JP2002317911A - Melting processing apparatus for waste such as incinerated ash - Google Patents

Melting processing apparatus for waste such as incinerated ash

Info

Publication number
JP2002317911A
JP2002317911A JP2001123450A JP2001123450A JP2002317911A JP 2002317911 A JP2002317911 A JP 2002317911A JP 2001123450 A JP2001123450 A JP 2001123450A JP 2001123450 A JP2001123450 A JP 2001123450A JP 2002317911 A JP2002317911 A JP 2002317911A
Authority
JP
Japan
Prior art keywords
melting
refractory
waste
piece bed
chamber
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
Application number
JP2001123450A
Other languages
Japanese (ja)
Inventor
Yasuo Kaneko
康男 兼子
Nobuo Kawakami
信雄 川上
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.)
Chiyoda Enji Kk
Original Assignee
Chiyoda Enji Kk
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 Chiyoda Enji Kk filed Critical Chiyoda Enji Kk
Priority to JP2001123450A priority Critical patent/JP2002317911A/en
Publication of JP2002317911A publication Critical patent/JP2002317911A/en
Pending legal-status Critical Current

Links

Classifications

    • YGENERAL 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
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W30/00Technologies for solid waste management
    • Y02W30/50Reuse, recycling or recovery technologies
    • Y02W30/62Plastics recycling; Rubber recycling

Landscapes

  • Separation, Recovery Or Treatment Of Waste Materials Containing Plastics (AREA)
  • Gasification And Melting Of Waste (AREA)
  • Processing Of Solid Wastes (AREA)

Abstract

PROBLEM TO BE SOLVED: To make harmless waste of refractory brick involving harmful metal such as sexivalent chrome by making use of an environment of a refractory piece bed of a molten slag, and improve the economy as the refractory piece bed. SOLUTION: A melting processing apparatus comprises a melting furnace comprising a combustion chamber or a gas decomposition chamber disposed on a bottom, a grate for heating and melting slag and a refractory piece bed disposed thereon and a deposition layer of incinerated ash disposed further thereon. A refractory brick containing harmful metal discarded as waste is used for the refractory piece bed.

Description

【発明の詳細な説明】DETAILED DESCRIPTION OF THE INVENTION

【0001】[0001]

【発明の属する技術分野】本発明は、焼却灰等の廃棄物
を溶融処理する為の装置に関し、更に詳細には、六価ク
ロム等の有害金属を含む耐火レンガの廃棄物を活用しつ
つ無害化処理できる処理装置に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to an apparatus for melting and processing waste such as incineration ash, and more particularly, to harmless refractory bricks containing toxic metals such as hexavalent chromium. The present invention relates to a processing device capable of performing a chemical treatment.

【0002】[0002]

【従来の技術】溶融スラグの溶融炉の炉壁等を構成する
レンガ等の耐火物(以下単に耐火レンガと呼ぶ)等に
は、六価クロムを含むものが用いられている。その理由
は、耐火レンガと溶融スラグが触れると、該溶融スラグ
と耐火レンガとの間には僅かではあるが反応が惹起さ
れ、その反応が永続すると無視できないレンガの損傷と
なるが、六価クロムを混入させると、六価クロムの強い
酸化作用等でこの反応を可及的に抑制することができる
からである。ところが、この耐火レンガも使用を継続さ
せて半年程度を経過すると、耐用期間を過ぎて廃棄処分
される運命にあり、これが一旦廃材となると、六価クロ
ムを含む有害なものとなる。そこで、従来は、この六価
クロムを含む耐火レンガの廃材は、六価クロムが溶出し
ないよう無害化処理が施されているが、この無害化処理
は複雑であると同時に経済的に極めて高価なものとなら
ざるを得ない。
2. Description of the Related Art As a refractory such as a brick constituting a furnace wall of a melting furnace for molten slag (hereinafter simply referred to as a refractory brick), a material containing hexavalent chromium is used. The reason is that when the refractory brick and the molten slag come into contact with each other, a slight reaction occurs between the molten slag and the refractory brick. This reaction can be suppressed as much as possible by the strong oxidizing action of hexavalent chromium and the like. However, this refractory brick is also destined to be disposed of after its useful life after about six months of continued use, and once it becomes waste material, it becomes harmful including hexavalent chromium. Therefore, conventionally, the waste material of the refractory brick containing hexavalent chromium has been subjected to detoxification treatment so that hexavalent chromium does not elute, but this detoxification treatment is complicated and extremely expensive economically. It has to be something.

