JP2001288474A - Dry distillation method and combustion method of urban waste - Google Patents

Dry distillation method and combustion method of urban waste

Info

Publication number
JP2001288474A
JP2001288474A JP2000104488A JP2000104488A JP2001288474A JP 2001288474 A JP2001288474 A JP 2001288474A JP 2000104488 A JP2000104488 A JP 2000104488A JP 2000104488 A JP2000104488 A JP 2000104488A JP 2001288474 A JP2001288474 A JP 2001288474A
Authority
JP
Japan
Prior art keywords
garbage
municipal
dry distillation
fine powder
carbonization
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.)
Granted
Application number
JP2000104488A
Other languages
Japanese (ja)
Other versions
JP4490549B2 (en
Inventor
Toru Kubota
亨 久保田
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.)
Individual
Original Assignee
Individual
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Filing date
Publication date
Application filed by Individual filed Critical Individual
Priority to JP2000104488A priority Critical patent/JP4490549B2/en
Publication of JP2001288474A publication Critical patent/JP2001288474A/en
Application granted granted Critical
Publication of JP4490549B2 publication Critical patent/JP4490549B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

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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
    • Y02EREDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
    • Y02E50/00Technologies for the production of fuel of non-fossil origin
    • Y02E50/10Biofuels, e.g. bio-diesel
    • 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
    • Y02EREDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
    • Y02E50/00Technologies for the production of fuel of non-fossil origin
    • Y02E50/30Fuel from waste, e.g. synthetic alcohol or diesel

Landscapes

  • Gasification And Melting Of Waste (AREA)
  • Processing Of Solid Wastes (AREA)
  • Coke Industry (AREA)
  • Solid Fuels And Fuel-Associated Substances (AREA)

Abstract

PROBLEM TO BE SOLVED: To provide an improved combustion method for rendering urban wastes harmless and recovering resources from urban wastes. SOLUTION: The treatment method comprises generation of stable, pollution- free carbide which does not emit toxic materials or heavy metals by dry distillation of urban wastes before complete combustion by a catalytic dry distillation plant. The method comprises grinding urban wastes, especially garbage, to fine powder, preferably fine powder with a smallness of 100-150 mesh, and then subjecting the same to dry distillation and carbonization. Any known method of complete combustion may be used.

Description

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

【0001】[0001]

【産業上の利用分野】本発明は、都市ゴミ、特に塵芥の
乾留方法および都市ゴミの、途中工程に乾留工程の存在
する燃焼方法に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method for carbonizing municipal garbage, particularly garbage, and a method for burning municipal garbage in which a carbonization process is provided in the process.

【0002】[0002]

【従来の技術】全国的に年々排出量が増え続けている一
般家庭ゴミや、事務所のゴミについて収集、運搬、処
理、処分する立場にある全国の市町村は、困窮の極みで
ある。これからは、生産者の立場、流通業者の立場、あ
るいは消費者の立場でゴミの資源化をしていかなければ
ならない。そして、環境保全上安心できるものでなけれ
ばならない。
2. Description of the Related Art Municipalities nationwide who collect, transport, treat and dispose of general household garbage and office garbage, whose emissions are increasing year by year nationwide, are in extreme difficulty. From now on, it is necessary to recycle garbage as producers, distributors, or consumers. And it must be safe for environmental protection.

【0003】ゴミは多種多様の元素から作られた物質で
あるため、そのまま埋めても、焼却して埋めても、経年
的には川や地下水の汚染を引き起こす恐れがある。まし
てやゴミの中には種々の化学物質、農薬などの毒性物質
や、感染性が問題になるゴミが混入することも考えられ
る。ゴミの組成をみると、厨芥(生ゴミ)が最も多く、
紙類、プラスチック類、ガラス類、その他となってい
る。ゴミの分別の基本は、不燃ゴミと可燃ゴミを分けて
焼却と埋立てをして、ゴミの資源化を図ることである。
[0003] Since garbage is a substance made from a variety of elements, there is a risk that rivers and groundwater will be polluted over time, whether buried as it is or buried by incineration. Furthermore, it is conceivable that toxic substances such as various chemical substances and pesticides, and trash for which infectivity is a problem are mixed in the trash. Looking at the composition of garbage, kitchen garbage (garbage) is the largest,
Paper, plastic, glass, etc. The basics of garbage separation are to separate non-combustible garbage and combustible garbage and incinerate and landfill them to recycle garbage.

