JP3276286B2 - Superheated steam production equipment using waste incineration heat - Google Patents
Superheated steam production equipment using waste incineration heatInfo
- Publication number
- JP3276286B2 JP3276286B2 JP06906796A JP6906796A JP3276286B2 JP 3276286 B2 JP3276286 B2 JP 3276286B2 JP 06906796 A JP06906796 A JP 06906796A JP 6906796 A JP6906796 A JP 6906796A JP 3276286 B2 JP3276286 B2 JP 3276286B2
- Authority
- JP
- Japan
- Prior art keywords
- steam
- char
- combustion
- pyrolysis
- temperature
- 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 - Fee Related
Links
- 238000004519 manufacturing process Methods 0.000 title claims description 22
- 238000004056 waste incineration Methods 0.000 title claims description 5
- 238000002485 combustion reaction Methods 0.000 claims description 118
- 238000000197 pyrolysis Methods 0.000 claims description 97
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 46
- 239000012530 fluid Substances 0.000 claims description 42
- 239000002699 waste material Substances 0.000 claims description 35
- 239000000203 mixture Substances 0.000 claims description 25
- 239000000463 material Substances 0.000 claims description 20
- 238000005979 thermal decomposition reaction Methods 0.000 claims description 17
- 238000010438 heat treatment Methods 0.000 claims description 11
- 238000006243 chemical reaction Methods 0.000 claims description 10
- 238000000926 separation method Methods 0.000 claims description 5
- 238000000034 method Methods 0.000 claims description 3
- 230000000116 mitigating effect Effects 0.000 claims description 3
- 239000007789 gas Substances 0.000 description 63
- 239000004576 sand Substances 0.000 description 29
- 239000000460 chlorine Substances 0.000 description 25
- 229910052801 chlorine Inorganic materials 0.000 description 22
- ZAMOUSCENKQFHK-UHFFFAOYSA-N Chlorine atom Chemical compound [Cl] ZAMOUSCENKQFHK-UHFFFAOYSA-N 0.000 description 21
- 239000000567 combustion gas Substances 0.000 description 18
- 238000005260 corrosion Methods 0.000 description 12
- 230000007797 corrosion Effects 0.000 description 12
- 239000006185 dispersion Substances 0.000 description 9
- 238000009835 boiling Methods 0.000 description 6
- 239000010813 municipal solid waste Substances 0.000 description 6
- VEXZGXHMUGYJMC-UHFFFAOYSA-N Hydrochloric acid Chemical compound Cl VEXZGXHMUGYJMC-UHFFFAOYSA-N 0.000 description 5
- 239000000126 substance Substances 0.000 description 4
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 3
- 238000010586 diagram Methods 0.000 description 3
- 239000000446 fuel Substances 0.000 description 3
- 239000007788 liquid Substances 0.000 description 3
- 239000001301 oxygen Substances 0.000 description 3
- 229910052760 oxygen Inorganic materials 0.000 description 3
- 229920003023 plastic Polymers 0.000 description 3
- 239000004033 plastic Substances 0.000 description 3
- 229920000915 polyvinyl chloride Polymers 0.000 description 3
- 239000004800 polyvinyl chloride Substances 0.000 description 3
- 238000010248 power generation Methods 0.000 description 3
- 230000001502 supplementing effect Effects 0.000 description 3
- UGFAIRIUMAVXCW-UHFFFAOYSA-N Carbon monoxide Chemical compound [O+]#[C-] UGFAIRIUMAVXCW-UHFFFAOYSA-N 0.000 description 2
- XEEYBQQBJWHFJM-UHFFFAOYSA-N Iron Chemical compound [Fe] XEEYBQQBJWHFJM-UHFFFAOYSA-N 0.000 description 2
- 239000000428 dust Substances 0.000 description 2
- 238000000605 extraction Methods 0.000 description 2
- 239000003546 flue gas Substances 0.000 description 2
- 239000000295 fuel oil Substances 0.000 description 2
- 239000011521 glass Substances 0.000 description 2
- 238000002844 melting Methods 0.000 description 2
- 230000008018 melting Effects 0.000 description 2
- 150000002894 organic compounds Chemical class 0.000 description 2
- 238000011084 recovery Methods 0.000 description 2
- 239000002918 waste heat Substances 0.000 description 2
- 238000007664 blowing Methods 0.000 description 1
- 125000001309 chloro group Chemical group Cl* 0.000 description 1
- 238000004939 coking Methods 0.000 description 1
- 238000001816 cooling Methods 0.000 description 1
- 238000000354 decomposition reaction Methods 0.000 description 1
- 230000000694 effects Effects 0.000 description 1
- 210000000416 exudates and transudate Anatomy 0.000 description 1
- 239000012634 fragment Substances 0.000 description 1
- IXCSERBJSXMMFS-UHFFFAOYSA-N hydrogen chloride Substances Cl.Cl IXCSERBJSXMMFS-UHFFFAOYSA-N 0.000 description 1
- 239000002440 industrial waste Substances 0.000 description 1
- 229910052742 iron Inorganic materials 0.000 description 1
- 238000002955 isolation Methods 0.000 description 1
- 239000003921 oil Substances 0.000 description 1
- 239000011819 refractory material Substances 0.000 description 1
- 230000000630 rising effect Effects 0.000 description 1
- 239000007787 solid Substances 0.000 description 1
- 238000003756 stirring Methods 0.000 description 1
- 239000011269 tar Substances 0.000 description 1
Landscapes
- Gasification And Melting Of Waste (AREA)
Description
【0001】[0001]
【発明の属する技術分野】本発明は、都市ごみや産業廃
棄物等を焼却し、その燃焼排ガスの熱により蒸気を製造
して、例えば該蒸気を発電プラント等に用いる過熱蒸気
製造に関する発明である。BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to the production of superheated steam by incinerating municipal refuse or industrial waste, producing steam by the heat of the combustion exhaust gas, and using the steam in a power plant or the like. .
【0002】[0002]
【従来の技術】従来より都市ごみ等の廃棄物を焼却する
焼却装置には流動床焼却装置が多く用いられ、かかる装
置は流動床焼却炉内の分散板(例えば多孔板)上に収容
された砂等の流動媒体に分散板下方より空気または焼却
排ガス等を吹き込むことにより流動媒体を流動化すると
ともに加熱し、そのようにして形成された流動床内に都
市ごみ等の廃棄物を投入して燃焼させる。この燃焼によ
り発生した燃焼ガスは、燃焼ガス出口ラインを経てボイ
ラに至り、該ボイラ内で温水との熱接触により蒸気を発
生させ、該蒸気を発電プラント等のタービン駆動源とし
て用いるものである。2. Description of the Related Art Conventionally, fluidized bed incinerators are often used as incinerators for incinerating waste such as municipal solid waste, and such apparatuses are accommodated on a dispersion plate (for example, a perforated plate) in a fluidized bed incinerator. The fluidized medium is fluidized and heated by blowing air or incineration exhaust gas etc. from below the dispersion plate into the fluidized medium such as sand, and waste such as municipal solid waste is thrown into the fluidized bed thus formed. Burn. The combustion gas generated by the combustion reaches a boiler via a combustion gas outlet line, generates steam by thermal contact with hot water in the boiler, and uses the steam as a turbine drive source of a power plant or the like.
【0003】[0003]
【発明が解決しようとする課題】さてかかる都市ごみ等
の廃棄物中には塩ビプラスチック等の含塩素有機化合物
が混入しており、可燃分中にClとして約0.2〜0.
5%含有されている。そして都市ごみ等の廃棄物中に混
入した塩ビプラスチック等に含まれる塩素は、燃焼によ
ってHClとなり(通常、都市ごみ燃焼排ガス中のHC
lは約500〜1000ppm)、焼却炉の後流に設置さ
れた蒸気発生用ボイラのチューブに作用してこれを腐食
させる。特にチューブ表面温度が約350℃以上では温
度の増加とともに高温腐食が顕著となる。このため、従
来、チューブ表面温度は350℃以下にする必要があ
り、製造される蒸気の温度は約300℃が限界であっ
た。その結果、従来のごみ焼却による発電効率は約15
%以下であって、塩素を殆ど含有しない重油やLNG等
を燃料とし、ボイラチューブ温度を500〜600℃に
できるプラントの発電効率約40%に比べて著しく低
く、その改善が強く望まれていた。The waste such as municipal waste contains a chlorine-containing organic compound such as polyvinyl chloride plastic and the like.
Contains 5%. Chlorine contained in PVC plastics and the like mixed into waste such as municipal waste becomes HCl by combustion (usually, HC in municipal waste combustion exhaust gas).
1 is about 500 to 1000 ppm), which acts on the tube of the steam generating boiler installed downstream of the incinerator to corrode it. In particular, when the tube surface temperature is about 350 ° C. or higher, high-temperature corrosion becomes remarkable as the temperature increases. For this reason, conventionally, the tube surface temperature had to be 350 ° C. or less, and the temperature of the produced steam was limited to about 300 ° C. As a result, the power generation efficiency of conventional waste incineration is about 15
% Or less, and using fuel such as heavy oil or LNG containing almost no chlorine as fuel, which is remarkably lower than the power generation efficiency of a plant capable of setting the boiler tube temperature to 500 to 600 ° C. of about 40%, and its improvement has been strongly desired. .
【0004】本発明者らはかかる技術的課題に鑑み、塩
素によるボイラチューブの高温腐食を防止しながら高温
・高圧の過熱蒸気を効率的に得ることのできる過熱蒸気
の製造にかかる発明を提供する事にある。本発明の他の
目的は、ボイラチューブとして高価な高級材料を用いる
ことなく効率良く塩素の低減ともに且つ高温度の過熱蒸
気を得ることの出来る過熱蒸気の製造にかかる発明を提
供する事にある。本発明の他の目的は後記するチャー燃
焼手段におけるチャー燃焼と熱分解手段における熱分解
を効率良く行い、効率良く塩素の低減ともに且つ高温度
の過熱蒸気を得ることの出来る過熱蒸気の製造にかかる
発明を提供する事にある。[0004] In view of such technical problems, the present inventors provide an invention relating to the production of superheated steam capable of efficiently obtaining high-temperature, high-pressure superheated steam while preventing high-temperature corrosion of a boiler tube due to chlorine. It is in the thing. Another object of the present invention is to provide an invention relating to production of superheated steam capable of efficiently reducing chlorine and obtaining high-temperature superheated steam without using expensive high-grade materials as a boiler tube. Another object of the present invention relates to the production of superheated steam capable of efficiently performing the char combustion in the char combustion means and the pyrolysis in the pyrolysis means to be described later, efficiently reducing chlorine, and obtaining high-temperature superheated steam. It is to provide an invention.