【0003】ところで、本発明者は、先に「焼却灰等廃
棄物の溶融処理装置」(特願平11−377258)を
提案しており、その概要は、「コークスの使用量を可及
的に最少のものとし、廃棄プラスチックを熱源として最
大100%にまで利用可能な処理装置」に関するもので
あり、そこでは、スラグを溶融すべき耐火物片には耐火
性に優れたセラミックス素材が用いられている。そこ
で、この耐火物片として上記六価クロム等の有害金属を
含む廃棄耐火レンガを活用することで、該六価クロム等
の有害金属を可及的に無害化処理しようと着眼したのが
本発明の狙いである。
The present inventor has previously proposed a "melting apparatus for waste such as incinerated ash" (Japanese Patent Application No. 11-377258). To a maximum of 100% using waste plastic as a heat source, in which refractory pieces to be used for melting slag are made of ceramic materials with excellent fire resistance. ing. Therefore, the present invention is based on the idea that the harmful metal such as hexavalent chromium is treated as much as possible by making use of the waste refractory brick containing the harmful metal such as hexavalent chromium as the refractory piece. The aim is.

【0004】[0004]

【発明が解決しようとする課題】本発明は上記実情を解
消しようとしてなされたもので、溶融スラグの耐火物片
ベッドの環境を利用して六価クロム等の有害金属を含む
耐火レンガの廃棄物を無害化処理し、且つ、耐火物片ベ
ッドとしての経済性も向上させようとするものである。
SUMMARY OF THE INVENTION The present invention has been made in order to solve the above-mentioned circumstances, and utilizes the environment of a refractory piece bed of molten slag to recycle refractory brick waste containing harmful metals such as hexavalent chromium. Is made harmless, and the economy as a refractory piece bed is also improved.

【0005】[0005]

【課題を解決するための手段】請求項1に記載の焼却灰
等廃棄物の溶融処理装置は、底部に燃焼室又はガス分解
室を配し、その上にスラグを熱溶融させるロストル及び
耐火物片ベッドを配し、その上に焼却灰の堆積層を配し
た溶融炉において、該耐火物片ベッドに廃棄処分された
有害金属を含む耐火レンガを用いたことを特徴として構
成される。
According to a first aspect of the present invention, there is provided an apparatus for melting waste such as incinerated ash, wherein a combustion chamber or a gas decomposition chamber is provided at a bottom portion, and a stork and a refractory for thermally melting slag thereon. In a melting furnace in which a single bed is provided and a deposited layer of incineration ash is provided thereon, the refractory single bed is formed by using refractory bricks containing toxic metals discarded in the refractory single bed.

【0006】請求項2記載の溶融処理装置は、該溶融炉
の下部に搬送空気を導入すると共に溶融後のスラグを一
時的に滞留させて廃棄プラスチックを熱分解する為の一
定空間を形成したガス分解室を配設し、該ガス分解室の
一部に廃棄プラスチックの細片を搬入する搬送空気の導
入口を臨ませ、 該ガス分解室の上部に耐火物片ベッド
及び溶融スラグの滴下を促すロストルを配すると共に分
解ガスとの燃焼を促す空気導入口を臨ませた燃焼溶融室
を形成した焼却灰等廃棄物溶融燃焼装置において、該耐
火物片ベッドに廃棄処分された有害金属を含む耐火レン
ガを用いたことを特徴として構成される。
In a second aspect of the present invention, there is provided a melting apparatus in which a carrier air is introduced into a lower portion of the melting furnace and a fixed space for thermally decomposing waste plastic is formed by temporarily retaining molten slag. A decomposition chamber is provided, and a part of the gas decomposition chamber faces the inlet of the carrier air for carrying the waste plastic pieces, and a refractory piece bed and molten slag are dripped at the upper part of the gas decomposition chamber. In a waste melting and burning apparatus such as an incineration ash formed with a combustion and melting chamber facing an air introduction port for disposing a roster and facilitating combustion with a decomposed gas, the refractory containing a hazardous metal discarded in the refractory piece bed It is characterized by using bricks.

【0007】請求項3記載の溶融処理装置は、焼却灰の
CaO/SiO 比を0.75以上として構成され
る。
A third aspect of the present invention is directed to a melting apparatus, wherein the incinerated ash has a CaO / SiO 2 ratio of 0.75 or more.

【0008】[0008]

【発明の実施の形態】本発明溶融処理装置は、焼却灰等
の廃棄物Sを溶融させる溶融炉部10と、これに廃棄プ
ラスチックを供給する廃棄プラスチック導入部30とか
ら成る。
DETAILED DESCRIPTION OF THE PREFERRED EMBODIMENTS The melting apparatus according to the present invention comprises a melting furnace section 10 for melting waste S such as incineration ash and a waste plastic introducing section 30 for supplying waste plastic thereto.