【0004】これまでの処理方法としては、生ゴミのコ
ンポスト化、廃プラスチックは燃やすと焼却炉内が高温
となり、炉体や煙突の耐久性に問題が生じる上に、有害
ガスを発生するので、不燃ゴミとして埋立処分してい
る。また、廃棄物処理を大別すると、リサイクル、焼
却、埋立となる。このうち環境保全の観点からは、リサ
イクルが重視されるが、これまでは、焼却処理が主流を
なしている。埋立処理は、国土の狭い我が国では先行き
がなく、有機物や有害物質の埋立は土壌を汚染する。
[0004] Conventional treatment methods include composting of garbage, and burning of waste plastics, when burning, the temperature inside the incinerator becomes high, which causes problems in the durability of the furnace body and the chimney and generates harmful gas. Landfilled as incombustible waste. Recycling, incineration and landfill can be roughly divided into waste treatment. Of these, recycling is emphasized from the viewpoint of environmental protection, but incineration has been the mainstream until now. Landfilling has no future in Japan, where land is narrow, and landfilling of organic and harmful substances pollutes the soil.

【0005】焼却処理は、有害物質の無害化や伝染病の
予防、また短時間で大量の減量ができるなど利点も多い
が環境保全上で問題点が多く、特に経済面でのコスト高
に大きな欠点がある。
[0005] Incineration treatment has many advantages such as detoxification of harmful substances, prevention of infectious diseases, and large-scale weight reduction in a short time, but it has many problems in environmental preservation, and it is particularly costly in terms of economics. There are drawbacks.

【0006】[0006]

【発明が解決しようとする課題】本発明の目的は、都市
ゴミの無害化・再資源化のための改良された燃焼方法を
提供することである。より詳細には、本発明の目的は、
都市ゴミを完全に焼却して、将来にわたり重金属類やダ
イオキシン類で環境を汚染することがない安全なセメン
ト系の資材をつくることができる焼却灰にする都市ゴミ
の燃焼方法を提供することである。
SUMMARY OF THE INVENTION It is an object of the present invention to provide an improved combustion method for detoxifying and recycling municipal waste. More specifically, the object of the present invention is to
It is to provide a method of burning municipal garbage by completely incinerating the municipal garbage and making incinerated ash that can produce a safe cement-based material without polluting the environment with heavy metals and dioxins in the future. .

【0007】[0007]

【課題を解決するための手段】本発明者は、完全焼却に
至るまでに、途中で乾留させ、有害物質や重金属公害の
発生のない無公害の安定した物質(炭化)を生成するこ
とを特徴とする触媒方式乾留プラントによる処理方法を
開発した。
Means for Solving the Problems The present inventor is characterized in that carbonization is performed on the way to complete incineration to produce a pollution-free stable substance (carbonized) free of harmful substances and heavy metal pollution. A treatment method using a catalytic carbonization plant was developed.

【0008】本発明は、都市ゴミ、特に塵芥を微粉状に
粉砕処理してから乾留して炭化させることを特徴とする
都市ゴミの乾留方法を要旨としている。
The gist of the present invention is to provide a method of carbonizing city garbage, which is characterized in that municipal garbage, especially garbage, is pulverized into fine powder and then carbonized by carbonization.

【0009】また、本発明は、都市ゴミ、特に塵芥の無
害化・再資源化のための燃焼方法において、完全焼却に
至るまでに途中で都市ゴミ、特に塵芥を乾留させ炭化物
質を生成する工程を経ることを特徴とする方法を要旨と
している。
Further, the present invention relates to a combustion method for detoxifying and recycling municipal garbage, especially garbage, in a process of carbonizing municipal garbage, especially garbage, to produce carbonized substances on the way to complete incineration. The method is characterized by passing through.