【0005】[0005]
【課題を解決するための手段】本第1発明は、温度30
0℃以上の空間内に廃棄物を供給して熱分解反応を行な
わせ、その反応により発生した熱分解ガスと未分解残渣
および流動媒体から成るチャー混合物と不燃物とを互い
に分離する熱分解手段と、 前記熱分解手段より取り出さ
れた未分解残渣および流動媒体から成るチャー混合物
を、空気によって流動させながら前記未分解残渣を燃焼
させるチャー燃焼手段と、 前記熱分解ガスの燃焼熱エネ
ルギーを利用して約400℃以下の温水または蒸気を製
造する第1の蒸気製造手段と、 前記チャー燃焼手段によ
り得られた熱エネルギにより前記第1の蒸気製造手段で
製造された温水または蒸気を過熱蒸気とする第2の蒸気
製造手段を含み、 前記チャー燃焼手段より加熱された流
動媒体の循環経路中に第2のチャー燃焼手段を介在さ
せ、該第2のチャー燃焼手段の燃焼媒体中に、前記第1
若しくは第2の蒸気製造手段を設けたことを特徴とする
ものである。 また、第2発明として、請求項3記載の発
明は、温度300℃以上の空間内に廃棄物を供給して熱
分解反応を行なわせ、その反応により発生した熱分解ガ
スと未分解残渣および流動媒体から成るチャー混合物と
不燃物とを互いに分離する熱分解手段と、 前記熱分解手
段より取り出された未分解残渣および流動媒体から成る
チャー混合物を、空気によって流動させながら前記未分
解残渣を燃焼させるチャー燃焼手段と、 前記熱分解ガス
の燃焼熱エネルギーを利用して約400℃以下の温水ま
たは蒸気を製造する第1の蒸気製造手段と、 前記チャー
燃焼手段により得られた熱エネルギにより前記第1の蒸
気製造手段で製造された温水または蒸気を過熱蒸気とす
る第2の蒸気製造手段を含み、 前記チャー燃焼手段より
加熱された流動媒体を熱分解手段に戻入する流動媒体経
路中に、熱交換手段等からなる熱落差緩和手段を設けた
第2のチャー燃焼手段を介在させたことを特徴とする。
尚、前記供給廃棄物のより好ましい温度域は略350〜
500℃で、前記熱分解ガスの熱エネルギーによって製
造する温水または蒸気の好ましい温度域は略200〜3
50℃であり、さらに前記熱分解手段に用いられる装置
としては例えば流動床、ロータリキルン、スクリュー撹
拌槽等、前記チャー燃焼手段には例えば気泡流動床、高
速流動床等が挙げられる。 According to the first aspect of the present invention, the temperature is set to 30 degrees.
The waste is supplied to the space above 0 ° C and the thermal decomposition reaction is performed.
Pyrolysis gas and undecomposed residue generated by the reaction
The char mixture and the noncombustible
Pyrolysis means for separating the, extracted from the pyrolysis unit
Mixture consisting of separated undecomposed residue and flowing medium
While burning the undecomposed residue with air
Char combustion means for causing combustion of the pyrolysis gas;
Produce hot water or steam of about 400 ° C or less using lug
The first steam producing means to be produced and the char burning means.
With the obtained thermal energy, the first steam producing means
Second steam using the produced hot water or steam as superheated steam
It comprises manufacturing means, a flow which is heated from the char combustion means
A second char combustion means is interposed in the circulation path of the moving medium.
In the combustion medium of the second char combustion means.
Alternatively, a second steam producing means is provided.
Things. According to a third aspect of the present invention,
Akira supplies waste in a space with a temperature of 300 ° C or more to generate heat.
Decomposition reaction is performed and the pyrolysis gas generated by the reaction is
And a char mixture consisting of uncracked residue and fluidized medium
Pyrolysis means for separating the noncombustible material together, the pyrolysis hand
Consists of unresolved residue and fluidized medium removed from the stage
The char mixture is allowed to flow through the
Char burning means for burning the cracked residue, and the pyrolysis gas
Hot water of about 400 ° C or less
Or a first steam producing means for producing steam or steam .
The heat energy obtained by the combustion means makes the first steam
The hot water or steam produced by the steam production means is regarded as superheated steam.
A second steam producing means, wherein the char combustion means
A fluid medium path for returning the heated fluid medium to the pyrolysis means.
In the road, a heat head mitigation means including heat exchange means was provided.
A second char combustion means is interposed.
The more preferable temperature range of the supply waste is approximately 350 to 350.
At 500 ° C, produced by the thermal energy of the pyrolysis gas
The preferred temperature range of the hot water or steam to be produced is approximately 200 to 3
An apparatus which is 50 ° C. and which is used for the thermal decomposition means
For example, fluidized beds, rotary kilns, screw agitators
Examples of the char combustion means such as a stirring tank include a bubble fluidized bed,
A fast fluidized bed and the like can be mentioned.
【0006】かかる発明によれば例えば図3に示すよう
に、都市ごみ等の廃棄物を、例えば熱分解してその熱分
解ガス中にHCl等が含有する含塩素熱分解ガスであっ
ても、該含塩素熱分解ガスの熱エネルギによるボイラ水
の加熱は、略200℃〜320℃前後の略沸点温度とし
ている為に、含塩素熱分解ガスが蒸気発生用ボイラのチ
ューブに作用してもチューブ表面温度が約350℃以上
とならない為に、これを腐食させる事にならない。この
場合前記ボイラ水は加圧により沸点を略200℃〜32
0℃前後に設定してある為に前記含塩素熱分解ガスのボ
イラ水への熱エネルギの付与にバラツキが生じていても
それは該ボイラ水の潛熱の吸収(言い換えれば水から蒸
気への相変換にのみ使用され温度上昇分として作用しな
い)に使用されるために、ボイラ水の熱交換チューブの
表面温度が塩素腐触温度以上に上昇する事なく、安定し
た加熱温度のボイラ水若しくは蒸気を得る事が出来る。According to this invention, for example, as shown in FIG. 3, waste such as municipal waste is pyrolyzed, for example, even if it is a chlorine-containing pyrolysis gas containing HCl or the like in the pyrolysis gas. The heating of the boiler water by the thermal energy of the chlorine-containing pyrolysis gas has a substantially boiling point of about 200 ° C. to 320 ° C. Therefore, even if the chlorine-containing pyrolysis gas acts on the tube of the steam generating boiler, the tube is heated. Since the surface temperature does not exceed about 350 ° C., it does not corrode. In this case, the boiler water has a boiling point of approximately 200 ° C. to 32
Since the temperature is set at about 0 ° C., even if the application of thermal energy to the boiler water of the chlorine-containing pyrolysis gas varies, it is absorbed by the latent heat of the boiler water (in other words, the phase conversion from water to steam). Is used only for the boiler water and does not act as a temperature rise), so that the boiler water or steam at a stable heating temperature is obtained without the surface temperature of the heat exchange tube of the boiler water rising above the chlorine corrosion temperature. I can do things.
【0007】そして前記略300℃〜500℃の熱分解
により分解されなかった未分解残渣は既に脱塩素されて
いるために、これを燃焼させて得られる、例えば500
〜950℃前後の熱エネルギを利用して前記略200℃
〜320℃前後に一次加熱したボイラ水若しくは蒸気を
二次〜三次加熱して400〜500℃の加熱蒸気(ボイ
ラチューブ温度を約450〜550℃)を得てもチュー
ブ腐触が生じる恐れがない。これによりごみ焼却による
発電を行なった場合においても、塩素を殆ど含有しない
重油やLNG等を燃料としたプラントと同様な30〜4
0%の発電効率を得る事が出来る。The undecomposed residue which has not been decomposed by the thermal decomposition at about 300 ° C. to 500 ° C. has already been dechlorinated.
Approximately 200 ° C. using heat energy of about 950 ° C.
Even if boiler water or steam that has been primarily heated to about 320 ° C. is subjected to secondary to tertiary heating to obtain heated steam of 400 to 500 ° C. (boiler tube temperature is about 450 to 550 ° C.), there is no possibility that tube corrosion will occur. . As a result, even when power is generated by incineration of garbage, 30 to 4 fuel cells, such as heavy oil or LNG, containing almost no chlorine, are used.
0% power generation efficiency can be obtained.
【0008】[0008]
【0009】[0009]
【0010】請求項2及び4記載の発明は、前記第1若
しくは第2の蒸気製造手段で加熱された蒸気若しくは前
記いずれかの製造手段に導入される温水若しくは蒸気の
一部を、前記チャー燃焼手段の高温域側に配した熱交換
手段に適宜導入して、該蒸気を加熱することを特徴とす
るものである。The invention according to claims 2 and 4 is characterized in that the steam heated by the first or second steam producing means or a part of the hot water or steam introduced into any of the producing means is subjected to the char combustion. The steam is heated by appropriately introducing the heat into the heat exchange means disposed on the high temperature side of the means.
【0011】[0011]
【0012】[0012]
【0013】請求項5記載の発明は、温度300℃以上
の空間内に廃棄物を供給して熱分解反応を行なわせ、そ
の反応により発生した熱分解ガスと未分解残渣および流
動媒体から成るチャー混合物と不燃物とを互いに分離す
る熱分解手段と、 前記熱分解手段より取り出された未分
解残渣および流動媒体から成るチャー混合物を、空気に
よって流動させながら前記未分解残渣を燃焼させるチャ
ー燃焼手段と、 前記熱分解手段の不燃物取りだし口より
排出された排出物について大型不燃物と他の排出物を分
離し、他の排出物をチャー燃焼手段底部側に給送する第
1のフィルタ手段と、前記燃焼手段の不燃物取りだし口
より排出された排出物について小型不燃物と流動媒体と
を分離し、流動媒体をチャー燃焼手段底部側に給送する
第2のフィルタ手段を設け、更に必要に応じて前記第2
のフィルタ手段の出口側に、灰分を分離し、灰分分離後
の流動媒体をチャー燃焼手段底部側に給送する第3のフ
ィルタ手段と、を設けたことを特徴とするものである。According to a fifth aspect of the present invention, the temperature is 300 ° C. or more.
The waste is supplied to the space to cause a thermal decomposition reaction,
Gas, undecomposed residue and stream generated by the reaction of water
Separation of char mixture consisting of moving medium and incombustible material from each other
Pyrolysis means that, unfractionated taken out from the pyrolysis unit
The char mixture consisting of the decomposed residue and the flowing medium is
Therefore, a chamber for burning the undecomposed residue while flowing
And over the combustion unit, the incombustible extraction discharged effluent from outlet of the pyrolysis means to separate the large incombustible and other emissions, the first for feeding the other exudates to the char combustion means bottom side Filter means, and second filter means for separating the small incombustibles and the fluid medium with respect to the discharge discharged from the incombustible material outlet of the combustion means, and feeding the fluid medium to the bottom side of the char combustion means, Further, if necessary, the second
And a third filter means for separating ash and feeding the ash-separated fluid medium to the bottom side of the char combustion means at the outlet side of the filter means.