【0009】該溶融炉部の溶融炉11には、シャフト型
溶融炉を用いることができ、該溶融炉の下部に後述の搬
送空気を迎え入れると共に溶融後のスラグGを一時的に
滞留させる為の一定空間を形成したガス分解室12を配
設する。該ガス分解室12の一部には、該搬送空気の導
入口13を配設し、他方には後述する初期の予備加熱を
司るバーナー14を配設し、下部に排出口15を配設す
る。尚、導入口13には、後述の二次空気の導入と同
様、熱交換機を経由した比較的高温の空気の導入管を併
用させても良く、又、必要に応じて該空気に酸素富化器
19を付設させても良い。
A shaft-type melting furnace can be used as the melting furnace 11 in the melting furnace section, and the lower part of the melting furnace is used to receive the below-described carrier air and temporarily retain the slag G after melting. A gas decomposition chamber 12 forming a certain space is provided. A part of the gas decomposition chamber 12 is provided with an inlet 13 for the carrier air, the other side is provided with a burner 14 for performing initial preheating described later, and a lower part is provided with an outlet 15. . The inlet 13 may be used together with a relatively high-temperature air inlet pipe via a heat exchanger, as in the case of the secondary air described below. If necessary, the air may be enriched with oxygen. A vessel 19 may be provided.

【00010】該ガス分解室12の上には、分解ガスの
上昇と溶融スラグの滴下を促すロストル16を配し、そ
の上には予備加熱の為の耐火物片ベッド40を配し、更
にその上に塊状の焼却灰Sを充填すべき燃焼溶融室17
を形成する。該燃焼溶融室17には、一部に高温燃焼を
促す為の二次空気導入口18を臨ませ、該二次空気導入
口18には、燃焼ガスとの熱交換機を経由した比較的高
温の空気を導入管から送気する。
On the gas decomposition chamber 12, there is disposed a roster 16 for promoting the rise of decomposition gas and dripping of molten slag. On top of that, a refractory piece bed 40 for preheating is disposed. The combustion melting chamber 17 to be filled with massive incineration ash S
To form Part of the combustion / melting chamber 17 faces a secondary air inlet 18 for promoting high-temperature combustion. The secondary air inlet 18 has a relatively high temperature through a heat exchanger with combustion gas. Air is supplied from the inlet pipe.

【00011】そして、本発明にあっては、当該耐火物
片ベッド40に、六価クロム等の有害金属を含む溶融炉
用耐火性の耐火レンガの廃棄物をベッドとしての適当形
状に、裁断又は砕いて用いる。上述した如く、耐火レン
ガには、耐食性を向上させる目的で、溶融スラグとの反
応を避ける目的で六価クロムが使用され、それが耐用期
間を過ぎると廃棄物として処分されるので、当該廃棄耐
火レンガを対象とする。そして、当該耐火レンガを適当
大きさに裁断又は砕いて耐火物片ベッド40とする。当
該耐火レンガは、溶融炉に使用されたもので、耐火性に
優れることは勿論であり、それをベッドとして使用すれ
ば、後述する予備加熱及びスラグの溶融段階で蓄熱性等
のベッドとしての機能性に優れたものとなる。そして、
当該ベッドに六価クロム等の有害金属を含む廃材を用い
る趣旨は、スラグの溶融段階でベッドを通過する際に起
こるクロムの拡散と、その後のスラグの冷却段階で導く
結晶化による六価クロム等の有害金属の無害化に狙いが
ある。ここで、有害金属とは、上記六価クロムの他、
鉛、カドミニウム、亜鉛等の有害金属のイオン又はその
化合物を指す。
In the present invention, the refractory piece bed 40 is formed by cutting or rejecting waste of refractory bricks for melting furnaces containing harmful metals such as hexavalent chromium into a suitable shape as a bed. Crush and use. As mentioned above, hexavalent chromium is used in refractory bricks for the purpose of avoiding reaction with molten slag for the purpose of improving corrosion resistance, and since it is disposed of as waste after its useful life, the waste refractory For bricks. Then, the refractory brick is cut or crushed into an appropriate size to form a refractory piece bed 40. The refractory brick is used in a melting furnace and, of course, has excellent fire resistance, and if it is used as a bed, it functions as a bed for heat storage and the like in the preheating and slag melting stages described below. It will be excellent in property. And
The purpose of using waste material containing harmful metals such as hexavalent chromium in the bed is that diffusion of chromium that occurs when the slag passes through the bed in the melting stage of slag, and hexavalent chromium and the like by crystallization guided in the subsequent cooling stage of slag The aim is to detoxify harmful metals. Here, the harmful metal means, in addition to the hexavalent chromium,
It refers to ions of harmful metals such as lead, cadmium and zinc or compounds thereof.

【0012】更に、溶融炉11の燃焼溶融室17の上に
は、燃焼前の塊状焼却灰を予熱させる為の予備加熱室2
0を形成し、その上の炉頭部には焼却灰の投入口21及
び燃焼後の排ガスを送り出す排気口22を形成する。
Further, a preheating chamber 2 for preheating bulk incineration ash before combustion is provided above the combustion melting chamber 17 of the melting furnace 11.
0 is formed, and an inlet 21 for incineration ash and an exhaust port 22 for sending out exhaust gas after combustion are formed in the furnace head above it.

