JP3531791B2 - Method and apparatus for melting incinerated fly ash - Google Patents
Method and apparatus for melting incinerated fly ashInfo
- Publication number
- JP3531791B2 JP3531791B2 JP17801298A JP17801298A JP3531791B2 JP 3531791 B2 JP3531791 B2 JP 3531791B2 JP 17801298 A JP17801298 A JP 17801298A JP 17801298 A JP17801298 A JP 17801298A JP 3531791 B2 JP3531791 B2 JP 3531791B2
- Authority
- JP
- Japan
- Prior art keywords
- fly ash
- ash
- melting
- stoker
- 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 - Lifetime
Links
Landscapes
- Gasification And Melting 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、焼却飛灰の溶融方
法に係り、特に、都市ごみ等の固体廃棄物を焼却する際
に発生するストーカ飛灰及び流動飛灰を溶融する方法と
装置に関する。BACKGROUND OF THE INVENTION The present invention relates to a method of melting the incineration fly ash, in particular, a method of melting the stoker fly ash and fluidized fly ash generated when incinerating solid wastes such as municipal waste
Regarding the device .
【0002】[0002]
【従来の技術】従来、都市ごみを焼却炉で焼却した時に
集じん器で捕集された飛灰は、重金属などが溶出する等
の問題があり、現状では一般にそのまま埋め立て処分す
る事はできず、厚生大臣の定める以下の4つの方法によ
り、無害化しなければ処分できなかった。
溶融固化
セメント固化
薬剤処理
酸その他溶媒による安定化
そのうち、焼却飛灰中には、猛毒のダイオキシン類が含
まれていることから、重金属の不溶化とダイオキシン類
の分解を同時に行うことができ、かつ埋め立て地の延命
化の図れる焼却飛灰の溶融固化法がもっとも有効な方法
とされている。さらに、飛灰の溶融固化によってできる
スラグは、有効利用が図れる再生素材としても注目され
ている。2. Description of the Related Art Conventionally, fly ash collected by a dust collector when incinerating municipal solid waste in an incinerator has a problem that heavy metals and the like are eluted, and at present, it cannot generally be landfilled as it is. , Could not be disposed of without detoxifying it by the following four methods specified by the Minister of Health and Welfare. Melt solidification Cement solidification Chemical treatment Stabilization with acids and other solvents Among them, incineration fly ash contains highly poisonous dioxins, so it is possible to insolubilize heavy metals and decompose dioxins at the same time, and landfill. The most effective method is the melting and solidification method of incineration fly ash that can prolong the life of the earth. Furthermore, slag formed by melting and solidifying fly ash has been attracting attention as a recycled material that can be effectively used.
【0003】焼却飛灰の溶融固化法には、次の方法があ
る。
ストーカ式都市ごみ焼却炉から排出される飛灰を、
ガラスあるいは焼却灰と混合して融点を下げて溶融する
方法、
流動床式焼却炉から排出される飛灰を単独で溶融す
る方法、
そして、ストーカ飛灰は、によらなければ溶融処理が
しにくく、溶融炉を長期安定連続運転することは困難と
されている。すなわち、飛灰は、一般に焼却炉の排ガス
処理において、塩化水素などの有害ガスを除去するため
に使用した消石灰を含むため、融点が高く、溶融エネル
ギー原単位の上昇と、炉内温度と溶湯温度上昇による溶
融炉内耐火物損耗などの、悪影響があった。There are the following methods for melting and solidifying incineration fly ash. Fly ash discharged from the stoker type municipal waste incinerator,
Melting process by mixing with glass or incineration ash to lower melting point, melting fly ash discharged from fluidized bed incinerator alone, and stoker fly ash is difficult to melt unless However, it is difficult to operate the melting furnace continuously for a long period of time. That is, since fly ash generally contains slaked lime used to remove harmful gases such as hydrogen chloride in the treatment of exhaust gas from incinerators, it has a high melting point, an increase in the unit energy of melting energy, and the temperature inside the furnace and the temperature of the molten metal. There were adverse effects such as wear of refractory in the melting furnace due to the rise.