【0010】上記の工程が、都市ゴミ、特に塵芥を微粉
状に粉砕処理してから、好ましくは100〜150メッ
シュの微粒子に粉砕処理してから行うことを特徴として
おり、その場合、本発明は、都市ゴミ、特に塵芥の無害
化・再資源化のための燃焼方法において、完全焼却に至
るまでに途中で都市ゴミ、特に塵芥を微粉状に粉砕処理
してから、好ましくは100〜150メッシュの微粒子
に粉砕処理してから、乾留させ炭化物質を生成する工程
を経ることを特徴とする方法である。完全焼却させる方
法自体は公知のいずれの方法を採用してもよい。
The above-mentioned process is characterized in that municipal garbage, especially garbage, is crushed into fine powder, and then crushed into fine particles of preferably 100 to 150 mesh. In a combustion method for detoxifying and recycling municipal garbage, particularly garbage, municipal garbage, especially garbage, is pulverized into fine powder on the way until complete incineration, and is preferably 100 to 150 mesh. The method is characterized by passing through a step of pulverizing into fine particles and then carbonizing to produce a carbonized substance. Any known method may be employed for the method of complete incineration.

【0011】[0011]

【発明の実施の形態】乾留処理工程は、塵芥を、外気と
絶縁された低酸素状態の空間で一定温度および一定時間
維持する炭化工程である。塵芥を必要に応じ乾燥処理し
て含水率を低減する乾燥処理工程に付すことができる。
場合により乾燥処理された塵芥は粉砕処理され微粉状態
にされ、その後に上記の外気と絶縁された低酸素状態の
空間で、一定温度および一定時間維持して乾留される。
乾燥処理工程および/または乾留処理工程は、排煙処理
工程を付属させることができる。
DESCRIPTION OF THE PREFERRED EMBODIMENTS The carbonization treatment step is a carbonization step of maintaining dust at a constant temperature and for a fixed time in a low oxygen state space insulated from the outside air. The garbage can be subjected to a drying treatment step for drying the garbage as needed to reduce the water content.
The refuse that has been dried in some cases is pulverized to be in a fine powder state, and then dry-dried in a low-oxygen space insulated from the outside air at a constant temperature and a constant time.
The drying treatment step and / or the dry distillation treatment step may be accompanied by a smoke exhaust treatment step.

【0012】乾留処理時の加熱は100℃〜450℃の
温度範囲で行われる。必用ににより塩化物の析出が始ま
る温度(200℃)以下、またはプラスチックの溶解が
始まる温度(100℃〜150℃)以下とすることがで
きる。都市ゴミに含まれている塩化物が析出する温度以
下である場合、乾留処理中には塩素系ガスの発生はな
く、また、プラスチック類が軟化してバインダの役目を
果し、取り扱いの安定した形状の脱塩素剤を混合した固
形化処理物(ペレット)が得られ、しかも、炭化処理し
ているので、後段工程において固形化燃料として使用で
きる燃焼効率の良い微粉状の固形化燃料が得られる。ま
た、後段工程において排煙処理工程を付属させた装置を
用いて焼却灰の完全燃焼装置を使用する場合は、上記の
乾留処理工程において、処理温度200℃〜450℃
に、時間40分〜60分維持する。上記の粉砕処理工程
において、100〜150メッシュの微粒子に粉砕処理
する。
Heating during the carbonization treatment is performed in a temperature range of 100 ° C. to 450 ° C. If necessary, the temperature can be lower than the temperature at which chloride precipitation starts (200 ° C.) or lower than the temperature at which plastic dissolution starts (100 ° C. to 150 ° C.). When the temperature is lower than the temperature at which the chloride contained in the municipal waste precipitates, no chlorine-based gas is generated during the dry distillation treatment, and the plastics soften to serve as a binder, and the handling becomes stable. A solidified product (pellet) mixed with a dechlorinating agent in a shape can be obtained, and since it has been carbonized, a finely powdered solid fuel with good combustion efficiency that can be used as a solidified fuel in the subsequent step can be obtained. . Further, when a complete incineration ash combustion apparatus is used using an apparatus to which a smoke exhaust treatment step is attached in a later step, in the above dry distillation treatment step, the treatment temperature is 200 ° C to 450 ° C.
And maintain the time for 40 to 60 minutes. In the above-mentioned crushing process, crushing is performed to fine particles of 100 to 150 mesh.