【0013】そして、上記ガス分解室12の一部に臨む
搬送空気の導入口13には、搬送空気パイプ31を連結
し、且つ、その管路の一部に適当形状の細片に切断した
廃棄プラスチックを蓄えて搬送空気中に送り出すホッパ
ー32及び定量供給機33を配設する。該搬送空気パイ
プ31の先には、ブロワー34を配設し、該ブロワーは
炉内の圧力が高い場合には、高圧の加わる形態とする。
又、上記プラスチック細片には、粒状のものも含まれ
る。
A transport air pipe 31 is connected to an inlet 13 of the transport air facing a part of the gas decomposition chamber 12, and a part of the pipe is cut into small pieces having a suitable shape. A hopper 32 and a fixed-rate feeder 33 for storing plastic and sending it into the carrier air are provided. A blower 34 is provided at the end of the conveying air pipe 31. When the pressure in the furnace is high, the blower is configured to apply high pressure.
In addition, the above-mentioned plastic strips include granular ones.

【0014】尚、本発明の熱源としての廃棄プラスチッ
クの対象物には、燃焼によってダイオキシン等の有毒ガ
スを発生する塩素系プラスチック等は除外するが、それ
以外の適当大きさに裁断又は成形可能なもの、例えばタ
イヤ等全てのプラスチックを含む。又、該廃棄プラスチ
ックの中には、溶融温度を大幅に落とさない範囲で、も
み殻、木くず、古紙等を混焼させても良い。
The object of the waste plastic as the heat source of the present invention excludes chlorinated plastics and the like which generate toxic gas such as dioxin by combustion, but can be cut or molded into other suitable sizes. Including all plastics such as tires. In addition, rice husks, wood chips, waste paper, and the like may be mixed in the waste plastic as long as the melting temperature is not significantly reduced.

【0015】次に、本発明装置の作用を説明する。先
ず、溶融炉11内に、焼却灰を豆タン状に塊状化させた
もの、又は、該焼却灰をセメントと混練させて塊状化さ
せたものを、投入口21から投入機等を用いて投下す
る。但し、該焼却灰は、塊状化させたものばかりでな
く、紛状のまま投入しても良い。
Next, the operation of the device of the present invention will be described. First, incinerator ash obtained by agglomerating the incinerated ash into a bean tongue or kneading the incinerated ash with cement into an agglomerate is dropped into the melting furnace 11 from the input port 21 using a charging machine or the like. I do. However, the incinerated ash is not limited to agglomerated one, and may be supplied as a powder.

【0016】 ここで、本発明にあっては、当該焼却灰
の成分は、CaO/SiO 比が0.75以上に調整
するが、これは、後述するスラグの冷却段階にあって、
可及的に結晶質を多く生成させる為である。即ち、本発
明にあっては、六価クロム等の有害金属を無害化させる
にあたって、スラグの溶融後に結晶質に導き混入した有
害金属を無害化させようとするが、そのスラグの結晶化
を促すには、焼却灰の成分比が重要であって、CaO/
SiO 比が0.7以下ではアモルファス状態とな
り、0.75以上でより多くの結晶化が促されるからで
ある。そこで、焼却灰の成分は大略CaO 15〜16
%、SiO 35〜36%、Al 17〜18%
から成るが、このCaO/SiO 比の調整のため、
投入する焼却灰のCaO/SiO 比を測定し、投入
する焼却灰が0.75以上であればそのまま用い、もし
この条件を満たさない場合には、CaO又はSiO
成分を補充して調整する。
Here, in the present invention, the component of the incinerated ash is adjusted to have a CaO / SiO 2 ratio of 0.75 or more.
This is in order to generate as many crystals as possible. That is, in the present invention, when detoxifying a harmful metal such as hexavalent chromium, the slag is melted, and the harmful metal introduced into the crystalline material is detoxified, but crystallization of the slag is promoted. In addition, the component ratio of incinerated ash is important, and CaO /
If the SiO 2 ratio is 0.7 or less, the amorphous state is obtained, and if the SiO 2 ratio is 0.75 or more, more crystallization is promoted. Therefore, the components of the incinerated ash are generally CaO 15-16.
%, SiO 2 35~36%, Al 2 O 3 17~18%
However, in order to adjust the CaO / SiO 2 ratio,
The CaO / SiO 2 ratio of the incinerated ash to be charged is measured. If the incinerated ash to be charged is 0.75 or more, the incinerated ash is used as it is. If this condition is not satisfied, CaO or SiO 2
Adjust by adding ingredients.

