬時に加熱溶融
するバーナー加熱装置14とで実質的に構成しており、
焼却灰12を溶融するための溶融炉は備えていない。FIG. 1 is a schematic view showing one embodiment of the first method of the present invention, and 10 is a melting system for heating and melting the incineration ash. The melting system 10 comprises a hopper section 11 filled with porous incineration ash 12 to be treated.
A control device 13 for controlling the amount of fall of the incineration ash 12 provided in the lower part of the hopper portion 11, and a burner heating device 14 for instantly heating and melting the incineration ash 12 falling from the lower end opening of the hopper portion 11. And consists essentially of
No melting furnace for melting the incineration ash 12 is provided.
【0020】ホッパー部11内に充填している焼却灰1
2は、都市ゴミ等を焼却炉にて焼却した際に生じたもの
であって、必要に応じてホッパー部11内に順次追加で
きるようになっている。制御装置13では、バーナー加
熱装置14での焼却灰12の溶融状態を探知し、焼却灰
12の降下量を自動的にコントロールしうるしぼり機構
付きの開閉口(図示せず)が備えられている。バーナー
加熱装置14は、同一円周上に位置するように配置した
6本のバーナーを備えており、降下してくる焼却灰12
の特定雰囲気を1300℃以上に加熱しうるよう設置し
ている。Incinerated ash 1 filled in the hopper section 11
2 is generated when incinerating municipal waste or the like in an incinerator, and can be sequentially added to the hopper unit 11 as needed. The control device 13 is provided with an opening / closing port (not shown) having a squeezing mechanism capable of detecting the molten state of the incineration ash 12 in the burner heating device 14 and automatically controlling the amount of fall of the incineration ash 12. . The burner heating device 14 is equipped with six burners arranged so as to be located on the same circumference, and the incinerated ash 12 falling
The specific atmosphere of 1 is installed so that it can be heated to 1300 ° C. or higher.
【0021】この溶融システム10は、廃棄物処分場所
に予め設けられた焼却灰処分穴15の上方であって、バ
ーナー加熱装置14が略地面の高さになるように設置し
ている。溶融システム10は溶融炉を備えていないの
で、このシステムの加熱溶融に係る区域を風等から遮る
ために、焼却灰処分穴15を囲む地表面には、耐熱製の
簡易な遮蔽枠17を配置している。The melting system 10 is installed above the incineration ash disposal hole 15 provided in advance at the waste disposal site, and the burner heating device 14 is installed at approximately the height of the ground. Since the melting system 10 does not have a melting furnace, a heat-resistant simple shielding frame 17 is arranged on the ground surface surrounding the incineration ash disposal hole 15 in order to shield the area related to heating and melting of this system from wind and the like. are doing.
【0022】次に、このシステムを使用する場合の本発
明の第1の方法による処分方法を説明する。ホッパー部
11に充填された処分すべき焼却灰12は、制御装置1
3により降下量をコントロールされながら、ホッパー部
11の下端部開口より連続的に降下する。この焼却灰1
2は降下する途中に設けられたバーナー加熱装置14を
通過することに、1300℃以上の雰囲気下にさらされ
て瞬時に加熱溶融する。溶融状態の焼却灰12は、その
まま焼却灰処分穴15内に降下していき、そこで自然冷
却されることによりスラグ16として堆積する。この際
スラグ16の溶融灰が連続的に降下してくる表面部は、
溶融状態が実質的に保持されるので、降下してくる溶融
灰は、順次焼却灰処分穴15内全領域に拡がって堆積さ
れる。このような加熱溶融・冷却処理により、焼却灰1
2の容積を約半分程度にして焼却灰処分穴15内に堆積
させることができる。Next, a disposal method according to the first method of the present invention when using this system will be described. The incineration ash 12 to be disposed of which is filled in the hopper section 11 is the control device 1
While descending amount is controlled by 3, it descends continuously from the lower end opening of the hopper 11. This incineration ash 1
2 passes through a burner heating device 14 provided on the way of descending, and is exposed to an atmosphere of 1300 ° C. or more and is heated and melted instantly. The incinerated ash 12 in a molten state descends into the incinerated ash disposal hole 15 as it is, and is naturally cooled therein to be deposited as a slag 16. At this time, the surface part where the molten ash of the slag 16 continuously falls is
Since the molten state is substantially maintained, the descending molten ash is sequentially spread and accumulated in the entire area of the incineration ash disposal hole 15. Incinerator ash 1 by such heating and melting / cooling treatment
The volume of 2 can be reduced to about half and deposited in the incineration ash disposal hole 15.
【0023】図2は、本発明の第2の方法の一実施態様
を示す概略図であって、予め堆積させた焼却灰を加熱溶
融している状態を示す。20は焼却灰を処分する最終処
分場所に設けた穴であって、穴20内には、予め多孔質
の焼却灰23を堆積させて置く。次に一対の高圧用電極
装置21の少なくとも電極部22の先端部が、堆積させ
た焼却灰23の下部に到達するように挿入埋設する。こ
の高圧用電極装置21は、電極部22に高電流を印加し
得るようになっており、電極部22は、伸縮自在となる
機構(図示せず)が備えられている。FIG. 2 is a schematic view showing an embodiment of the second method of the present invention, and shows a state in which incineration ash deposited in advance is heated and melted. Reference numeral 20 denotes a hole provided at a final disposal place for disposing of the incineration ash, and a porous incineration ash 23 is previously deposited and placed in the hole 20. Next, at least the tips of the electrode portions 22 of the pair of high-voltage electrode devices 21 are inserted and embedded so as to reach the lower portion of the deposited incineration ash 23. The high voltage electrode device 21 is configured to be able to apply a high current to the electrode portion 22, and the electrode portion 22 is provided with a mechanism (not shown) capable of expanding and contracting.