【0014】尚、前記第1のフィルタ手段は少なくとも
第2のフィルタ手段より網目を大きくすることが必要
で、具体的には第1のフィルタ手段は投入される廃棄物
の大きさにもよるが5mm前後に、又第2のフィルタ手
段は流動媒体の最大径(約1.0mm)より大きい2m
m前後に設定するのが良い。第3のフィルタ手段は流動
媒体の最小径(約0.2mm)より小さい0.1mm前
後に設定するのが良い。又、前記フィルタ手段には、例
えば振動篩等を用いることが出来る。It is necessary that the first filter means has a mesh size larger than at least the second filter means. More specifically, the first filter means depends on the size of waste to be charged. About 5 mm, and the second filter means is 2 m larger than the maximum diameter of the flowing medium (about 1.0 mm).
It is better to set it to around m. The third filter means is preferably set to about 0.1 mm which is smaller than the minimum diameter (about 0.2 mm) of the fluid medium. Further, for example, a vibration sieve or the like can be used as the filter means.
【0015】かかる請求項1〜5記載の発明によれば前
記いずれの請求項においても熱分解手段で分離されたチ
ャー混合物には塩素が実質的に含まれないので、これを
第2の蒸気製造手段の過熱源として用い500℃以上の
過熱蒸気を得るように構成しても、機器の高温腐食は生
じない。[0015] Since the char mixture separated by pyrolyzing means even in the any of the claims according to the invention of such claims 1-5, wherein not included in the chlorine substantially, the second steam producing this Even if it is used as a superheat source of the means to obtain superheated steam of 500 ° C. or more, high-temperature corrosion of equipment does not occur.
【0016】また第1の蒸気製造手段の加熱源には、塩
素を含む熱分解ガスの燃焼排ガスを用いるも、該熱を利
用して約400℃以下、具体的には略200〜320℃
以下の温水または蒸気を製造を製造するものである為
に、高温腐食の温度以下の温度しか加熱しないために、
ボイラチューブ等の腐食の恐れはなく、高価な高級材料
を用いる必要はない。As the heating source of the first steam producing means, a combustion exhaust gas of a pyrolysis gas containing chlorine is used, but the heat is utilized to be about 400 ° C. or less, specifically, about 200 to 320 ° C.
In order to produce only the following hot water or steam, to heat only below the temperature of hot corrosion,
There is no danger of corrosion of boiler tubes and the like, and there is no need to use expensive high-grade materials.
【0017】請求項2又は4記載の発明においては、前
記第1若しくは第2の蒸気製造手段で加熱された蒸気若
しくは前記いずれかの製造手段に導入される温水若しく
は蒸気の一部を、前記燃焼手段の高温域側に配した熱交
換手段(以下第1の熱交換手段という)に適宜導入する
ことを特徴とするものである。In the invention described in claim 2 or 4 , the steam heated by the first or second steam producing means or a part of the hot water or steam introduced into any one of the producing means is subjected to the combustion. It is characterized in that it is appropriately introduced into heat exchange means (hereinafter referred to as first heat exchange means) arranged on the high temperature side of the means.
【0018】即ち、前記チャー燃焼手段では空気によっ
てチャー混合物を流動させながら未分解残渣を燃焼させ
るので、その燃焼ガス中は高温、具体的には700℃〜
950℃になる。That is, since the char combustion means burns the undecomposed residue while flowing the char mixture with air, the combustion gas has a high temperature, specifically 700 ° C.
It reaches 950 ° C.
【0019】そこで該高温ガスを利用して前記第1若し
くは第2の蒸気製造手段で加熱された蒸気若しくは前記
いずれかの製造手段に導入される温水若しくは蒸気の一
部と熱交換する事により、後記する作用を営むことが出
来る。Therefore, the high-temperature gas is used to exchange heat with the steam heated by the first or second steam producing means or a part of the hot water or steam introduced into any of the producing means. The following functions can be performed.
【0020】即ち、前記第1の蒸気製造手段に導入され
る温水を前記熱交換手段に導入してある程度の昇温を図
ってもよく、又、前記第2の蒸気製造手段に導入される
温水又は蒸気を前記第1の蒸気製造手段とともに、前記
熱交換手段にパラレルに導入することにより、第2の蒸
気製造手段の加熱量を多くする事が出来、多量の過熱蒸
気を得ることが出来る。That is, the hot water introduced into the first steam producing means may be introduced into the heat exchange means to raise the temperature to a certain extent, or the hot water introduced into the second steam producing means may be heated. Alternatively, by introducing steam in parallel with the first steam producing means to the heat exchanging means, the amount of heating of the second steam producing means can be increased, and a large amount of superheated steam can be obtained.
【0021】更に前記チャー燃焼手段の高温域側は、8
00〜950℃に加熱されているために、第2の蒸気製
造手段で加熱後の過熱蒸気を前記熱交換手段に導入する
ことにより、一層加熱された例えば400〜520℃の
過熱蒸気を得ることも出来、十分加熱された過熱蒸気を
得ることが出来る。従って第1の蒸気製造手段、第2の
蒸気製造手段、及び前記、第1の熱交換手段を利用し
て、実質的に直列/並列の多段階昇温を図ることにより
多量且つ十分加熱された過熱蒸気を得ることが出来る。Further, the high temperature side of the char combustion means is 8
Since the heated superheated steam is heated to 00 to 950 ° C., the superheated steam heated by the second steam producing means is introduced into the heat exchanging means to obtain a further heated superheated steam of, for example, 400 to 520 ° C. And a sufficiently heated superheated steam can be obtained. Therefore, the first and second steam producing means, the second steam producing means, and the first heat exchanging means were used to increase the temperature substantially in series / parallel in a multi-step manner, so that a large amount and sufficient heat were obtained. Superheated steam can be obtained.
【0022】又前記チャー燃焼手段の高温域側に熱交換
手段を配設する事は、950〜1300℃と無用に高く
なった高温域側をそのまま出口ラインに流すと通常の耐
火材では温度的に持たないが、これを800〜950℃
に落とすことにより通常の耐火材ラインの利用が可能と
なる。又前記のように800〜950℃に落としても第
2の蒸気製造手段における蒸気温度を400〜520℃
に維持する上で何の支障もない。The provision of the heat exchange means on the high-temperature area side of the char combustion means means that when the high-temperature area, which is unnecessarily high at 950 to 1300 ° C., is allowed to flow to the outlet line as it is, the temperature of ordinary refractory material becomes high. To 800-950 ° C
The normal refractory line can be used. Further, even if the temperature is lowered to 800 to 950 ° C as described above, the steam temperature in the second steam producing means is set to 400 to 520 ° C.
There is no hindrance in maintaining it.
【0023】一方、前記チャー燃焼手段より加熱された
流動媒体も同様に高温となる。そこで請求項1記載の発
明のように、その高温の流動媒体を利用して、前記チャ
ー燃焼手段により加熱された流動媒体の循環経路中に第
2のチャー燃焼手段を介在させ、該第2のチャー燃焼手
段の燃焼媒体中に、前記第1若しくは第2の蒸気製造手
段若しくは請求項3記載の熱交換手段を前記チャー燃焼
手段の高温域側に配設するのがよい。これにより、第1
の蒸気製造手段、第2の蒸気製造手段、及び前記第1及
び第2の熱交換手段を利用して、実質的に直列/並列の
多段階昇温を図ることにより多量且つ十分加熱された過
熱蒸気を得ることが出来る。従って、流動媒体は熱容量
が大きくその熱接触により安定した高温が得られる。On the other hand, the temperature of the fluid medium heated by the char combustion means also becomes high. Therefore, as in the first aspect of the present invention, the second char combustion means is interposed in the circulation path of the fluid medium heated by the char combustion means by utilizing the high temperature fluid medium, and the second char combustion means is provided. It is preferable that the first or second steam producing means or the heat exchange means according to claim 3 is disposed in the combustion medium of the char burning means on the high temperature side of the char burning means. Thereby, the first
A large amount of sufficiently heated superheat by substantially multi-stage heating in series / parallel using the steam producing means, the second steam producing means, and the first and second heat exchanging means. You can get steam. Therefore, liquidity medium stable high temperature is obtained by the heat capacity is large thermal contact.
【0024】又、前記チャー燃焼手段の流動媒体は熱分
解手段との間を循環する訳であるが、チャー燃焼手段の
流動媒体の温度は略700〜850℃、一方熱分解手段
の流動媒体の温度は350〜500℃であり、両者間の
熱落差が大きく、この為チャー燃焼手段の流動媒体を熱
分解手段側に直接導入すると、前記熱落差により熱分解
手段内の熱分解温度が高くなったり熱変動が生じる恐れ
があり、従って前記戻入される流動媒体の量の調整が煩
雑化する。The fluid medium of the char combustion means circulates between the pyrolysis means. The temperature of the fluid medium of the char combustion means is approximately 700 to 850 ° C. The temperature is 350 to 500 ° C., and the heat drop between the two is large. Therefore, when the fluid medium of the char combustion means is directly introduced to the pyrolysis means side, the heat drop increases the pyrolysis temperature in the pyrolysis means. Or heat fluctuations may occur, thus complicating the adjustment of the amount of the fluid medium to be returned.
【0025】そこで請求項3記載の発明のように、前記
チャー燃焼手段より加熱された流動媒体を熱分解手段に
戻入する流動媒体経路中に、熱落差緩和手段、好ましく
は熱交換手段を設けた第2のチャー燃焼手段を介在させ
るのがよい。これにより、該第2のチャー燃焼手段で請
求項1記載の発明と同様な効果を得るとともに、例えば
第1のチャー燃焼手段で700〜850℃に加熱した流
動媒体を、前記第2のチャー燃焼手段で熱交換手段によ
る奪熱により500〜700℃に落とし、該500〜7
00℃に落とした流動媒体を熱分解手段に戻入する事が
出来るためになだらかな熱傾斜が可能であり、この結果
前記熱分解手段内の熱分解温度を350℃から500℃
前後に安定して制御が可能である。尚、前記第1及び第
2の熱交換手段にはスーパヒータ若しくはボイラを用い
るのがよい。Therefore, as in the third aspect of the present invention, a thermal head mitigation means, preferably a heat exchange means, is provided in the fluid medium path for returning the fluid medium heated by the char combustion means to the thermal decomposition means. Preferably, a second char combustion means is interposed. Thereby, the same effect as the first aspect of the invention is obtained by the second char combustion means, and for example, the fluid medium heated to 700 to 850 ° C. by the first char combustion means is cooled by the second char combustion means. The temperature is lowered to 500 to 700 ° C by heat removal by the heat exchange means.
