JPH08261425A - Gasification of combustible waste, and melting method of ash - Google Patents
Gasification of combustible waste, and melting method of ashInfo
- Publication number
- JPH08261425A JPH08261425A JP9735695A JP9735695A JPH08261425A JP H08261425 A JPH08261425 A JP H08261425A JP 9735695 A JP9735695 A JP 9735695A JP 9735695 A JP9735695 A JP 9735695A JP H08261425 A JPH08261425 A JP H08261425A
- Authority
- JP
- Japan
- Prior art keywords
- gas
- ash
- combustible waste
- carbon
- gasification
- 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
Landscapes
- Gasification And Melting Of Waste (AREA)
Abstract
Description
【0001】[0001]
【産業上の利用分野】可燃性の一般廃棄物及び産業廃棄
物の処理に於いて、鉄、アルミニウム等の有価物を回収
すると共に、灰及び炭素類の固化物を乾留ガス化で発生
したガスを燃焼させて溶融固化し、路盤材として活用
し、高温の燃焼ガスは、エネルギー回収して発電し、地
球温暖化防止にも寄与することが出来る。[Industrial field of application] In the processing of flammable general waste and industrial waste, valuable materials such as iron and aluminum are recovered, and gas generated by dry distillation gasification of solidified ash and carbon Can be used as a roadbed material by burning, melting and solidifying, and the high-temperature combustion gas can recover energy to generate electricity and contribute to the prevention of global warming.
【0002】[0002]
【従来の技術】現在、可燃性廃棄物の処理の主流は焼却
処理であるが、次の問題点がありこれ以上の改善は限界
に来ている。2. Description of the Related Art At present, incineration is the main stream for the processing of combustible waste, but the following problems are present and further improvement has reached the limit.
【0003】廃棄物の燃焼ガスが腐蝕性であるところか
ら、水蒸気の温度は300℃が限度とされ、発電効率は
10〜15%に止まっている。更に、灰溶融や排ガス処
理で施設内の消費が増大し、実質的なエネルギー回収は
限界に来ている。Since the combustion gas of the waste is corrosive, the temperature of the steam is limited to 300 ° C., and the power generation efficiency is 10 to 15%. In addition, the consumption of ash and the exhaust gas treatment increase the consumption in the facility, and the practical energy recovery has reached the limit.
【0004】排ガス処理設備が複雑化して、コスト及び
スペースが増大している。[0004] Exhaust gas treatment facilities have become complicated, resulting in increased cost and space.
【0005】環境整備上、灰の溶融が必須となる情勢で
あるが、殆どのプロセスに於いて電力の消費が大きい。Although ash melting is indispensable for environmental maintenance, power consumption is large in most processes.
【0006】ダイオキシン類の生成の低減、抑制 焼却、ガス冷却での一定レベルの発生は防止できないの
で、除去設備が必要となる。Reduction and suppression of production of dioxins It is impossible to prevent a certain level of incineration and gas cooling, so a removal facility is required.
【0007】有価物の回収は困難であるIt is difficult to collect valuables
【発明が解決しようとする課題】現在、廃棄物処理の主
流となっている焼却法には前述の問題がある。本発明
は、下記の課題について解決するものである。The incineration method which is currently the mainstream of waste treatment has the above-mentioned problems. The present invention solves the following problems.
【0008】[0008]
【発明の効果】可燃性ごみを温度500〜700℃で乾
溜ガス化し、発生する固体から金属類を分離し、残りの
残渣は乾溜ガスの燃焼により1000℃以上に昇温溶融
せしめ、高温の燃焼ガスをエネルギー回収することによ
り、以下のように解決される。EFFECTS OF THE INVENTION Combustible waste is gasified by dry distillation at a temperature of 500 to 700 ° C., metals are separated from the generated solids, and the remaining residue is heated to 1000 ° C. or higher by combustion of dry distillation gas, and burned at high temperature. The energy recovery of the gas solves the following problems.