【0017】そして、予備加熱に移り、バーナー14に
点火して、炉内の温度を上昇させ、耐火物片ベッド40
等に蓄熱させて、炉内を1500〜1800℃程度の高
温に導く。すると、上述の如く、CaO、SiO、A
等を主成分とする焼却灰は溶融点に達し、その
溶融スラグの一部がロストル16を経て、ガス分解室1
2の底部に滴下される。
Then, the process proceeds to preheating, and the burner 14 is ignited to raise the temperature in the furnace.
The furnace is heated to a high temperature of about 1500 to 1800 ° C. Then, as described above, CaO, SiO 2 , A
The incinerated ash mainly composed of l 2 O 3 or the like reaches the melting point, and a part of the molten slag passes through the roastle 16 and passes through the gas decomposition chamber 1.
2 is dropped on the bottom.

【0018】その時点で、バーナー14の燃焼を停止さ
せる。そして一方、空気を送る為のブロワー34の運転
を開始し、その途中でホッパー32から適当形状の細片
に裁断した廃棄プラスチックを搬送空気中に定量供給機
33を経て送り出し、この廃棄プラスチックを搬送空気
と共に導入口13を経てガス分解室12内に送り込む。
At that time, the combustion of the burner 14 is stopped. On the other hand, the operation of the blower 34 for sending air is started, and on the way, the waste plastic cut into small pieces of an appropriate shape is sent out from the hopper 32 into the transport air through the quantitative feeder 33, and the waste plastic is transported. It is sent into the gas decomposition chamber 12 through the inlet 13 together with air.

【0019】すると、該ガス分解室12内は、上記溶融
スラグがその底部に滞留しているので、室内が1500
〜1800℃の高温に保たれた状態となり、そしてそこ
に搬送空気によって廃棄プラスチックの細片が運び込ま
れると、該プラッスチック細片は、一部が燃焼するもの
のその殆どは熱分解して可燃ガスに変成する。即ち、ガ
ス分解室内は滞留する溶融スラグからの熱放射、対流等
の熱エネルギーの供給を受けて、室内が常に溶融温度と
ほぼ等しい温度に保たれることとなり、かかる高温下で
は、ポリエチレン、ポリスチレン等の廃棄プラスチック
は、分子間結合が解かれて一気に熱分解し、可燃ガスに
変化する。尚、前述した通り、斯かる高温下では、導入
された搬送空気と可燃物としてのプラスチックが存在す
れば当然に燃焼するが、それは一部であり、且つ、その
燃焼は後述するスラグの溶融を妨げない。
Then, in the gas decomposition chamber 12, since the molten slag stays at the bottom of the gas decomposition chamber 12,
When it is kept at a high temperature of 11800 ° C. and the waste plastic strip is carried by the carrier air, the plastic strip is partially burned, but most of it is thermally decomposed to a flammable gas. Metamorphose. That is, the gas decomposition chamber receives heat radiation from the molten slag staying therein, heat energy such as convection and the like, and the chamber is always kept at a temperature substantially equal to the melting temperature. Waste plastics such as are broken down at a stretch by intermolecular bonds and are thermally decomposed to change to combustible gas. As described above, under such a high temperature, if the introduced carrier air and the plastic as a combustible are present, they naturally burn, but part of the combustion and the burning of slag which will be described later. Do not hinder.

【0020】ここで、搬入される廃棄プラスチックの大
きさ及び形状は、瞬時に熱分解可能なもので、且つ、空
気による搬送が可能なものでなけらばならず、この為に
は、可級的に小さな細片が望ましいが、本発明者の実験
では、直径20mm以下の細片であれば問題がないこと
が確認された。
Here, the size and shape of the waste plastic to be carried in must be such that it can be pyrolyzed instantaneously and can be transported by air. Although small strips are desirable, it has been confirmed by the inventor's experiments that there is no problem with strips having a diameter of 20 mm or less.

【0021】次いで該可燃ガスは、ロストル16の孔を
通して、燃焼溶融室17内に上昇し、そこで二次空気導
入口18から導かれた空気と反応して燃焼を起こす。こ
のとき、該廃棄プラスチックの分解した可燃ガスの熱カ
ロリーの値は、コークスが7000〜8000kcal
/kgであるのに対し、約8000〜9000kcal
/kgの値を示し、極めてカロリー値が高く、且つ、そ
の熱交換機を通した二次空気は、比較的高温に保たれて
いる。従って、そこから発生する燃焼熱は、従来のコー
クスと同等又はそれ以上であって、その結果、塊状の焼
却灰は円滑に溶融点に至り、溶融スラグGとなる。
Next, the combustible gas rises into the combustion melting chamber 17 through the hole of the rostrum 16, where it reacts with the air introduced from the secondary air inlet 18 to cause combustion. At this time, the value of the thermal calorie of the decomposed combustible gas of the waste plastic is 7000 kcal to 8000 kcal.
/ Kg, about 8000-9000 kcal
/ Kg, a very high calorie value, and the secondary air passed through the heat exchanger is kept at a relatively high temperature. Therefore, the combustion heat generated therefrom is equal to or higher than that of the conventional coke, and as a result, the massive incinerated ash smoothly reaches the melting point and becomes molten slag G.