Since the fluidized medium dropped to 00 ° C. can be returned to the pyrolysis means, a gentle thermal gradient is possible. As a result, the pyrolysis temperature in the pyrolysis means is increased from 350 ° C. to 500 ° C.
Control is possible stably before and after. It is preferable to use a superheater or a boiler for the first and second heat exchange means.
【0026】さて、請求項5記載の発明は、廃棄物とし
て一般に約200mm程度の廃棄物が前記熱分解手段に
投入されるが、このため前記熱分解手段を構成する例え
ば流動床炉の不燃物取りだし口の径をある程度大きくせ
ねばならず、この為前記取りだし口より不燃物の他に一
部のチャー残査や砂等の流動媒体も取り出されてしま
う。そこで熱分解手段の不燃物取りだし口より排出され
た排出物について前記第1のフィルタ手段により、大型
不燃物と他の排出物を分離し、大型の不燃物のみ排出さ
せ、そして他の排出物については燃焼手段底部側に給送
し燃焼の用に供しようとするものである。According to a fifth aspect of the present invention, generally about 200 mm of waste is introduced into the thermal decomposition means as waste. It is necessary to increase the diameter of the discharge port to some extent, so that some char residue and a fluid medium such as sand are taken out of the discharge port in addition to the non-combustible material. Therefore, the first filter means separates large incombustibles and other exhausts from the exhausts discharged from the incombustible material outlet of the thermal decomposition means, and discharges only large incombustibles. Is intended to be fed to the bottom of the combustion means and used for combustion.
【0027】更に前記チャー燃焼手段には既に大型の不
燃物が除去されているために、又チャー残査も十分燃焼
されているために、不燃物取りだし口より排出された排
出物については小型不燃物と流動媒体のみを第2のフィ
ルタ手段で分離すればよく、これにより分離された流動
媒体を燃焼手段底部側に給送すれば流動媒体の損失を防
止して循環再使用が可能となる。また第3フィルタ手段
は必ずしも必要とするものではないが、第2フィルタ手
段で補足されなかった流動砂を補足しながら灰分のみを
外部に排出するもので、これにより効率的な灰分除去と
流動砂の回収が容易になる。Further, since the large incombustibles have already been removed from the char burning means and the char residue has been sufficiently burned, the exhaust discharged from the incombustible material outlet is small incombustible. Only the material and the fluid medium need to be separated by the second filter means. By feeding the separated fluid medium to the bottom side of the combustion means, loss of the fluid medium can be prevented, and circulating reuse can be performed. Although the third filter means is not always necessary, it discharges only the ash to the outside while supplementing the fluid sand not supplemented by the second filter means, so that efficient ash removal and fluid sand can be achieved. Recovery becomes easier.
【0028】[0028]
【発明の実施の形態】以下図面を参照して本発明の実施
形態を説明する。但し、この実施形態に記載されている
構成部品の寸法、材質、形状、その相対的配置等は特に
特定的な記載がないかぎりは、この発明の範囲をそれに
限定する趣旨ではなく、単なる説明例にすぎない。図1
は本発明の実施例に係る廃棄物の焼却熱を利用した過熱
蒸気製造装置を示し、図中、1は流動床からなる熱分解
炉で、多孔板等の分散板3−1上に流動砂等の流動媒体
2−1が収納されており、廃棄物供給ライン4及び砂循
環(戻入)ライン5より流動砂と都市ごみ等の廃棄物が
投入され、燃焼排ガス入口ライン6より供給された燃焼
排ガス等(本熱分解炉は基本的には燃焼ではなく熱分解
の為に、供給されるガスは酸素を消費した燃焼排ガスが
大部分であるが、温度制御を行なう為に必要に応じ空気
を僅かに入れる)により温度300℃以上の流動床空間
を生成し、廃棄物の熱分解反応を行なわせ、その反応に
より発生した熱分解ガスは熱分解ガス出口ライン7よ
り、又未分解残渣および流動砂から成るチャー混合物は
チャー混合物取り出しライン9より、不燃物は不燃物取
り出しライン8より、夫々互いに分離して取り出す。Embodiments of the present invention will be described below with reference to the drawings. However, the dimensions, materials, shapes, relative arrangements, and the like of the components described in this embodiment are not intended to limit the scope of the present invention unless otherwise specified, and are merely illustrative examples. It's just FIG.
1 shows a superheated steam production apparatus using the heat of incineration of waste according to an embodiment of the present invention. In the drawing, reference numeral 1 denotes a pyrolysis furnace comprising a fluidized bed, and And the like. Fluid medium and waste such as municipal solid waste are supplied from a waste supply line 4 and a sand circulation (return) line 5, and the combustion supplied from a combustion exhaust gas inlet line 6. Exhaust gas, etc. (This pyrolysis furnace is basically for the purpose of pyrolysis rather than combustion, so the supplied gas is mostly combustion exhaust gas that consumes oxygen. A small amount) to generate a fluidized bed space at a temperature of 300 ° C. or higher, and to cause a pyrolysis reaction of the waste. The pyrolysis gas generated by the reaction is supplied from a pyrolysis gas outlet line 7 to the undecomposed residue Char mixture consisting of sand removes the char mixture From line 9, incombustible than incombustible material withdrawal line 8, taken in isolation, respectively from each other.
【0029】この際熱分解ガスとチャー混合物の熱カロ
リー比が「約7(熱分解ガス):約3(チャー混合
物)」になるように熱分解を行うことが望ましい。これ
は、加温すべきボイラ水を100Kgf/cm2前後に
加圧した場合、沸点が309℃前後になる為に、熱分解
ガスでは水冷壁ボイラ36及び第1のボイラ24でボイ
ラ水を常温より「沸点309℃+蒸発潜熱」言換えれば
309℃で殆ど蒸気化するまで立上げるカロリーと、該
立上げた蒸気を沸点309℃より500℃まで立上げる
カロリーの比は、約7:3である事による。At this time, it is desirable to carry out the thermal decomposition so that the thermal calorie ratio of the pyrolysis gas and the char mixture becomes "about 7 (pyrolysis gas): about 3 (char mixture)". This is because when the boiler water to be heated is pressurized to about 100 kgf / cm 2 , the boiling point becomes about 309 ° C. Therefore, with the pyrolysis gas, the boiler water is cooled to room temperature by the water-cooled wall boiler 36 and the first boiler 24. More specifically, the ratio of the calorie that rises until almost vaporized at 309 ° C. and the calorie that rises the raised steam from 309 ° C. to 500 ° C. at about 309 ° C. is about 7: 3. It depends.
【0030】又熱分解炉1出口側の熱分解ガス出口ライ
ン7には空気入口ライン21Aが取付けられており、熱
分解炉1より取り出された熱分解ガスは、空気入口ライ
ン21より空気を導入して熱分解ガス中に含まれるター
ル等を一部燃焼させ、出口ライン7におけるタール付着
防止やコーキング防止を図ることも必要に応じて行う。
又前記出口ライン7の下流端には、燃焼ダクトからなる
熱分解ガス燃焼炉34が配設され、前記熱分解ガスに十
分なライン21’より空気を供給して該熱分解ガスの完
全燃焼を行う。An air inlet line 21 A is attached to the pyrolysis gas outlet line 7 on the outlet side of the pyrolysis furnace 1, and the pyrolysis gas extracted from the pyrolysis furnace 1 is introduced into the air through the air inlet line 21. If necessary, tar and the like contained in the pyrolysis gas are partially burned to prevent tar adhesion and caulking in the outlet line 7.
At the downstream end of the outlet line 7, a pyrolysis gas combustion furnace 34 composed of a combustion duct is provided, and sufficient air is supplied to the pyrolysis gas from a line 21 'to complete combustion of the pyrolysis gas. Do.
【0031】10は気泡流動床炉からなるチャー燃焼炉
で、底部に配した分散板11上にチャー混合物取り出し
ライン9より供給されたチャー混合物、及び砂循環ライ
ン19ー2/19−1を介して副チャー燃焼炉10Bと
の間で循環された流動砂が収納される。そして前記分散
板11下方の空気供給ライン12より空気が供給されて
流動床2−3内で700〜800℃に加熱して未分解残
渣の燃焼を行い、更にチャー燃焼炉10中域の空気供給
ライン13より空気が導入されて更に燃焼し約800〜
1300℃前後の燃焼ガスを生成すると共に、そのチャ
ー燃焼炉10中の上方域に第2スーパヒータ29−1を
配設し、第2の蒸気製造手段(第1スーパヒータ20)
よりライン28−1を介して導入された過熱蒸気の過熱
とともに、950〜1300℃前後と無用に高くなった
燃焼ガスを800〜950℃に落とす。尚前記のように
燃焼ガス温度を800〜950℃に落としても第1スー
パヒータ20における蒸気温度を200〜320℃に維
持する上で何の支障もない。そして前記チャー燃焼炉1
0で燃焼されない小型の不燃物は不燃物取り出しライン
14より取り出される。Reference numeral 10 denotes a char combustion furnace composed of a bubble fluidized bed furnace. The char mixture is supplied from a char mixture take-out line 9 onto a dispersion plate 11 disposed at the bottom of the char combustion furnace, and a sand circulation line 19-2 / 19-1. The fluidized sand circulated between the auxiliary char combustion furnace 10B is stored. Then, air is supplied from an air supply line 12 below the dispersion plate 11 and is heated to 700 to 800 ° C. in the fluidized bed 2-3 to burn undecomposed residues. Air is introduced from the line 13 and burns further to about 800-
A combustion gas of about 1300 ° C. is generated, and a second superheater 29-1 is disposed in an upper region of the char combustion furnace 10 to provide a second steam production means (first superheater 20).
Along with the superheating of the superheated steam introduced through the line 28-1, the combustion gas, which has become unnecessarily high around 950 to 1300 ° C, is dropped to 800 to 950 ° C. As described above, even if the combustion gas temperature is lowered to 800 to 950 ° C., there is no problem in maintaining the steam temperature in the first superheater 20 at 200 to 320 ° C. And the char combustion furnace 1
Small incombustibles that are not burned at 0 are taken out from the incombustibles take-out line 14.