【0004】そこで、ストーカ焼却灰や珪素分を含むガ
ラスなどと混ぜて塩基度を低くして、溶融温度を下げな
いと溶融困難とされていた。しかし、ストーカ飛灰は、
見掛け比重が小さく(0.3〜0.4)、見掛け比重の
大きい焼却灰やガラスくず(約1)と混合しても、比重
差のために十分混合できず、塩基度が変動して溶融温度
が変わり、安定した運転ができなかった。一方、流動飛
灰もストーカ飛灰と同様に、厚生大臣指定の無害化処理
なしでは埋め立て処分できないものであるが、流動床式
焼却炉で使用する流動砂などの混入もあり、成分的にス
トーカ式焼却炉の焼却灰に類似しており、そのままでも
溶融温度が高くならずに溶融運転が可能であることが知
られている。Therefore, it has been considered difficult to melt unless the melting temperature is lowered by lowering the basicity by mixing with stoker incinerated ash or glass containing silicon. However, the stoker fly ash is
Even if mixed with incinerated ash or glass waste (about 1), which has a small apparent specific gravity (0.3 to 0.4) and a large apparent specific gravity, it cannot be sufficiently mixed due to the difference in specific gravity, and the basicity fluctuates and melts. The temperature changed and stable operation was not possible. On the other hand, fluid fly ash, like stoker fly ash, cannot be landfilled without detoxification treatment specified by the Minister of Health and Welfare, but because of the inclusion of fluid sand used in fluidized bed incinerators, the stoker is a component. It is known that it is similar to the incineration ash of the incinerator, and that the melting operation is possible without increasing the melting temperature as it is.
【0005】[0005]
【発明が解決しようとする課題】本発明では、上記従来
技術に鑑み、ストーカ炉焼却灰やガラスなどと混合する
ことなく、ストーカ飛灰の融点を下げることができ、溶
融エネルギーの削減と耐火物の損耗を抑制し、安定運転
ができる焼却飛灰の溶融方法と装置を提供することを課
題とする。In view of the above-mentioned prior art, the present invention is capable of lowering the melting point of stoker fly ash without mixing with ash or incinerator ash incinerator furnace, reducing melting energy and refractory materials. It is an object of the present invention to provide a method and an apparatus for melting incineration fly ash, which suppresses the wear of the incinerator and enables stable operation.
【0006】[0006]
【課題を解決するための手段】上記課題を解決するため
に、本発明では、都市ごみ等の廃棄物を焼却するストー
カ式焼却炉から発生する飛灰と、流動床式焼却炉から発
生する飛灰とを、一定割合で混合して灰溶融炉で溶融す
ることを特徴とする焼却飛灰の溶融方法としたものであ
る。前記溶融方法において、ストーカ飛灰と流動飛灰の
混合は、均一に混合するのが良く、また、前記一定割合
は、ストーカ飛灰1に対して、流動飛灰が1以上、好ま
しくは2〜3の割合が良い。また、本発明では、灰を溶
融する溶融炉と、都市ごみ等の廃棄物を焼却するストー
カ式焼却炉から得られる飛灰と流動床式焼却炉から得ら
れる飛灰とを一定割合で混合させる手段と、該混合され
た灰を前記溶融炉に供給する手段とを備えたことを特徴
とする焼却飛灰の溶融装置としたものである。 In order to solve the above-mentioned problems, in the present invention, fly ash generated from a stoker type incinerator for incinerating waste such as municipal solid waste and fly ash generated from a fluidized bed type incinerator. This is a method for melting incineration fly ash, which is characterized in that ash and ash are mixed at a fixed ratio and melted in an ash melting furnace. In the melting method, the stoker fly ash and the fluid fly ash are preferably mixed uniformly, and the fixed ratio is 1 or more of the fluid fly ash, preferably 2 to 1 of the stoker fly ash. A ratio of 3 is good. In the present invention, the ash is melted.
A melting furnace that melts and a stove that incinerates waste such as municipal waste
Fly ash from mosquito type incinerator and from fluidized bed type incinerator
Means for mixing the fly ash to be mixed at a constant ratio,
And a means for supplying ash to the melting furnace.
This is a melting device for incinerated fly ash.