【0022】このとき、廃棄プラスチックは、瞬時にガ
ス化して焼却灰等と接触するので、塊状の焼却灰をくま
なく囲繞し、且つ、目詰まり等を起こす恐れがなく、溶
融に適した燃焼形態となる。
At this time, the waste plastic is instantaneously gasified and comes into contact with the incineration ash and the like, so that it surrounds the lump incineration ash all over, and there is no danger of clogging or the like, and the combustion form suitable for melting Becomes

【0023】斯かる手段による廃棄プラスチックの燃焼
は、コークスの存在を殆ど必要とせず、コークスを10
0%置き換えた場合でも、本発明者らの実験は成功して
いる。但し、熱源としてコークスを併用することも否定
するものではない。
Combustion of waste plastics by such means requires little coke and reduces coke by 10%.
Even with 0% replacement, our experiments were successful. However, use of coke as a heat source is not denied.

【0024】ここでロストルを通過する以前にあって
は、溶融したスラグは耐火物片ベッド40と接触しつ
つ、ここを流下させる。この流下の過程にあって、耐火
物片ベッド40は耐火性に優れるから溶融スラグとは本
来反応を起こさないが、僅かの反応は避けられず、耐火
物片ベッド40は少しづつ消耗していく。そして、この
消耗の過程にあって、耐火物片ベッド40中に含まれる
六価クロム等の有害金属は、溶融スラグと接触すると拡
散現象を惹起して、僅かづつ溶融スラグ中に移行してい
く。
Here, before passing through the roster, the molten slag flows down while contacting the refractory piece bed 40. In the course of this flow, the refractory piece bed 40 is excellent in fire resistance and does not originally react with the molten slag, but a slight reaction is inevitable, and the refractory piece bed 40 is gradually consumed. . In the course of this consumption, the harmful metal such as hexavalent chromium contained in the refractory piece bed 40 causes a diffusion phenomenon when coming into contact with the molten slag, and gradually moves into the molten slag. .

【0025】そして、該溶融スラグGは、ロストル16
の孔を通して滴下し、ガス分解室12の底部に蓄えら
れ、前述のガス分解室を高温に保つ溶融スラグとしての
働きを成した後、排出口15から流下して、本来の粉砕
処理等に移される。この工程が順次繰り返される。
[0025] The molten slag G is
And is stored at the bottom of the gas decomposition chamber 12 and acts as a molten slag for keeping the gas decomposition chamber at a high temperature. Then, it flows down from the discharge port 15 and is transferred to the original pulverizing process or the like. It is. This step is sequentially repeated.

【0026】さて、この排出口から流下された溶融スラ
グは、冷却工程に移行するが、その冷却は、水砕法や空
冷法を避けて温度管理下において、徐冷法によって可及
的に多くの結晶質を生成させるように徐々に冷却させ
る。
The molten slag flowing down from the discharge port is transferred to a cooling step. The cooling is carried out by a slow cooling method under a temperature control avoiding a granulation method or an air cooling method. Is allowed to cool gradually.

【0027】すると、当該徐冷による冷却工程と前記C
aO/SiO 比の調整等によって当該溶融スラグ
は、アモルファス状態を避けてより多くの結晶質が形成
され、その結晶過程にあって前記耐火物片ベッド40か
ら拡散移動した六価クロム等の有害金属成分も結晶中に
混入され、新たな結晶質の形成に関与する。即ち、焼却
灰の成分は大略CaO 15〜16%、SiO 35〜
36%、Al 17〜18%から成り、このうち
CaO/SiO 比を0.75以上に調整すると、こ
れら成分が1300〜1800℃の温度下で一旦溶融
し、その後冷却を施すと溶融物から新たな結晶が生成さ
れる過程が生まれる。その結果、六価クロム等の有害金
属成分が新たな結晶質中に取り込まれ、容易には外に溶
出しない形態となり、即ち無害化された形態となる。
Then, the cooling step by the slow cooling and the C
By adjusting the aO / SiO 2 ratio or the like, the molten slag forms more crystalline while avoiding the amorphous state, and harmful substances such as hexavalent chromium diffused and moved from the refractory piece bed 40 during the crystallization process. The metal component is also mixed into the crystal and participates in the formation of new crystalline material. That is, the components of the incinerated ash are approximately 15 to 16% of CaO and 35 to 35% of SiO 2 .
36%, consists of Al 2 O 3 17-18% Adjusting these CaO / SiO 2 ratio of 0.75 or more, if these components are once melt at a temperature of 1,300 to 1,800 ° C., subjected to subsequent cooling A process of producing new crystals from the melt is created. As a result, harmful metal components such as hexavalent chromium are taken into the new crystalline material, and are in a form that is not easily eluted outside, that is, a harmless form.