【0032】一方、チャー燃焼炉10には副流動床とし
ての副チャー燃焼炉10Bが付設されており、図1及び
図2に示すように、砂循環ライン19ー2/19−1を
介して副チャー燃焼炉10Bとの間で流動砂が流動する
ように構成し、そして前記副チャー燃焼炉10Bの流動
媒体内に第3スーパヒータ29−2を配設し、第2スー
パヒータ29−1の出口側とライン28−2を介して接
続している。尚、副チャー燃焼炉10Bは図2に示すよ
うに、独立して設けてもよいが、図1に示すように、前
記チャー燃焼炉10より加熱された流動媒体を熱分解炉
1に戻入する流動媒体経路19−1/5中に、第3スー
パヒータ29−2を設けた副チャー燃焼炉10Bを介在
させるのがよい。On the other hand, the char combustion furnace 10 is provided with a sub-char combustion furnace 10B as a sub-fluidized bed, as shown in FIGS. 1 and 2, through a sand circulation line 19-2 / 19-1. Liquid sand is configured to flow between the auxiliary char combustion furnace 10B, and a third superheater 29-2 is disposed in the flowing medium of the auxiliary char combustion furnace 10B, and an outlet of the second superheater 29-1 is provided. Side and a line 28-2. The auxiliary char combustion furnace 10B may be provided independently as shown in FIG. 2, but the fluid medium heated from the char combustion furnace 10 is returned to the pyrolysis furnace 1 as shown in FIG. It is preferable to interpose a sub-char combustion furnace 10B provided with a third superheater 29-2 in the fluid medium path 19-1 / 5.
【0033】さて前記第2スーパヒータ29−1で熱交
換された燃焼ガスは、砂/燃焼ガス出口ライン15より
必要に応じて気・固分離装置例えばサイクロン16に導
入され、ここでダストや灰と燃焼ガスとを分離し、燃焼
ガスはガス出口ライン17より第1スーパヒータ20に
導入される。The combustion gas heat-exchanged by the second superheater 29-1 is introduced from a sand / combustion gas outlet line 15 to a gas / solid separation device, for example, a cyclone 16, as required, where the dust and ash are removed. The combustion gas is separated from the combustion gas, and the combustion gas is introduced into the first superheater 20 through the gas outlet line 17.
【0034】20は第1スーパヒータ及び24は第1ボ
イラで、第1ボイラ24では熱分解ガス出口ライン7よ
り取り出された熱分解ガスは、水冷壁ボイラ36が内装
されている燃焼ガス燃焼炉34内で燃焼されて第1スー
パヒータ20のボイラガス出口22より排出された燃焼
排ガスと共に、第1のボイラ24に導入され、ボイラ水
入口26より取込んだボイラ水を300℃前後に加熱
し、第1ボイラ出口ライン27より第1スーパヒータ2
0に蒸気若しくは加熱水を供給する。Reference numeral 20 denotes a first superheater and reference numeral 24 denotes a first boiler. In the first boiler 24, the pyrolysis gas extracted from the pyrolysis gas outlet line 7 is supplied to a combustion gas combustion furnace 34 in which a water-cooled wall boiler 36 is installed. The boiler water introduced into the first boiler 24 and taken in from the boiler water inlet 26 together with the combustion exhaust gas discharged from the boiler gas outlet 22 of the first superheater 20 through the boiler gas outlet 22 is heated to about 300 ° C. 1st superheater 2 from boiler outlet line 27
Supply steam or heated water to zero.
【0035】ボイラ水は分岐ライン26’を介して燃焼
ガス燃焼炉34内の水冷壁ボイラ36にも導入され分岐
ライン27’を介して第1スーパヒータ20に蒸気若し
くは加熱水を供給する。尚、100Kgf/cm2前後
に加圧してその沸点を309℃前後に設定している前記
ボイラ水は水冷壁ボイラ36及び第1のボイラ24に導
入されて第1段階の加熱を行うわけであるが、その加熱
温度が前記沸点近くの309℃前後になるようにその通
水量を制御している。The boiler water is also introduced into a water wall boiler 36 in a combustion gas combustion furnace 34 through a branch line 26 ', and supplies steam or heated water to the first superheater 20 through a branch line 27'. The boiler water, which is pressurized to about 100 kgf / cm 2 and its boiling point is set at about 309 ° C., is introduced into the water-cooled wall boiler 36 and the first boiler 24 to perform the first-stage heating. However, the flow rate of water is controlled so that the heating temperature is about 309 ° C., which is near the boiling point.
【0036】この結果、水冷壁ボイラ36及び第1のボ
イラ24のチューブ表面壁温度は、前記加温水に追従し
て350以下に維持でき、例え熱交換される熱分解ガス
に塩素若しくはHClを含んでいても腐食が生じる事は
ない。As a result, the tube surface wall temperature of the water-cooled wall boiler 36 and the first boiler 24 can be maintained at 350 or less following the heated water, and for example, the heat-exchanged pyrolysis gas contains chlorine or HCl. No corrosion will occur.
【0037】第1スーパヒータ20では前記第1ボイラ
24及び水冷壁ボイラ36の出口ライン27、27’よ
り取り出した蒸気/加熱水及び水冷壁ボイラ36により
加熱され分岐蒸気ライン27’を介してとりだされた蒸
気/加熱水を導入して、前記燃焼ガスライン17を介し
て供給された燃焼ガスで加熱し、過熱蒸気を製造し、以
下蒸気出口ライン28ー1より第2スーパヒータ29−
1に、更にライン28ー2より第3スーパヒータ29−
2に夫々直列に導入して400〜520℃に過熱された
過熱蒸気を取り出し、発電機に送給する。In the first superheater 20, steam / heated water taken out from the outlet lines 27 and 27 'of the first boiler 24 and the water-cooled wall boiler 36, and heated by the water-cooled wall boiler 36 and taken out through a branch steam line 27'. The heated steam / heated water is introduced and heated by the combustion gas supplied through the combustion gas line 17 to produce superheated steam.
1 and a third superheater 29- from line 28-2.
The superheated steam which is introduced in series into each of 2 and superheated to 400 to 520 ° C. is taken out and sent to the generator.
【0038】既に前記実施例の作用は構成とともに、説
明したが簡単に繰返し説明するに、熱分解炉1に供給さ
れる都市ごみ等の廃棄物中には塩ビプラスチック等の含
塩素有機化合物が混入しており、可燃分中にClとして
約0.2〜0.5%含有されている。そして、廃棄物供
給ライン4から都市ごみ、流動砂循環ライン5から高温
の循環流動砂を、それぞれ熱分解炉1に供給し、下部の
空気または燃焼排ガス入口ライン6から燃焼排ガスに僅
かな温度調整用空気を供給して流動砂2−1を流動させ
た流動床内で、温度350〜500℃で処理することに
より、チャー混合物取り出しライン9からは実質的に塩
素を含有しない未分解残渣が得られる。すなわち、廃棄
物中に含まれていた塩素は、実質的に全て熱分解ガスに
含まれて、熱分解ガス出口ライン7に排出されることに
なる。なお、熱分解炉1内の熱分解反応で分離された大
型の不燃物は、不燃物取り出しライン8から炉外に取り
出される。この際前記熱分解ガスとチャー混合物の熱カ
ロリ比が7:3になるように熱分解時間と熱分解温度を
設定する。Although the operation of the above embodiment has been described together with the configuration, the explanation will be briefly repeated. A chlorine-containing organic compound such as PVC plastic is mixed in the waste such as municipal solid waste supplied to the pyrolysis furnace 1. It contains about 0.2 to 0.5% as Cl in combustibles. Then, municipal solid waste from the waste supply line 4 and high-temperature circulating fluidized sand from the fluidized sand circulation line 5 are supplied to the pyrolysis furnace 1, respectively, and the temperature is slightly adjusted to the combustion air from the lower air or the combustion exhaust gas inlet line 6. By treating at a temperature of 350 to 500 ° C. in a fluidized bed in which the fluidized sand 2-1 is fluidized by supplying air for use, an undecomposed residue substantially free of chlorine is obtained from the char mixture removal line 9. Can be That is, substantially all of the chlorine contained in the waste is contained in the pyrolysis gas and discharged to the pyrolysis gas outlet line 7. The large-sized incombustibles separated by the thermal decomposition reaction in the thermal decomposition furnace 1 are taken out of the furnace through an incombustibles take-out line 8. At this time, the pyrolysis time and the pyrolysis temperature are set so that the thermal calorie ratio of the pyrolysis gas and the char mixture becomes 7: 3.
【0039】熱分解炉1の熱分解出口ライン7から取り
出された上記熱分解ガスには、ガス、油分、タールおよ
びHClが含まれているが、これらの熱分解炉1の空気
入口ライン21から供給される空気で予備燃焼させて温
度の低下を防止させ、出口ライン7におけるタール付着
防止やコーキング防止と共に、ライン21’より更に空
気を熱分解燃焼炉34に導入して該熱分解燃焼炉34内
で完全燃焼を行う。この結果熱分解燃焼炉34内の熱分
解ガス温度を高く設定できるために、水冷壁ボイラ36
−1、36−2及び第一ボイラ24に導入され沸点20
0〜320℃近くまで立上げる蒸気/ボイラ水を多量に
製造できる。The pyrolysis gas extracted from the pyrolysis outlet line 7 of the pyrolysis furnace 1 contains gas, oil, tar, and HCl. Preliminary combustion is performed with the supplied air to prevent the temperature from lowering, while preventing tar adhesion and coking at the outlet line 7 and introducing air into the pyrolysis combustion furnace 34 further from the line 21 ′. Perform complete combustion within. As a result, since the temperature of the pyrolysis gas in the pyrolysis combustion furnace 34 can be set high, the water-cooled wall boiler 36
-1, 36-2 and a boiling point of 20 introduced into the first boiler 24
It is possible to produce a large amount of steam / boiler water which rises to about 0 to 320 ° C.
【0040】又熱分解燃焼炉34内で水冷壁ボイラ36
−1と熱交換した熱分解燃焼排ガスは、第1スーパヒー
タボイラガス出口ライン22よりの燃焼排ガスとともに
第1ボイラガス入口23から第1ボイラ24に供給す
る。前記熱分解燃焼炉34内及び第1ボイラ24内に導
入されるガスにはHClが約500〜1000ppm含ま
れているので、ボイラ水の流量を調整して水冷壁ボイラ
36及び第1ボイラ24のチューブ表面温度は従来並み
の約350℃以下として、高温腐食を抑制する。このた
め、水冷壁ボイラ36−1、36−2及び第1ボイラ2
4では高温の過熱蒸気は得られないが、約300〜32
0℃までは加熱できるので、これを更に第1スーパヒー
タ20以降のスーパヒータ29−1、29−2で加熱す
れば、約500〜700℃の高温の過熱蒸気を得ること
ができる。The water-cooled wall boiler 36 in the pyrolysis combustion furnace 34
-1 is supplied to the first boiler 24 from the first boiler gas inlet 23 together with the flue gas from the first superheater boiler gas outlet line 22. Since the gas introduced into the pyrolysis combustion furnace 34 and the first boiler 24 contains about 500 to 1000 ppm of HCl, the flow rate of the boiler water is adjusted to adjust the water cooling wall boiler 36 and the first boiler 24. The surface temperature of the tube is set to about 350 ° C. or less, which is the same as the conventional one, to suppress high temperature corrosion. For this reason, the water-cooled wall boilers 36-1, 36-2 and the first boiler 2
In No. 4, high temperature superheated steam cannot be obtained, but about 300 to 32
Since it can be heated to 0 ° C., if it is further heated by the super heaters 29-1 and 29-2 after the first super heater 20, a high-temperature superheated steam of about 500 to 700 ° C. can be obtained.