【0009】エネルギー回収の高効率化 現在、15%以下である発電効率を25〜35%に引き
上げる。Increasing the efficiency of energy recovery The power generation efficiency, which is currently 15% or less, is raised to 25 to 35%.
【0010】有価物の回収 鉄、アルミニウム等の有価物を回収することが出来る。Recovery of valuables It is possible to recover valuables such as iron and aluminum.
【0011】灰の溶融固化 ごみのエネルギーのみで灰を溶融固化することが出来
る。Melting and Solidification of Ash Ashes can be melted and solidified only by the energy of waste.
【0012】ダイオキシン類の生成 灰の溶融のため、温度が1000℃以上に上がるので炭
化水素の炭化が進んで不活性となり、ガスの降温過程で
ダイオキシンの発生は大幅に低下すると考えられる。Formation of dioxins It is considered that the temperature rises to 1000 ° C. or higher due to the melting of ash and the hydrocarbon is carbonized to become inactive, so that the generation of dioxins is significantly reduced during the temperature lowering process of the gas.
【0013】[0013]
【課題を解決するための手段】本発明方法の実施例を示
す装置の主要部を図−1に示す。全体的な施設を図−2
に示す。可燃ごみは500〜700℃でガス化され、ガ
スは乾式でHCL、H2Sを除去される。ガス化の残渣
は灰、カーボン、鉄、アルミの金属類である。鉄、アル
ミ等の有価物は炉底に、灰とカーボンの混合物中のカー
ボンは発生ガスに同伴され、精製されたガスと共に燃焼
し、1000℃以上で灰を溶融する。溶融スラッグは水
砕され、最終処分されるか骨材として再利用される。灰
溶融炉の排気はガスタービンで発電し、ガスタービンの
排気は廃熱ボイラーで給水加熱、蒸気発生、蒸気加熱を
して、150℃で大気中に放出される。発生した400
℃40kg/m2の加熱蒸気はスチームタービンで発電
し、復水器で復水される。FIG. 1 shows a main part of an apparatus showing an embodiment of the method of the present invention. Figure 2 of the overall facility
Shown in The combustible waste is gasified at 500 to 700 ° C., and the gas is dry and HCL and H 2 S are removed. Gasification residues are metals such as ash, carbon, iron and aluminum. Valuable materials such as iron and aluminum are entrained in the bottom of the furnace, and carbon in a mixture of ash and carbon is entrained in the generated gas and burns with the purified gas to melt the ash at 1000 ° C or higher. Molten slag is water granulated and either disposed of for final disposal or reused as aggregate. The exhaust gas of the ash melting furnace is generated by a gas turbine, and the exhaust gas of the gas turbine is heated by a waste heat boiler to heat feed water, generate steam, and heat steam, and is discharged to the atmosphere at 150 ° C. Occurred 400
The steam heated at 40 ° C / m 2 is generated by a steam turbine and condensed by a condenser.
【0014】[0014]
【実施例】1900kcal/kgの可燃ごみ200T
/Dを処理したが、ガスタービン、スチームタービンの
発電量は夫々、4640kW、1200kWで発電効率
は30%に達した。ガスタービンを設置せず、1300
℃の燃焼ガスを直接廃熱ボイラーに入れ、蒸気タービン
のみで発電した場合は4870kWの発電が可能で、発
電効率は25%であった。灰は溶融スラッグを水砕して
排出せしめ、路盤材として使用出来る。炉底から鉄くず
6トン/日、アルミニウム2トン/日が得られた。Example: 1900 kcal / kg combustible waste 200T
/ D was treated, but the power generation amounts of the gas turbine and the steam turbine were 4640 kW and 1200 kW, respectively, and the power generation efficiency reached 30%. No gas turbine installed 1300
When the combustion gas at ℃ was put directly into the waste heat boiler and power was generated only by the steam turbine, power generation of 4870 kW was possible, and the power generation efficiency was 25%. Ash can be used as a roadbed material by granulating molten slag and discharging it. Iron scrap 6 tons / day and aluminum 2 tons / day were obtained from the furnace bottom.