【0028】尚、上記処理の対象物として焼却灰を例に
説明したが、同様の原理で処理が可能な廃棄物であれば
これに限定されるものではなく、製鉄スラッジ、ガラス
屑、金属スラッジ、金属屑その他にも広く応用が可能で
ある。
Although the incineration ash has been described as an example of the object to be treated, the invention is not limited to such waste as long as it can be treated according to the same principle. It can be widely applied to metal scraps and others.

【0029】[0029]

【試験例】溶融処理装置において、表2に示す如き組成
のクロムを含む廃棄耐火レンガを耐火物片ベッドとして
用い、そこに記表1の如き組成の焼却灰を投入して、溶
融処理した。そして、溶融処理した溶融スラグを加温を
加えつつ徐冷し、その冷却固化後の処理物について、溶
出試験を行った。その結果を示すと、表3の如きで、C
+6 が0.005以下の基準で不検出の結果を得る
ことができ、六価クロムが無害化処理されていることが
確認できた。
Test Example In a melting treatment apparatus, a waste refractory brick containing chromium having a composition shown in Table 2 was used as a refractory piece bed, and incineration ash having a composition shown in Table 1 was put into the bed and melted. Then, the melted slag was gradually cooled while applying heat, and a dissolution test was performed on the treated product after the cooling and solidification. The results are shown in Table 3, where C
An undetected result could be obtained on the basis that r + 6 is 0.005 or less, and it was confirmed that hexavalent chromium was detoxified.

【0030】[0030]

【表1】<スラグの組成> [Table 1] <Slag composition>

【0031】[0031]

【表2】<廃棄耐火レンガの組成> [Table 2] <Composition of waste refractory bricks>

【0032】[0032]

【表3】<溶出試験結果> [Table 3] <Dissolution test results>

【0033】[0033]

【発明の効果】以上の構成及び作用に基づいて本発明
は、以下の如き効果を奏する。 (1) 焼却灰等の廃棄物を溶融処理装置にあって、処
理に窮していた六価クロム等の有害金属をむ耐火レンガ
の廃棄物を耐火物片ベッドに利用することができ、且
つ、それが溶融処理過程にあって溶融スラグの結晶化を
促してこれを無害化処理できるという一挙両得の優れた
効果を奏する。
The present invention has the following effects based on the above configuration and operation. (1) Waste such as incinerated ash can be used in a melting treatment device, and waste of refractory bricks containing harmful metals such as hexavalent chromium, which has been difficult to treat, can be used for refractory piece beds, and In the melting process, the slag promotes the crystallization of the molten slag and can be rendered harmless.

【0034】このとき、焼却灰のCaO/SiO
を0.75以上とすれば、六価クロム等の有害金属成分
が新たな結晶質中に取り込まれる条件が向上する。
At this time, if the CaO / SiO 2 ratio of the incinerated ash is set to 0.75 or more, the conditions under which harmful metal components such as hexavalent chromium are taken into new crystals are improved.

【0035】(2)又、必要に応じて、 熱源として殆
どコークスを使用することなく全てを廃棄プラスチック
に置き換えることができるので、エネルギーコストを大
幅に削減することができ、且つ、その際廃棄プラスチッ
クをそのまま燃焼させるのでなく、一旦、高温下で熱分
解させて可燃ガスとし、それを処理対象物を囲繞しつつ
二次空気との混合で燃焼させるので、接触効率を頗る良
好とすることができる。
(2) If necessary, all of the waste plastic can be replaced with waste plastic without using coke as a heat source, so that the energy cost can be greatly reduced. Instead of burning as it is, once, it is thermally decomposed at high temperature to a combustible gas, and it is burned by mixing with secondary air while surrounding the object to be treated, so that the contact efficiency can be made very good .

【図面の簡単な説明】[Brief description of the drawings]

【図1】 本発明装置の断面図。FIG. 1 is a cross-sectional view of the device of the present invention.

【符号の説明】[Explanation of symbols]

10 溶融炉部 11 溶融炉 12 ガス分解室 13 搬送空気導入口 14 バーナー 15 排出口 16 ロストル 17 燃焼溶融室 18 二次空気導入口 19 酸素富化器 20 予備加熱室 21 投入口 22 排気口 30 廃棄プラスチック導入部 31 搬送空気パイプ 32 ホッパー 33 定量供給機 34 ブロワー 40 耐火物片ベッド DESCRIPTION OF SYMBOLS 10 Melting furnace part 11 Melting furnace 12 Gas decomposition chamber 13 Carrier air inlet 14 Burner 15 Outlet 16 Rostor 17 Combustion melting chamber 18 Secondary air inlet 19 Oxygen enricher 20 Preheating chamber 21 Input port 22 Exhaust port 30 Disposal Plastic introduction section 31 Conveying air pipe 32 Hopper 33 Metering machine 34 Blower 40 Refractory piece bed