【0041】熱分解炉1でチャー混合物取り出しライン
9から取り出されたチャー混合物は流動砂と未分解残渣
から成り、実質的に塩素を含有しないチャー混合物を、
燃焼炉10では燃焼炉10の下部に供給し、空気供給ラ
イン12から分散板11を介して供給される空気によっ
て燃焼させる。この場合、空気供給ライン12から供給
する空気量を調整して、流動砂を流動させながら未分解
残渣を燃焼させる。完全燃焼のために空気供給ライン1
3及び19−3から更に空気を供給することもある。燃
焼炉10の温度は燃焼発熱反応によって上昇する。この
温度値は、チャー混合物取り出しライン9から供給され
る未分解残渣の発熱量と空気供給ライン12、13の空
気および砂循環ライン19−1、19−2の流動砂の量
と温度によって決まるが、1000〜1200℃前後の
高温になる場合がある。The char mixture taken out from the char mixture take-out line 9 in the pyrolysis furnace 1 is composed of fluidized sand and uncracked residue, and is substantially free of chlorine.
In the combustion furnace 10, the air is supplied to a lower part of the combustion furnace 10 and is burned by air supplied from an air supply line 12 through a dispersion plate 11. In this case, the amount of air supplied from the air supply line 12 is adjusted, and the undecomposed residue is burned while flowing the fluidized sand. Air supply line 1 for complete combustion
Further air may be supplied from 3 and 19-3. The temperature of the combustion furnace 10 rises due to a combustion exothermic reaction. This temperature value is determined by the calorific value of the undecomposed residue supplied from the char mixture removal line 9, the amount of air in the air supply lines 12, 13 and the amount and temperature of the fluidized sand in the sand circulation lines 19-1, 19-2. , 1000 to 1200 ° C.
【0042】そこで第2スーパヒータ29ー1によりラ
イン28ー1を介して第1スーパヒータ20よりの過熱
蒸気と熱交換することにより燃焼ガスを800〜950
℃にすることは容易である。尚必要に応じ第1スーパヒ
ータ20の代りに又は第1スーパヒータ20とともにラ
イン26、27を分岐したライン26”、27”により
循環されるボイラ水の加熱を行う水冷壁ボイラ36−2
を設けてもよい。又ガラスや缶類等の溶融により小型化
された不燃物は不燃物取り出しライン14から抜き出
す。Then, the second superheater 29-1 exchanges heat with the superheated steam from the first superheater 20 via the line 28-1 to reduce the combustion gas to 800 to 950.
It is easy to reach ° C. A water-cooled wall boiler 36-2 for heating the boiler water circulated by the lines 26 ", 27" branching off the lines 26, 27 instead of the first superheater 20 or together with the first superheater 20 as necessary.
May be provided. Incombustibles that have been miniaturized by melting glass, cans and the like are extracted from the incombustibles take-out line 14.
【0043】尚、副チャー燃焼炉10Bは図2に示すよ
うに、独立して設けてもよいが、前記チャー燃焼炉10
の流動媒体は熱分解炉1との間を循環する為、チャー燃
焼炉10の流動媒体の温度は略700〜850℃、一方
熱分解炉1の流動媒体の温度は350〜400℃であ
り、両者間の熱落差が大きく、この為チャー燃焼炉10
の流動媒体を熱分解炉1側に直接導入すると、前記熱落
差により熱分解炉1内の熱分解温度が高くなったり熱変
動が生じる恐れがあり、従って前記戻入される流動媒体
の量の調整が煩雑化する。The sub-char combustion furnace 10B may be provided independently as shown in FIG.
Is circulated between the thermal decomposition furnace 1 and the temperature of the fluid medium of the char combustion furnace 10 is approximately 700 to 850 ° C., while the temperature of the fluid medium of the thermal decomposition furnace 1 is 350 to 400 ° C. Since the heat drop between the two is large, the char combustion furnace 10
If the fluid medium is directly introduced into the pyrolysis furnace 1, the thermal head may increase the pyrolysis temperature or cause thermal fluctuations in the pyrolysis furnace 1, and therefore, adjust the amount of the fluid medium returned. Is complicated.
【0044】そこで図1にしめすように、前記チャー燃
焼炉10より加熱された流動媒体を熱分解炉1に戻入す
る流動媒体経路19−1/5中に、第3スーパヒータ2
9−2を設けた副チャー燃焼炉10Bを介在させること
により、第1のチャー燃焼炉10で700〜800℃に
加熱した流動媒体を、前記副チャー燃焼炉10Bで第3
スーパヒータ29−2による奪熱により500〜700
℃に落とし、該500〜700℃に落とした流動媒体を
熱分解炉1に戻入する事が出来るためになだらかな熱傾
斜が可能であり、この結果前記熱分解炉1内の熱分解温
度を350℃から500℃前後に安定して制御が可能で
ある。28−3は過熱蒸気取り出しライン、12’は空
気供給ラインである。Therefore, as shown in FIG. 1, the third superheater 2 is provided in the flowing medium path 19- / for returning the flowing medium heated from the char combustion furnace 10 to the pyrolysis furnace 1.
By interposing the sub-char combustion furnace 10B provided with 9-2, the fluid medium heated to 700 to 800 ° C. in the first char combustion furnace 10
500-700 due to heat removal by super heater 29-2
C., and the fluid medium dropped to 500 to 700 ° C. can be returned to the pyrolysis furnace 1, so that a gentle thermal gradient is possible. As a result, the pyrolysis temperature in the pyrolysis furnace 1 is reduced to 350 ° C. It is possible to stably control the temperature from about 500C to about 500C. 28-3 is a superheated steam take-out line, and 12 'is an air supply line.
【0045】一方チャー燃焼炉10で生成し800〜9
50℃の高温でかつ塩素を実質的に含有しない燃焼ガス
は燃焼ガス出口ライン15を経て必要に応じサイクロン
16に導入され、ダスト及び灰は出口ライン18から、
排ガスはガス出口ライン17からそれぞれ分離して取り
出される。On the other hand, 800-9
Combustion gas at a high temperature of 50 ° C. and substantially free of chlorine is introduced into a cyclone 16 as needed via a combustion gas outlet line 15, and dust and ash are discharged from an outlet line 18.
The exhaust gas is separated and taken out from each of the gas outlet lines 17.
【0046】一方、上記サイクロン16のガス出口ライ
ン17から取り出された800〜950℃の高温排ガス
は、第1スーパヒータ20に導入され、第1ボイラ24
及び水冷壁ボイラ36で製造された200〜320℃前
後の蒸気/ボイラ水を加熱して過熱蒸気とするために用
いられる。ガス出口ライン17を経て来た排ガスは実質
的に塩素を含有していないので、第1スーパヒータ20
のボイラチューブ表面温度を350℃以上としても高温
腐食は大幅に軽減される。したがってチューブ内流体の
温度を約400〜520℃とすることができ、第1スー
パヒータボイラ蒸気出口28−1からは安定して高温の
過熱蒸気が得られる。On the other hand, the high temperature exhaust gas of 800 to 950 ° C. taken out of the gas outlet line 17 of the cyclone 16 is introduced into the first superheater 20 and the first boiler 24
And it is used for heating steam / boiler water at about 200 to 320 ° C. produced by the water-cooled wall boiler 36 to produce superheated steam. Since the exhaust gas passing through the gas outlet line 17 does not substantially contain chlorine, the first superheater 20
Even when the surface temperature of the boiler tube is set to 350 ° C. or higher, high-temperature corrosion is greatly reduced. Therefore, the temperature of the fluid in the tube can be set to about 400 to 520 ° C., and high-temperature superheated steam can be stably obtained from the first superheater boiler steam outlet 28-1.
【0047】前記熱分解炉1で熱分解炉1の温度を所定
温度300℃以上に維持するには、燃焼排ガス入口ライ
ン6から供給される流動気体の酸素量を調節、言換えれ
ば第1ボイラ24よりの燃焼排ガスとともに空気を僅か
に供給するとともに、副チャー燃焼手段10Bよりの高
温約500〜700℃の流動砂の一部を砂循環ライン5
から供給して熱源としている。In order to maintain the temperature of the pyrolysis furnace 1 at a predetermined temperature of 300 ° C. or higher in the pyrolysis furnace 1, the amount of oxygen in the flowing gas supplied from the flue gas inlet line 6 is adjusted, in other words, the first boiler A small amount of air is supplied together with the combustion exhaust gas from the combustion chamber 24, and a part of the fluidized sand at a high temperature of about 500 to 700 ° C.
And heat source.
【0048】例えば燃焼排ガス入口ライン6より熱分解
炉1に供給される空気または燃焼排ガスは、350〜5
00℃の範囲で熱分解を効率的に行うために、酸素の少
ない(3〜5%程度)且つ温度が150〜200℃の温
度を維持している燃焼排ガス、具体的には第1のボイラ
24の出口ライン25より取り出された燃焼排ガスを用
いるのが良い。尚、各図において11、3−1、3−2
は分散板、2−1、2−2、2−3は流動床である。For example, air or combustion exhaust gas supplied to the pyrolysis furnace 1 from the combustion exhaust gas inlet line 6 is 350 to 5
In order to efficiently perform pyrolysis in the range of 00 ° C, a combustion exhaust gas containing a small amount of oxygen (about 3 to 5%) and maintaining a temperature of 150 to 200 ° C, specifically, a first boiler It is preferable to use the combustion exhaust gas taken out from the 24 outlet lines 25. In addition, in each figure, 11, 3-1, 3-2
Denotes a dispersion plate, and 2-1 and 2-2 and 2-3 denote fluidized beds.
【0049】さて図4は本発明の他の実施例に係る廃棄
物の焼却熱を利用した過熱蒸気製造装置を示し前記図1
の実施例との相違点を説明するに、前記熱分解炉の不燃
物取りだしライン8には5mm程度の網径を有する振動
篩等の第1のフィルタ291を設け、前記ライン8より
排出された排出物について大型不燃物と他の排出物を分
離し、他の排出物をライン50及びライン54を介し
て、チャー燃焼炉10の分散板11上方の流動床底部側
に給送するように構成している。51は大型不燃物取り
出しラインである。FIG. 4 shows an apparatus for producing superheated steam using the heat of incineration of waste according to another embodiment of the present invention.