【0007】[0007]
【発明の実施の形態】本発明は、都市ごみ等の廃棄物を
ストーカ式焼却炉で焼却することによって発生する飛灰
と、都市ごみを流動床式焼却炉で焼却することによって
発生する飛灰を、溶融前処理として、一定割合で均一混
合後、灰溶融炉に投入して溶融処理する。一般に、スト
ーカ式焼却炉と流動床式焼却炉は近隣には設置されてい
ないが、複数の都市ごみ焼却場から発生する飛灰などを
一ケ所で灰溶融処理をするケースでは、ストーカ飛灰と
流動飛灰を混合して処理している(センター方式とよ
ぶ)。このように、本発明では、ストーカ飛灰と流動飛
灰を、溶融前処理として混合機により一定割合で均一混
合することにより、飛灰の融点を下げて溶融炉耐火物の
延命化を図ることができ、またかさ比重を上げ安定処理
をすることができる。BEST MODE FOR CARRYING OUT THE INVENTION The present invention relates to fly ash generated by incinerating waste such as municipal waste in a stoker type incinerator and fly ash generated by incinerating municipal waste in a fluidized bed type incinerator. As a pre-melting treatment, the mixture is uniformly mixed at a fixed ratio and then placed in an ash melting furnace to perform the melting treatment. Generally, a stoker type incinerator and a fluidized bed type incinerator are not installed in the neighborhood, but in the case where fly ash generated from multiple municipal waste incinerators is ash melted in one place, Fluid fly ash is mixed and processed (called the center method). Thus, in the present invention, the stoker fly ash and the fluidized fly ash are uniformly mixed by a mixer as a pre-melting treatment at a constant ratio to lower the melting point of the fly ash and prolong the life of the melting furnace refractory. In addition, the bulk density can be increased and stable treatment can be performed.
【0008】次に、本発明を図面を用いて詳細に説明す
る。図1に、本発明の溶融方法を実施するための、装置
の概略構成図を示す。図1において、1は流動飛灰、2
はストーカ飛灰、3、4は貯留ホッパ、5、6は灰計量
器、7、8は灰供給コンベヤ、9は混合装置、10は灰
供給装置、11は灰溶融炉、12はプラズマトーチ、1
3はスラグ、14は排ガスである。図1を用いて、本発
明の方法を説明する。Next, the present invention will be described in detail with reference to the drawings. FIG. 1 shows a schematic configuration diagram of an apparatus for carrying out the melting method of the present invention. In FIG. 1, 1 is fluid fly ash, 2
Is a stoker fly ash, 3 and 4 are storage hoppers, 5 and 6 are ash scales, 7 and 8 are ash supply conveyors, 9 is a mixing device, 10 is an ash supply device, 11 is an ash melting furnace, 12 is a plasma torch, 1
3 is slag and 14 is exhaust gas. The method of the present invention will be described with reference to FIG.
【0009】まず、ストーカ飛灰2と流動飛灰1は、い
ずれも都市ごみ焼却工場からローリー車で運搬されて、
それぞれのホッパ3、4へ受け入れた。焼却量が同一の
場合、ストーカ飛灰と流動飛灰の焼却工場からの発生比
率は概ね1:2〜1:3である。本発明では基本的には
流動飛灰が多ければ良く、多ければ多い程、取り扱い
(処理)が容易となるが、一方が残ることは好ましくな
いので、処理できる範囲で流動飛灰を多く処理するのが
良い。表1に、ストーカ飛灰、流動飛灰及びそれらを混
合した場合の融点測定結果を示す。表1のストーカ飛
灰、流動飛灰共に都市ごみ焼却により発生した飛灰であ
り、いずれも焼却排ガス処理時に中和剤として乾式で使
用した消石灰を含んでおり、一般的な組成のものであ
る。First, both the stoker fly ash 2 and the fluidized fly ash 1 are transported by a truck from an urban refuse incineration plant,
Accepted to each hopper 3, 4. When the amount of incineration is the same, the generation ratio of stoker fly ash and fluid fly ash from the incineration plant is about 1: 2 to 1: 3. In the present invention, basically, the larger the amount of the fluid fly ash, the more the handling (treatment) becomes easier, but it is not preferable that one remains, so that the fluid fly ash is treated in a large amount within the processable range. Is good. Table 1 shows the melting point measurement results of stoker fly ash, fluid fly ash and a mixture thereof. Both the stoker fly ash and the fluid fly ash in Table 1 are fly ash generated by incineration of municipal solid waste, and both contain slaked lime used dry as a neutralizing agent when treating incineration exhaust gas and have a general composition. .
【0010】[0010]
【表1】 [Table 1]
【0011】次に、これらのホッパ3、4から切り出さ
れた2種の飛灰は、灰計量器5、6及びコンベヤ7、8
を通して、後段の2軸スクリュータイプの混合装置9で
一定時間ほぼ均一になるように混合した。混合装置9
は、パドル回転式や回転ドラム式などでも、均一な混合
効果が得られるものであれば何れでも良い。混合飛灰を
成型機で成型すれば、いっそう効果的である。この場合
の混合比率は、図2に示すように塩基度(CaO/Si
O2 )で2以下で、好ましくは1.5〜2程度になるよ
うに、ストーカ飛灰:流動飛灰=1:2〜1:3とする
のが良い。焼却炉の排ガス処理が、ストーカ、流動床焼
却炉とも消石灰を使用しない場合、塩基度はストーカ飛
灰、流動飛灰とも1以下なので、混合比率は任意にでき
る(逆に言うとあえて混合の必要はない)。溶融炉11
は、電気溶融式のプラズマトーチ式バッチ溶融炉で運転
した。溶融炉は燃料式でも連続式でも構わない。Next, the two types of fly ash cut out from these hoppers 3 and 4 are ash scales 5 and 6 and conveyors 7 and 8, respectively.