【図1】可燃性ごみガス化・灰溶融法の主要部分を示す
フロー図である。FIG. 1 is a flow chart showing a main part of a combustible waste gasification / ash melting method.
1 流動床 2 噴流床 3 空気コンプレッサー 4 ガスタービン 5 廃熱ボイラー 1 Fluidized bed 2 Jet bed 3 Air compressor 4 Gas turbine 5 Waste heat boiler
【図2】可燃ごみガス化・灰溶融システムを示すフロー
図である。FIG. 2 is a flowchart showing a combustible waste gasification / ash melting system.
1 ガス化 2 ガス精製 3 灰溶融 4 ガスタービン 5 蒸気タービン 6 ボイラー加熱器 7 復水器 1 Gasification 2 Gas refining 3 Ash melting 4 Gas turbine 5 Steam turbine 6 Boiler heater 7 Condenser
Claims (2)
性廃棄物を流動床反応装置で500〜700℃で乾留ガ
ス化し、発生する固体残渣は金属類の有価物を分離し、
或いは分離しないで、乾留ガス化によって生成したガス
の燃焼により1000℃以上で溶融せしめ、高温の燃焼
ガスのエネルギー回収することを特徴とする可燃性廃棄
物のガス及び灰の溶融方法。1. A method of treating combustible waste, wherein the combustible waste is subjected to dry distillation gasification at 500 to 700 ° C. in a fluidized bed reactor, and the solid residue generated separates valuable metals from metals.
Alternatively, a method of melting combustible waste gas and ash, characterized in that the gas generated by dry distillation gasification is melted at a temperature of 1000 ° C. or higher without being separated, and the energy of the high-temperature combustion gas is recovered.
気流反応器で行うことを特徴とする可燃性廃棄物のガス
化及び灰の溶融方法。2. A method for gasifying combustible waste and melting ash according to claim 1, wherein the ash is melted in an air flow reactor.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP9735695A JPH08261425A (en) | 1995-03-20 | 1995-03-20 | Gasification of combustible waste, and melting method of ash |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP9735695A JPH08261425A (en) | 1995-03-20 | 1995-03-20 | Gasification of combustible waste, and melting method of ash |
Publications (1)
Publication Number | Publication Date |
---|---|
JPH08261425A true JPH08261425A (en) | 1996-10-11 |
Family
ID=14190222
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP9735695A Pending JPH08261425A (en) | 1995-03-20 | 1995-03-20 | Gasification of combustible waste, and melting method of ash |
Country Status (1)
Country | Link |
---|---|
JP (1) | JPH08261425A (en) |
Cited By (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US6190429B1 (en) | 1994-03-10 | 2001-02-20 | Ebara Corporation | Method and apparatus for treating wastes by gasification |
JP2004136184A (en) * | 2002-10-16 | 2004-05-13 | Kangen Yoyu Gijutsu Kenkyusho:Kk | Waste treatment system |
JP2009034679A (en) * | 2008-09-12 | 2009-02-19 | Kangen Yoyu Gijutsu Kenkyusho:Kk | Waste disposal system |
-
1995
- 1995-03-20 JP JP9735695A patent/JPH08261425A/en active Pending
Cited By (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US6190429B1 (en) | 1994-03-10 | 2001-02-20 | Ebara Corporation | Method and apparatus for treating wastes by gasification |
JP2004136184A (en) * | 2002-10-16 | 2004-05-13 | Kangen Yoyu Gijutsu Kenkyusho:Kk | Waste treatment system |
JP2009034679A (en) * | 2008-09-12 | 2009-02-19 | Kangen Yoyu Gijutsu Kenkyusho:Kk | Waste disposal system |
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