In order to explain the difference from this embodiment, a first filter 291 such as a vibrating sieve having a mesh diameter of about 5 mm is provided in the incombustibles removal line 8 of the pyrolysis furnace, and the first filter 291 is discharged from the line 8. It is configured to separate large incombustibles and other effluents from the effluent, and feed the other effluent to the bottom of the fluidized bed above the dispersion plate 11 of the char combustion furnace 10 via the lines 50 and 54. are doing. Reference numeral 51 denotes a large incombustible substance take-out line.
【0050】一方チャー燃焼炉10で燃焼されない小型
の不燃物等は不燃物取り出しライン14より取り出され
る。前記不燃物取り出しライン14には網目が2mm前
後の第2フィルタ292が介装され、前記ライン14よ
り排出された排出物について小型不燃物と流動砂・灰分
とを分離し、流動砂をライン52、第3フィルタ29
3、ライン55及び54を介してチャー燃焼炉10の分
散板11上方の流動床底部側に給送するように構成して
いる。小型不燃物についてはライン53より外部に排出
される。On the other hand, small incombustibles and the like that are not burned in the char combustion furnace 10 are taken out from the incombustibles take-out line 14. A second filter 292 having a mesh of about 2 mm is interposed in the incombustibles removal line 14 to separate small incombustibles from fluidized sand and ash from the discharged material from the line 14, and to remove fluidized sand into a line 52. , The third filter 29
3. It is configured to feed to the fluidized bed bottom side above the dispersion plate 11 of the char combustion furnace 10 via lines 55 and 54. The small incombustibles are discharged from the line 53 to the outside.
【0051】第3フィルタ293では、必ずしも必要と
するものではないが、第2フィルタ292で補足されな
かった流動砂を補足しながら灰分のみを外部に排出する
もので、その網目は最小径(約0.2mm)より小さい
0.1mm前後に設定する。これにより第3フィルタ2
93で、第2フィルタ292で補足されなかった流動砂
を補足しながら灰分のみをライン56を介して外部に排
出する事ができ、これにより効率的な灰分除去と流動砂
の回収が容易になる。The third filter 293 is not necessarily required, but discharges only the ash to the outside while supplementing the fluidized sand not captured by the second filter 292. 0.2 mm), which is set to about 0.1 mm. Thereby, the third filter 2
At 93, only the ash can be discharged to the outside via the line 56 while supplementing the fluid sand not captured by the second filter 292, thereby facilitating efficient ash removal and recovery of the fluid sand. .
【0052】次に前記実施例の作用について詳述する。
熱分解炉1内の熱分解反応で分離された大型の不燃物
は、不燃物取り出しライン8から炉外に取り出される。
廃棄物として一般に約200mm程度の廃棄物が前記熱
分解炉1に投入されるが、このため前記熱分解炉8の不
燃物取りだしライン8の径をある程度大きくせねばなら
ず、この為前記取りだしライン8より大型の不燃物の他
にチャー残査や流動砂、更には小型の不燃物が取り出さ
れる。そこで熱分解炉1の不燃物取りだしライン8より
排出された排出物について前記第1のフィルタ291に
より、大型不燃物と他の排出物を分離し、大型の不燃物
のみ排出させ、そして他の排出物についてはチャー燃焼
炉10底部側に給送し燃焼の用に供する事が出来る。Next, the operation of the above embodiment will be described in detail.
The large-sized incombustibles separated by the thermal decomposition reaction in the thermal decomposition furnace 1 are taken out of the furnace through an incombustibles take-out line 8.
Generally, about 200 mm of waste is introduced into the pyrolysis furnace 1 as waste. For this reason, the diameter of the non-combustible material take-out line 8 of the pyrolysis furnace 8 must be increased to some extent. In addition to non-combustible materials larger than 8, char residue, fluidized sand, and small non-combustible materials are taken out. Therefore, the first filter 291 separates large-sized incombustibles from other exhausts from the incombustibles take-out line 8 of the pyrolysis furnace 1 and discharges only large-sized incombustibles. The material can be fed to the bottom side of the char combustion furnace 10 and used for combustion.
【0053】チャー燃焼炉10ではガラス片や鉄くず等
の小型化された不燃物は不燃物取り出しライン14から
抜き出す。一方前記チャー燃焼炉10には既に大型の不
燃物が除去されているために、又チャー残査も十分燃焼
されているために、不燃物取りだしライン14より排出
された排出物については小型不燃物と流動砂のみを第2
のフィルタ292及び第3フィルタ293で分離すれば
よく、これにより分離された流動砂をライン52/55
/54を介して燃焼炉10の流動床底部側に給送すれば
流動砂のみの循環再使用が可能となる。In the char combustion furnace 10, miniaturized incombustible substances such as glass fragments and iron swarf are extracted from an incombustible substance extraction line 14. On the other hand, since the large incombustibles have already been removed from the char combustion furnace 10 and the char residue has been sufficiently burned, the exhaust discharged from the incombustibles removal line 14 is small incombustibles. And second only liquid sand
And the liquid sand separated by the filter 292 and the third filter 293.
By feeding the fluidized sand to the bottom side of the fluidized bed of the combustion furnace 10 via / 54, only the fluidized sand can be circulated and reused.
【0054】[0054]
【発明の効果】以上記載した如く本発明によれば、高価
な高級材料を用いることなく廃棄物を燃焼して過熱蒸気
を得る場合に塩素によるボイラチューブの高温腐食を防
止しながら高温・高圧の過熱蒸気を効率的に得ることの
できる。本発明によれば廃棄物の熱分解手段とチャー燃
焼手段における不燃物の除去と流動媒体の分離を更に効
率良く行い、安定した熱分解とチャー燃焼を行うことが
出来る。等の種々の著効を有す。As described above, according to the present invention, when waste is burned to obtain superheated steam without using expensive high-grade materials, it is possible to prevent high-temperature corrosion of the boiler tube by chlorine while preventing high-temperature and high-pressure corrosion. Superheated steam can be obtained efficiently. ADVANTAGE OF THE INVENTION According to this invention, the removal of incombustible substances and the separation of the fluid medium in the waste pyrolysis means and the char combustion means can be performed more efficiently, and stable pyrolysis and char combustion can be performed. And so on.
【図1】本発明の第1実施例に係る廃棄物の焼却熱を利
用した過熱蒸気製造装置を示す系統図である。FIG. 1 is a system diagram showing an apparatus for producing superheated steam using heat of waste incineration according to a first embodiment of the present invention.
【図2】本発明の第2実施例に係る廃棄物の焼却熱を利
用した過熱蒸気製造装置を示す系統図である。FIG. 2 is a system diagram showing an apparatus for producing superheated steam using waste heat of incineration according to a second embodiment of the present invention.
【図3】本発明の基本構成に係る廃棄物の焼却熱を利用
した過熱蒸気の製造手順を示すグラフ図である。FIG. 3 is a graph showing a procedure for producing superheated steam using the heat of incineration of waste according to the basic configuration of the present invention.
【図4】本発明の第2実施例に係る廃棄物の焼却熱を利
用した過熱蒸気製造装置を示す系統図である。FIG. 4 is a system diagram showing a superheated steam production apparatus using waste heat of incineration according to a second embodiment of the present invention.
【符号の説明】 1 熱分解炉(熱分解手段) 10 燃焼炉(チャー燃焼手段) 11 分散板 20 第1スーパヒータ(第2の蒸気製造手段) 29−1 第2スーパヒータ(第2の蒸気製造手段) 20−2 第3スーパヒータ(第2の蒸気製造手段) 24 第1ボイラ(第1の蒸気製造手段) 34 熱分解ガス燃焼炉 36 水冷壁ボイラ(第1の蒸気製造手段) 31 灰溶融炉 291 第1のフィルタ手段 292 第2のフィルタ手段[Description of Signs] 1 Pyrolysis furnace (pyrolysis means) 10 Combustion furnace (char combustion means) 11 Dispersion plate 20 First superheater (second steam production means) 29-1 Second superheater (second steam production means) 20-2 Third superheater (second steam producing means) 24 First boiler (first steam producing means) 34 Pyrolysis gas combustion furnace 36 Water-cooled wall boiler (first steam producing means) 31 Ash melting furnace 291 First filter means 292 Second filter means
───────────────────────────────────────────────────── フロントページの続き (51)Int.Cl.7 識別記号 FI F23G 5/30 ZAB F23G 5/30 ZABH (72)発明者 保田 静生 横浜市中区錦町12番地 三菱重工業株式 会社横浜製作所内 (72)発明者 貝原 裕二 横浜市中区錦町12番地 三菱重工業株式 会社横浜製作所内 (56)参考文献 特開 平5−346204(JP,A) 特開 昭58−95104(JP,A) (58)調査した分野(Int.Cl.7,DB名) F23G 5/48 F22B 1/18 F22G 1/16 F23G 5/027 F23G 5/30 ──────────────────────────────────────────────────続 き Continued on the front page (51) Int.Cl. 7 Identification code FI F23G 5/30 ZAB F23G 5/30 ZABH (72) Inventor Shizuo Yasuda 12 Nishikicho, Naka-ku, Yokohama-shi Mitsubishi Heavy Industries, Ltd. (72) Inventor Yuji Kaihara 12 Nishikicho, Naka-ku, Yokohama-shi Yokohama Heavy Industries, Ltd. (56) References JP-A-5-346204 (JP, A) JP-A-58-95104 (JP, A) (58) ) Surveyed field (Int.Cl. 7 , DB name) F23G 5/48 F22B 1/18 F22G 1/16 F23G 5/027 F23G 5/30
Claims (5)
給して熱分解反応を行なわせ、その反応により発生した
熱分解ガスと未分解残渣および流動媒体から成るチャー
混合物と不燃物とを互いに分離する熱分解手段と、 前記熱分解手段より取り出された未分解残渣および流動
媒体から成るチャー混合物を、空気によって流動させな
がら前記未分解残渣を燃焼させるチャー燃焼手段と、 前記熱分解ガスの燃焼熱エネルギーを利用して約400
℃以下の温水または蒸気を製造する第1の蒸気製造手段
と、 前記チャー燃焼手段により得られた熱エネルギにより前
記第1の蒸気製造手段で製造された温水または蒸気を過
熱蒸気とする第2の蒸気製造手段を含み、 前記チャー燃焼手段より加熱された流動媒体の循環経路
中に第2のチャー燃焼手段を介在させ、該第2のチャー
燃焼手段の燃焼媒体中に、前記第1若しくは第2の蒸気
製造手段を設けたことを特徴とする廃棄物の焼却熱を利
用した過熱蒸気製造装置。 (1)Provide waste in a space with a temperature of 300 ° C or higher.
To cause the thermal decomposition reaction, which is generated by the reaction
Char consisting of pyrolysis gas, uncracked residue and flowing medium
Pyrolysis means for separating the mixture and incombustibles from each other, Undecomposed residue and fluid removed from the pyrolysis means
Do not allow the char mixture consisting of the medium to flow with air.