【0013】乾留処理を受ける都市ゴミは微粉末に粉砕
してその表面積を大きくすることで、その乾留速度を高
めることができる。まず、固形物選別、鉄分選別等し、
乾留処理を受ける前に、100〜150メッシュの微粉
末にする。炭化炉内の乾留(炭化)は微粉末に粉砕する
ことで、乾留速度が促進される。
Municipal waste subjected to the carbonization treatment can be pulverized into fine powder to increase the surface area, thereby increasing the carbonization speed. First of all, we sort solids, sort iron, etc.
Before being subjected to the carbonization treatment, it is pulverized to a fine powder of 100 to 150 mesh. The carbonization rate in the carbonization furnace is accelerated by pulverizing the carbonization (carbonization) into fine powder.

【0014】[0014]

【実施例】本願発明の詳細を実施例で説明する。本願発
明はこれら実施例によって何ら限定されるものではな
い。
DESCRIPTION OF THE PREFERRED EMBODIMENTS The present invention will be described in detail with reference to embodiments. The present invention is not limited by these examples.

【0015】参考例1 生ゴミ1000gの組成を調べたら厨芥(生ゴミ)28
5g、紙類320g、プラスチック160g、ガラス1
20g、その他115gであった。このゴミを400℃
の炭化炉で30分加熱し、計量したら595gになっ
た。
Reference Example 1 When the composition of 1,000 g of garbage was examined, kitchen garbage (garbage) 28
5 g, paper 320 g, plastic 160 g, glass 1
20 g and other 115 g. 400 ° C
Was heated in a carbonization furnace for 30 minutes and weighed to 595 g.

【0016】参考例2 同じ量のゴミをガラスその他不燃物を取り除き、同じよ
うに400℃の炭化炉で30分加熱させたら425gに
なった。
Reference Example 2 The same amount of dust was removed of glass and other non-combustible materials, and heated in a carbonizing furnace at 400 ° C. for 30 minutes to obtain 425 g.

【0017】実施例1 同じ量の、同じゴミをガラスその他不燃物を取り除き、
粉砕して微粉末にして、同じように400℃の炭化炉で
30分加熱させたら320gになった。
Example 1 The same amount of the same dust was removed from glass and other non-combustible materials.
The powder was pulverized to a fine powder and heated in a carbonizing furnace at 400 ° C. for 30 minutes to obtain 320 g.

【0018】参考例1、2ならびに実施例1の結果か
ら、不燃物を除き微粉末にして処理すると炭化が早いこ
とが分かった。
From the results of Reference Examples 1 and 2 and Example 1, it was found that carbonization was faster when the powder was treated with fine powder except for non-combustible substances.

【0019】実施例2 温度400℃の乾燥炉の中に微粉末のゴミをバーナーで
噴霧したところ、瞬時に燃え炭化された。
Example 2 Fine powder dust was sprayed into a drying furnace at a temperature of 400 ° C. with a burner, and was instantaneously burned and carbonized.

【0020】[0020]

【発明の効果】都市ゴミの無害化・再資源化のための改
良された燃焼方法を提供することができる。都市ゴミを
完全に焼却して、将来にわたり重金属類やダイオキシン
類で環境を汚染することがない安全なセメント系の資材
をつくることができる焼却灰を得るための改良された都
市ゴミの燃焼方法を提供することができる。
According to the present invention, an improved combustion method for detoxifying and recycling urban waste can be provided. An improved method of burning municipal garbage to incinerate municipal garbage completely to obtain incinerated ash that can produce safe cement-based materials without polluting the environment with heavy metals and dioxins in the future Can be provided.

───────────────────────────────────────────────────── 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) C10L 5/46 F23G 5/033 ZABA F23G 5/027 ZAB B09B 3/00 ZAB 5/033 ZAB 303J Fターム(参考) 3K061 AA24 AB02 AC01 BA01 BA04 BA07 3K065 AA24 AB02 AC01 BA01 BA04 BA07 4D004 AA03 AA46 AB03 CA04 CA07 CA26 CA28 DA03 DA20 4H012 HA01 4H015 AA01 AB01 BA12 BB03 BB10 CA03 CB01 ──────────────────────────────────────────────────続 き Continued on the front page (51) Int.Cl. 7 Identification symbol FI Theme coat ゛ (Reference) C10L 5/46 F23G 5/033 ZABA F23G 5/027 ZAB B09B 3/00 ZAB 5/033 ZAB 303J F term ( Reference) 3K061 AA24 AB02 AC01 BA01 BA04 BA07 3K065 AA24 AB02 AC01 BA01 BA04 BA07 4D004 AA03 AA46 AB03 CA04 CA07 CA26 CA28 DA03 DA20 4H012 HA01 4H015 AA01 AB01 BA12 BB03 BB10 CA03 CB01