The mixture was mixed in a twin-screw type mixing device 9 in the subsequent stage so as to be substantially uniform for a certain period of time. Mixing device 9
May be a paddle rotating type, a rotating drum type or the like as long as a uniform mixing effect can be obtained. It is even more effective if the mixed fly ash is molded with a molding machine. The mixing ratio in this case is, as shown in FIG. 2, basicity (CaO / Si
It is preferable that the stoker fly ash: fluid fly ash = 1: 2 to 1: 3 so that O 2 ) is 2 or less, preferably about 1.5 to 2. When the exhaust gas treatment of the incinerator does not use slaked lime for both the stoker and the fluidized bed incinerator, the basicity is 1 or less for both the stoker fly ash and the fluid fly ash, so the mixing ratio can be set arbitrarily (in other words, mixing is necessary. Not). Melting furnace 11
Operated in an electric melting plasma torch batch melting furnace. The melting furnace may be a fuel type or a continuous type.
【0012】[0012]
【実施例】以下、本発明を実施例により具体的に説明す
る。
実施例1
図1の装置を用いて、ストーカ飛灰と流動飛灰の混合比
を1:3とした混合飛灰(実施例)と、ストーカ飛灰と
ストーカ焼却灰の混合比を1:3とした混合灰(比較
例)とを用いて溶融試験を行った。その際の処理条件と
結果を表2に示す。EXAMPLES The present invention will be specifically described below with reference to examples. Example 1 Using the apparatus shown in FIG. 1, mixed fly ash (Example) in which the mixing ratio of stoker fly ash and fluidized fly ash was 1: 3, and mixing ratio of stoker fly ash and stoker incinerated ash was 1: 3. And a mixed ash (comparative example) was used to perform a melting test. Table 2 shows the processing conditions and results at that time.
【0013】[0013]
【表2】 [Table 2]
【0014】これらの結果より、塩基度1.5〜2の範
囲の混合比では、融点がコンスタントに1400℃程度
以下になり、耐火物の損耗が抑えられ、溶融炉補修間隔
が従来の2倍程度に延びた。一方、従来のようにストー
カ飛灰とストーカ焼却灰を混合した場合は、飛灰混合比
が大きいほど(焼却飛灰1に対し焼却灰4以下)、均一
に混合する事が困難なため、塩基度はばらつき、溶湯の
融点もばらついた結果、溶融電力が変動し、耐火物の損
耗を促進する。溶融炉の耐火物の損耗は、溶湯である液
相と雰囲気ガスの気相の界面部分、すなわち、溶湯の流
れがある部分が損耗する。また、ストーカ飛灰のかさ比
重は0.35〜0.5で、流動飛灰のかさ比重は0.7
程度なので、上記の混合比率では0.5〜0.65にな
った。上記のかさ比重では、炉内で飛灰が飛散し難く、
炉内や出湯口が監視可能になった。従来のストーカ飛灰
と焼却灰の混合灰溶融では、混合が十分でないため、か
さ比重が小さい混合状態で炉内に供給されると飛散が生
じ、監視が困難で安定な溶融運転ができなかった。From these results, at a mixing ratio in the range of basicity of 1.5 to 2, the melting point is constantly about 1400 ° C. or less, the wear of refractory is suppressed, and the melting furnace repair interval is twice as long as the conventional one. Extended to a degree. On the other hand, when the stoker fly ash and the stoker incineration ash are mixed as in the conventional case, the higher the fly ash mixing ratio (incineration fly ash 1 to incineration ash 4 or less), the more difficult it is to uniformly mix the base. As a result of variations in the degree and the melting point of the molten metal, the melting power fluctuates, and the wear of the refractory is promoted. The refractory in the melting furnace is worn away at the interface between the liquid phase which is the molten metal and the vapor phase of the atmospheric gas, that is, the part where the molten metal flows. The bulk specific gravity of the stoker fly ash is 0.35 to 0.5, and the bulk specific gravity of the fluid fly ash is 0.7.