Char burning means for burning the undecomposed residue, Approximately 400 using the combustion heat energy of the pyrolysis gas
First steam production means for producing hot water or steam at a temperature of not more than ℃
When, The heat energy obtained by the char combustion means causes
The hot water or steam produced by the first steam production means
A second steam producing means for producing hot steam, Circulation path of fluid medium heated by the char combustion means
A second char combustion means interposed therein, and the second char
The first or second steam in the combustion medium of the combustion means;
Utilizes the heat of incineration of waste, characterized by the provision of manufacturing means.
Superheated steam production equipment used.
加熱された蒸気若しくは前記いずれかの製造手段に導入
される温水若しくは蒸気の一部を、前記チャー燃焼手段
の高温域側に配した熱交換手段に導入して、該蒸気を加
熱することを特徴とすることを特徴とする請求項1記載
の廃棄物の焼却熱を利用した過熱蒸気製造装置。 2. The method according to claim 1, wherein the first or second steam producing means is used.
Introduced into heated steam or any of the above manufacturing means
A portion of the hot water or steam that is
Into the heat exchange means located on the high temperature side of the
2. The method according to claim 1, wherein the heating is performed.
Superheated steam production equipment using the heat of incineration of waste.
給して熱分解反応を行なわせ、その反応により発生した
熱分解ガスと未分解残渣および流動媒体から成るチャー
混合物と不燃物とを互いに分離する熱分解手段と、 前記熱分解手段より取り出された未分解残渣および流動
媒体から成るチャー混合物を、空気によって流動させな
がら前記未分解残渣を燃焼させるチャー燃焼手段と、 前記熱分解ガスの燃焼熱エネルギーを利用して約400
℃以下の温水または蒸気を製造する第1の蒸気製造手段
と、 前記チャー燃焼手段により得られた熱エネルギにより前
記第1の蒸気製造手段 で製造された温水または蒸気を過
熱蒸気とする第2の蒸気製造手段を含み、 前記チャー燃焼手段より加熱された流動媒体を熱分解手
段に戻入する流動媒体経路中に、熱交換手段等からなる
熱落差緩和手段を設けた第2のチャー燃焼手段を介在さ
せたことを特徴とする廃棄物の焼却熱を利用した過熱蒸
気製造装置。 (3)Provide waste in a space with a temperature of 300 ° C or higher.
To cause the thermal decomposition reaction, which is generated by the reaction
Char consisting of pyrolysis gas, uncracked residue and flowing medium
Pyrolysis means for separating the mixture and incombustibles from each other, Undecomposed residue and fluid removed from the pyrolysis means
Do not allow the char mixture consisting of the medium to flow with air.
Char burning means for burning the undecomposed residue, Approximately 400 using the combustion heat energy of the pyrolysis gas
First steam production means for producing hot water or steam at a temperature of not more than ℃
When, The heat energy obtained by the char combustion means causes
First steam production means Through the hot water or steam produced in
A second steam producing means for producing hot steam, The fluid medium heated by the char combustion means is thermally decomposed.
In the fluidized medium path returning to the stage, consist of heat exchange means etc.
The second char combustion means provided with the thermal head mitigation means is interposed.
Superheated steam using the heat of incineration of waste
Qi production equipment.
加熱された蒸気若しくは前記いずれかの製造手段に導入
される温水若しくは蒸気の一部を、前記チャー燃焼手段
の高温域側に配した熱交換手段に導入して、該蒸気を加
熱することを特徴とする請求項3記載の廃棄物の焼却熱
を利用した過熱蒸気製造装置。4. The steam heated by the first or second steam producing means or a portion of hot water or steam introduced into any one of the producing means is disposed on a high temperature side of the char combustion means. The steam is introduced into the heat exchange means and
The apparatus for producing superheated steam using waste incineration heat according to claim 3, wherein the apparatus is heated.
給して熱分解反応を行なわせ、その反応により発生した
熱分解ガスと未分解残渣および流動媒体から成るチャー
混合物と不燃物とを互いに分離する熱分解手段と、 前記熱分解手段より取り出された未分解残渣および流動
媒体から成るチャー混合物を、空気によって流動させな
がら前記未分解残渣を燃焼させるチャー燃焼手段と、 前記熱分解手段の不燃物取りだし口より排出された排出
物について大型不燃物と他の排出物を分離し、他の排出
物をチャー燃焼手段底部側に給送する第1のフィルタ手
段と、 前記燃焼手段の不燃物取りだし口より排出された排出物
について小型不燃物と流動媒体とを分離し、流動媒体を
チャー燃焼手段底部側に給送する第2のフィルタ手段を
設け、 更に必要に応じて前記第2のフィルタ手段の出口側に、
灰分を分離し、灰分分離後の流動媒体をチャー燃焼手段
底部側に給送する第3のフィルタ手段と、 を設けたことを特徴とする廃棄物の焼却熱を利用した過
熱蒸気製造装置。 Claim 5.Provide waste in a space with a temperature of 300 ° C or higher.
To cause the thermal decomposition reaction, which is generated by the reaction
Char consisting of pyrolysis gas, uncracked residue and flowing medium
Pyrolysis means for separating the mixture and incombustibles from each other, Undecomposed residue and fluid removed from the pyrolysis means
Do not allow the char mixture consisting of the medium to flow with air.
Char burning means for burning the undecomposed residue, Emissions discharged from the incombustibles outlet of the pyrolysis means
Separation of large incombustibles and other emissions from materials and other emissions
A first filter hand for feeding material to the bottom side of the char combustion means
Steps and Emissions discharged from the incombustible material outlet of the combustion means
About the small incombustibles and the fluid medium,
A second filter means for feeding to the bottom side of the char combustion means;
Provided, Further, if necessary, on the outlet side of the second filter means,
Separates the ash and uses the fluid medium after the ash separation as char combustion means.
Third filter means for feeding to the bottom side; The use of waste incineration heat
Hot steam production equipment.
Priority Applications (7)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP06906796A JP3276286B2 (en) | 1996-02-29 | 1996-02-29 | Superheated steam production equipment using waste incineration heat |
| EP97903617A EP0823590B1 (en) | 1996-02-29 | 1997-02-27 | Method and apparatus for producing superheated steam using heat generated through incineration of wastes |
| PCT/JP1997/000573 WO1997032161A1 (en) | 1996-02-29 | 1997-02-27 | Method and apparatus for producing superheated steam using heat generated through incineration of wastes |
| KR1019970707702A KR100264723B1 (en) | 1996-02-29 | 1997-02-27 | Method and apparatus for producing superheated steam using heat generated through incineration of wastes |
| US08/945,591 US6133499A (en) | 1996-02-29 | 1997-02-27 | Method and apparatus for producing superheated steam using heat from the incineration of waste material |
| DE69732394T DE69732394T2 (en) | 1996-02-29 | 1997-02-27 | METHOD AND DEVICE FOR PRODUCTION OF OVERHEATED STEAM BY THE HEAT OF WASTE INCINERATION |
| SG9904761A SG96183A1 (en) | 1996-02-29 | 1997-02-27 | Method and apparatus for producing superheated steam using heat from the incineration of waste material |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP06906796A JP3276286B2 (en) | 1996-02-29 | 1996-02-29 | Superheated steam production equipment using waste incineration heat |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPH09236230A JPH09236230A (en) | 1997-09-09 |
| JP3276286B2 true JP3276286B2 (en) | 2002-04-22 |
Family
ID=13391869
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP06906796A Expired - Fee Related JP3276286B2 (en) | 1996-02-29 | 1996-02-29 | Superheated steam production equipment using waste incineration heat |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JP3276286B2 (en) |
Families Citing this family (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP7042112B2 (en) * | 2018-02-27 | 2022-03-25 | 三菱重工業株式会社 | Power plant |
-
1996
- 1996-02-29 JP JP06906796A patent/JP3276286B2/en not_active Expired - Fee Related
Also Published As
| Publication number | Publication date |
|---|---|
| JPH09236230A (en) | 1997-09-09 |
Similar Documents
| Publication | Publication Date | Title |
|---|---|---|
| KR910009058B1 (en) | Combined gas turbine power generation system and its operation method | |
| WO1997032161A1 (en) | Method and apparatus for producing superheated steam using heat generated through incineration of wastes | |
| JP3276273B2 (en) | Superheated steam production equipment using waste incineration heat | |
| JP3276286B2 (en) | Superheated steam production equipment using waste incineration heat | |
| PL179698B1 (en) | Fluidised bed furnace for performing heat treatment of waste materials | |
| JP3327749B2 (en) | Superheated steam production equipment using waste incineration heat | |
| JP3322557B2 (en) | Superheated steam production equipment using waste incineration heat | |
| JP3276271B2 (en) | Superheated steam production equipment using waste incineration heat | |
| JP3408678B2 (en) | Superheated steam production equipment using waste incineration heat | |
| AU7074594A (en) | Method of treating solid material at high temperatures | |
| JP3285740B2 (en) | Superheated steam production equipment using waste incineration heat | |
| JP3276274B2 (en) | Superheated steam production equipment using waste incineration heat | |
| JP3276272B2 (en) | Superheated steam production equipment using waste incineration heat | |
| JP3272582B2 (en) | Superheated steam production equipment using waste incineration heat | |
| JP3534552B2 (en) | Waste incineration apparatus and superheated steam production apparatus using incineration heat of the waste | |
| JP3477327B2 (en) | Superheated steam production method and apparatus using waste incineration heat | |
| JP3408686B2 (en) | Superheated steam production equipment using waste incineration heat | |
| JP3272583B2 (en) | Superheated steam production equipment using waste incineration heat | |
| JP3305172B2 (en) | Superheated steam production equipment using waste incineration heat | |
| JP3310853B2 (en) | Superheated steam production equipment using waste incineration heat | |
| JP3285752B2 (en) | Superheated steam production equipment using waste incineration heat | |
| JP2004219067A (en) | Incinerator | |
| JP3272581B2 (en) | Superheated steam production equipment using waste incineration heat | |
| JP2989351B2 (en) | Waste incineration method | |
| JP3029517B2 (en) | Fluid bed waste incinerator with waste heat boiler |
Legal Events
| Date | Code | Title | Description |
|---|---|---|---|
| A01 | Written decision to grant a patent or to grant a registration (utility model) |
Free format text: JAPANESE INTERMEDIATE CODE: A01 Effective date: 20020108 |
|
| FPAY | Renewal fee payment (event date is renewal date of database) |
Free format text: PAYMENT UNTIL: 20080208 Year of fee payment: 6 |
|
| FPAY | Renewal fee payment (event date is renewal date of database) |
Free format text: PAYMENT UNTIL: 20090208 Year of fee payment: 7 |
|
| LAPS | Cancellation because of no payment of annual fees |