フロントページの続き (51)Int.Cl.7 識別記号 FI テーマコート゛(参考) F23G 5/44 F23J 1/00 B F23J 1/00 B09B 3/00 303L Fターム(参考) 3K061 AA16 AB02 AB03 AC03 AC13 AC14 BA05 BA09 CA01 DA12 DB16 DB17 FA21 FA25 FA26 FA27 NB03 3K065 AA16 AB02 AB03 AC03 AC13 AC14 BA05 BA09 EA12 GA03 GA13 GA22 GA23 GA33 GA34 4D004 AA07 AA37 AB03 CA27 CA29 CA32 CB04 CB34 CB50 CC02 DA03 DA10 4F301 AA00 AA03 AA13 AA14 CA09 CA25 CA26 CA41 CA52 CA62 CA64 Continuation of the front page (51) Int.Cl. 7 Identification symbol FI Theme coat II (reference) F23G 5/44 F23J 1/00 B F23J 1/00 B09B 3/00 303L F term (reference) 3K061 AA16 AB02 AB03 AC03 AC13 AC14 BA05 BA09 CA01 DA12 DB16 DB17 FA21 FA25 FA26 FA27 NB03 3K065 AA16 AB02 AB03 AC03 AC13 AC14 BA05 BA09 EA12 GA03 GA13 GA22 GA23 GA33 GA34 4D004 AA07 AA37 AB03 CA27 CA29 CA32 CB04 CB34 CB50 CC02 DA03 CA10 A13A25 CA10 CA62 CA64

Claims (3)

【特許請求の範囲】[Claims] 【請求項1】 底部に燃焼室又はガス分解室を配し、そ
の上にスラグを熱溶融させるロストル及び耐火物片ベッ
ドを配し、その上に焼却灰の堆積層を配した溶融炉にお
いて、 該耐火物片ベッドに廃棄処分された有害金属を含む耐火
レンガを用いたことを特徴とする焼却灰等廃棄物の溶融
処理装置。
1. A melting furnace in which a combustion chamber or a gas decomposition chamber is provided at a bottom portion, a roster for thermally melting slag and a refractory piece bed are provided thereon, and a deposition layer of incineration ash is provided thereon. An apparatus for melting waste such as incinerated ash, wherein refractory bricks containing harmful metals disposed of in the refractory piece bed are used.
【請求項2】 該溶融炉の下部に搬送空気を導入すると
共に溶融後のスラグを一時的に滞留させて廃棄プラスチ
ックを熱分解する為の一定空間を形成したガス分解室を
配設し、 該ガス分解室の一部に廃棄プラスチックの細片を搬入す
る搬送空気の導入口を臨ませ、 該ガス分解室の上部に耐火物片ベッド及び溶融スラグの
滴下を促すロストルを配すると共に分解ガスとの燃焼を
促す空気導入口を臨ませた燃焼溶融室を形成した焼却灰
等廃棄物溶融燃焼装置において、 該耐火物片ベッドに廃棄処分された有害金属を含む耐火
レンガを用いたことを特徴とする溶融処理装置。
2. A gas cracking chamber having a fixed space for thermally decomposing waste plastic by introducing conveying air into the lower portion of the melting furnace and temporarily retaining the slag after melting, and A part of the gas decomposition chamber faces the inlet of the carrier air for carrying waste plastic strips, and a refractory piece bed and a roster for facilitating the dripping of molten slag are arranged at the upper part of the gas decomposition chamber. A combustion melting chamber formed with a combustion-melting chamber facing an air introduction port for promoting the combustion of air, characterized in that a fire-resistant brick containing toxic metals disposed of in the refractory piece bed is used in the refractory piece bed. Melt processing equipment.
【請求項3】 焼却灰のCaO/SiO 比を0.7
5以上とした請求項1、2のうちいずれか1項記載の溶
融処理装置。
3. The incinerated ash has a CaO / SiO 2 ratio of 0.7.
The melt processing apparatus according to claim 1, wherein the number is 5 or more.
JP2001123450A 2001-04-20 2001-04-20 Melting processing apparatus for waste such as incinerated ash Pending JP2002317911A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
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Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP2001123450A JP2002317911A (en) 2001-04-20 2001-04-20 Melting processing apparatus for waste such as incinerated ash

Publications (1)

Publication Number Publication Date
JP2002317911A true JP2002317911A (en) 2002-10-31

Family

ID=18973000

Family Applications (1)

Application Number Title Priority Date Filing Date
JP2001123450A Pending JP2002317911A (en) 2001-04-20 2001-04-20 Melting processing apparatus for waste such as incinerated ash

Country Status (1)

Country Link
JP (1) JP2002317911A (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN103557528A (en) * 2013-11-04 2014-02-05 赵山山 Integrated environment-friendly gasification and melting incinerator

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN103557528A (en) * 2013-11-04 2014-02-05 赵山山 Integrated environment-friendly gasification and melting incinerator

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