Claims (6)

【特許請求の範囲】[Claims] 【請求項1】 都市ゴミを微粉状に粉砕処理してから
乾留して炭化させることを特徴とする都市ゴミの乾留方
法。
1. A method for carbonizing urban refuse, comprising crushing municipal garbage into fine powder and carbonizing by carbonization.
【請求項2】 都市ゴミが塵芥である請求項1の都市
ゴミの乾留方法。
2. The method of claim 1, wherein the municipal waste is garbage.
【請求項3】 都市ゴミの無害化・再資源化のための
燃焼方法において、完全焼却に至るまでに途中で都市ゴ
ミを乾留させ炭化物質を生成する工程を経ることを特徴
とする方法。
3. A combustion method for detoxifying and recycling municipal garbage, which comprises a step of carbonizing municipal garbage and producing a carbonized substance on the way to complete incineration.
【請求項4】 上記の工程が、都市ゴミを微粉状に粉
砕処理してから行われる請求項1の都市ゴミの無害化・
再資源化のための燃焼方法。
4. The method of claim 1, wherein said step is performed after pulverizing the municipal waste into fine powder.
Combustion method for recycling.
【請求項5】 上記の粉砕処理工程において、100
〜150メッシュの微粒子に粉砕処理する請求項1の都
市ゴミの無害化・再資源化のための燃焼方法。
5. In the above-mentioned pulverizing treatment step, 100
The combustion method for detoxifying and recycling municipal refuse according to claim 1, wherein the municipal garbage is pulverized into fine particles of 150 mesh.
【請求項6】 都市ゴミが塵芥である請求項3、4ま
たは5の都市ゴミの処理方法。
6. The method of claim 3, wherein the municipal waste is garbage.
JP2000104488A 2000-04-06 2000-04-06 Method for carbonization and combustion of municipal waste Expired - Fee Related JP4490549B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP2000104488A JP4490549B2 (en) 2000-04-06 2000-04-06 Method for carbonization and combustion of municipal waste

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP2000104488A JP4490549B2 (en) 2000-04-06 2000-04-06 Method for carbonization and combustion of municipal waste

Publications (2)

Publication Number Publication Date
JP2001288474A true JP2001288474A (en) 2001-10-16
JP4490549B2 JP4490549B2 (en) 2010-06-30

Family

ID=18618021

Family Applications (1)

Application Number Title Priority Date Filing Date
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Country Status (1)

Country Link
JP (1) JP4490549B2 (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2006082045A (en) * 2004-09-17 2006-03-30 Toru Kubota Treatment method for recycling of contaminant and its apparatus
KR102577393B1 (en) 2023-01-18 2023-09-13 (주)현대에스엔티 Processing apparatus of harmlessness with rotating function

Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5056370A (en) * 1973-09-20 1975-05-17
JPS53110265A (en) * 1977-03-05 1978-09-26 Ebara Infilco Co Ltd Burning of wastes
JPH04277072A (en) * 1991-03-06 1992-10-02 Toshiba Mach Co Ltd Method and apparatus for treating garbage
JPH101678A (en) * 1996-06-19 1998-01-06 Mitsui Eng & Shipbuild Co Ltd Thermal decomposition reaction furnace

Patent Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5056370A (en) * 1973-09-20 1975-05-17
JPS53110265A (en) * 1977-03-05 1978-09-26 Ebara Infilco Co Ltd Burning of wastes
JPH04277072A (en) * 1991-03-06 1992-10-02 Toshiba Mach Co Ltd Method and apparatus for treating garbage
JPH101678A (en) * 1996-06-19 1998-01-06 Mitsui Eng & Shipbuild Co Ltd Thermal decomposition reaction furnace

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2006082045A (en) * 2004-09-17 2006-03-30 Toru Kubota Treatment method for recycling of contaminant and its apparatus
JP4599127B2 (en) * 2004-09-17 2010-12-15 株式会社リバース Processing method and apparatus for waste recycling
KR102577393B1 (en) 2023-01-18 2023-09-13 (주)현대에스엔티 Processing apparatus of harmlessness with rotating function

Also Published As

Publication number Publication date
JP4490549B2 (en) 2010-06-30

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