【0024】次に、焼却灰23内に挿入埋設された電極
部22に電流を印加し、焼却灰23を下方部から加熱溶
融する。この加熱溶融を行っている際に、経時的に高圧
用電極装置21の電極部22を徐々に短縮していき、即
ち電極部22が焼却灰23内を上方に移動するようにし
て順次上方に位置する焼却灰23を加熱溶融していく。
下方に位置する溶融された焼却灰23は、減容しながら
自然冷却により固化する。この際、ある程度電極部22
を短縮した段階で、焼却灰23上に新たな焼却灰24を
堆積させていき、電極部22を地表付近まで短縮させな
がら、全ての焼却灰を加熱溶融することができる。この
ような加熱溶融・冷却処理により、焼却灰(23,2
4)の容積を約半分程度にして焼却灰処分穴20内に堆
積させることができる。Next, an electric current is applied to the electrode portion 22 inserted and buried in the incineration ash 23 to heat and melt the incineration ash 23 from the lower portion. During this heating and melting, the electrode part 22 of the high-voltage electrode device 21 is gradually shortened over time, that is, the electrode part 22 is moved upward in the incineration ash 23 and is sequentially moved upward. The incineration ash 23 located is heated and melted.
The molten incineration ash 23 located below is solidified by natural cooling while reducing the volume. At this time, the electrode portion 22
At the stage of shortening, the new incinerated ash 24 is deposited on the incinerated ash 23, and all the incinerated ash can be heated and melted while shortening the electrode portion 22 to the vicinity of the ground surface. By such heating and melting / cooling treatment, incineration ash (23, 2
The volume of 4) can be reduced to about half and deposited in the incineration ash disposal hole 20.
【0025】[0025]
【発明の効果】本発明の焼却灰の処分方法は、通常廃棄
物最終処分場所においてそのまま埋設される、焼却炉に
て減容化された焼却灰を対象とするので、更なる減容化
が期待できる。また溶融炉を構築せずに処分場所で加熱
溶融・冷却するので、溶融のための処分場所とは別の土
地を必要とせず、特に冷却装置等も必要としないので、
コスト的に有利であり、しかも容易に焼却灰を減容化で
き、処分場所の確保も同量処理するのに略半減させるこ
とができる。EFFECTS OF THE INVENTION Since the incineration ash disposal method of the present invention is intended for the incineration ash that is normally buried at the final waste disposal site and has been volume-reduced in the incinerator, further volume reduction is possible. Can be expected. In addition, since heating and melting / cooling is performed at the disposal site without constructing a melting furnace, there is no need for a land separate from the disposal site for melting, and no particular cooling device is required.
It is advantageous in terms of cost, and the volume of incinerated ash can be easily reduced, and the securing of a disposal site can be reduced to about half when processing the same amount.
【図1】本発明の第1の方法の一実施例を説明するため
の溶融システムと焼却灰処分場所との関係を示す概略図
である。FIG. 1 is a schematic diagram showing a relationship between a melting system and an incineration ash disposal site for explaining an embodiment of a first method of the present invention.
【図2】本発明の第2の方法の一実施例を説明するため
の高圧用電極装置を堆積させた焼却灰中に挿入・埋設さ
せた状態を示す状態概略図である。FIG. 2 is a schematic state view showing a state in which a high-voltage electrode device is inserted / embedded in the incinerated ash in which the high-voltage electrode device is deposited, for explaining one embodiment of the second method of the present invention.
12,22,23:焼却灰 14:バーナー加熱装置 15,20:焼却灰処分穴 16:スラグ 21:高圧用電極装置 12, 22, 23: Incinerated ash 14: Burner heating device 15, 20: Incinerator ash disposal hole 16: Slag 21: High-voltage electrode device
Claims (3)
炉を構築せずに加熱溶融し、冷却して固化スラグとして
処分する方法であって、焼却灰を直接溶融しながら実質
的に連続に処分場所に供給し、冷却により固化させるこ
とを特徴とする焼却灰の処分方法。1. A method of heating and melting incinerated ash produced by incinerating waste without constructing an incinerator, and then cooling and disposing as solidified slag. A method for disposing of incinerated ash, which comprises continuously supplying to the disposal site and solidifying by cooling.
炉を構築せずに加熱溶融し、冷却して固化スラグとして
処分する方法であって、処分する焼却灰を、予め処分場
所に堆積させた後、加熱溶融し、続いて冷却により固化
させることを特徴とする焼却灰の処分方法。2. A method for incinerating ash produced by incinerating wastes by heating and melting without constructing an incinerator, cooling and disposing as solidified slag, in which the incinerated ash to be disposed is disposed in advance. A method for disposing of incinerated ash, characterized in that after being deposited on, it is heated and melted and then solidified by cooling.
加熱又はこれらの組合せにより行なうことを特徴とする
請求項1又は2記載の焼却灰の処分方法。3. The method for disposing of incineration ash according to claim 1, wherein the heating and melting are performed by burner heating, electric heating or a combination thereof.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP15004195A JPH094828A (en) | 1995-06-16 | 1995-06-16 | Disposal method of incineration ash |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP15004195A JPH094828A (en) | 1995-06-16 | 1995-06-16 | Disposal method of incineration ash |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| JPH094828A true JPH094828A (en) | 1997-01-10 |
Family
ID=15488216
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP15004195A Pending JPH094828A (en) | 1995-06-16 | 1995-06-16 | Disposal method of incineration ash |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPH094828A (en) |
-
1995
- 1995-06-16 JP JP15004195A patent/JPH094828A/en active Pending
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