Since it is a degree, it became 0.5 to 0.65 in the above mixing ratio. With the above-mentioned bulk specific gravity, fly ash is difficult to fly in the furnace,
The inside of the furnace and the tap hole can now be monitored. In the conventional mixed ash fusion of stoker fly ash and incineration ash, mixing is not sufficient, so if it is supplied into the furnace in a mixed state with a low bulk specific gravity, scattering occurs, monitoring is difficult and stable melting operation was not possible. .
【0015】[0015]
【発明の効果】本発明によれば、ストーカ飛灰と流動飛
灰を一定割合で均一混合して溶融処理することにより、
融点を下げ、耐火物損耗の少ない溶融運転ができると共
に、かさ比重を上げ、安定処理をすることができた。According to the present invention, the stoker fly ash and the fluid fly ash are uniformly mixed at a constant ratio and melt-treated,
The melting point was lowered, melting operation with less wear of refractory was possible, and the bulk specific gravity was increased and stable treatment was possible.
【図1】本発明の溶融方法を実施するための装置の一例
を示す概略構成図。FIG. 1 is a schematic configuration diagram showing an example of an apparatus for carrying out a melting method of the present invention.
【図2】灰の塩基度と融点(℃)の関係を示すグラフ。FIG. 2 is a graph showing the relationship between ash basicity and melting point (° C.).
1:流動飛灰、2:ストーカ飛灰、3、4:貯留ホッ
パ、5、6:灰計量器、7、8:灰供給コンベヤ、9:
混合装置、10:灰供給装置、11:灰溶融炉、12:
プラズマトーチ、13:スラグ、14:排ガス1: Fly fly ash, 2: Stalker fly ash, 3, 4: Storage hopper, 5, 6: Ash meter, 7, 8: Ash supply conveyor, 9:
Mixing device, 10: Ash supply device, 11: Ash melting furnace, 12:
Plasma torch, 13: Slag, 14: Exhaust gas
───────────────────────────────────────────────────── フロントページの続き (58)調査した分野(Int.Cl.7,DB名) B09B 3/00 F23J 1/00 ─────────────────────────────────────────────────── ─── Continuation of front page (58) Fields surveyed (Int.Cl. 7 , DB name) B09B 3/00 F23J 1/00
Claims (4)
式焼却炉から発生する飛灰と、流動床式焼却炉から発生
する飛灰とを、一定割合で混合して灰溶融炉で溶融する
ことを特徴とする焼却飛灰の溶融方法。1. Fly ash generated from a stoker-type incinerator that incinerates waste such as municipal waste and fly ash generated from a fluidized-bed-type incinerator are mixed at a fixed ratio and melted in an ash melting furnace. A method for melting incinerated fly ash, which is characterized in that
均一に混合することを特徴とする請求項1に記載の焼却
飛灰の溶融方法。2. The mixing of the stoker fly ash and the fluid fly ash,
The method for melting incinerated fly ash according to claim 1, wherein the method is a uniform mixing.
て、流動飛灰が1以上であることを特徴とする請求項1
又は2に記載の焼却飛灰の溶融方法。3. The fixed ratio is 1 or more fluid fly ash to 1 stoker fly ash.
Alternatively, the method for melting incinerated fly ash according to 2 above.
棄物を焼却するストーカ式焼却炉から得られる飛灰と流
動床式焼却炉から得られる飛灰とを一定割合で混合させ
る手段と、該混合された灰を前記溶融炉に供給する手段
とを備えたことを特徴とする焼却飛灰の溶融装置。4. A melting furnace for melting ash, and waste such as municipal waste
Fly ash and flow from a stoker incinerator that incinerates waste.
The fly ash obtained from the moving bed incinerator is mixed at a constant ratio.
And means for supplying the mixed ash to the melting furnace
Melter baked却飛ash comprising the and.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP17801298A JP3531791B2 (en) | 1998-06-11 | 1998-06-11 | Method and apparatus for melting incinerated fly ash |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP17801298A JP3531791B2 (en) | 1998-06-11 | 1998-06-11 | Method and apparatus for melting incinerated fly ash |
Publications (2)
Publication Number | Publication Date |
---|---|
JPH11347519A JPH11347519A (en) | 1999-12-21 |
JP3531791B2 true JP3531791B2 (en) | 2004-05-31 |
Family
ID=16041027
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP17801298A Expired - Lifetime JP3531791B2 (en) | 1998-06-11 | 1998-06-11 | Method and apparatus for melting incinerated fly ash |
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