JPH09236221A - Manufacture of superheated steam utilizing incinerated heat of waste - Google Patents

Manufacture of superheated steam utilizing incinerated heat of waste

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Publication number
JPH09236221A
JPH09236221A JP6909096A JP6909096A JPH09236221A JP H09236221 A JPH09236221 A JP H09236221A JP 6909096 A JP6909096 A JP 6909096A JP 6909096 A JP6909096 A JP 6909096A JP H09236221 A JPH09236221 A JP H09236221A
Authority
JP
Japan
Prior art keywords
gas
combustion
pyrolysis
pyrolysis gas
steam
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
JP6909096A
Other languages
Japanese (ja)
Other versions
JP3285752B2 (en
Inventor
Hirotoshi Horizoe
浩俊 堀添
Shizuo Yasuda
静生 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.)
Mitsubishi Heavy Industries Ltd
Original Assignee
Mitsubishi Heavy Industries Ltd
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Priority to JP06909096A priority Critical patent/JP3285752B2/en
Application filed by Mitsubishi Heavy Industries Ltd filed Critical Mitsubishi Heavy Industries Ltd
Priority to US08/945,591 priority patent/US6133499A/en
Priority to EP97903617A priority patent/EP0823590B1/en
Priority to PCT/JP1997/000573 priority patent/WO1997032161A1/en
Priority to KR1019970707702A priority patent/KR100264723B1/en
Priority to DE69732394T priority patent/DE69732394T2/en
Priority to SG9904761A priority patent/SG96183A1/en
Publication of JPH09236221A publication Critical patent/JPH09236221A/en
Application granted granted Critical
Publication of JP3285752B2 publication Critical patent/JP3285752B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

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  • Incineration Of Waste (AREA)
  • Gasification And Melting Of Waste (AREA)

Abstract

PROBLEM TO BE SOLVED: To efficiently reduce chlorine and to obtain the superheated steam of high temperature by dissolving to separate the ash content separated from the gas removed by char combustion or thermally decomposing means by primary combustion heat of the pyrolysis gas between the decomposing means and steam manufacturing means, and conducting secondary combustion. SOLUTION: Fluid sand and waste such as municipal refuse are introduced from a line 5, fluidized bed space of 300 deg.C or higher is generated by combustion exhaust gas, and pyrolysis reaction is conducted. The pyrolysis gas from a pyrolysis gas outlet line 7 is introduced into an ash melting furnace 31, the air is introduced together with the pyrolysis gas from a line 30 into the furnace 31 while turning and separating the sand mixed pyrolysis gas ash, the ash content is melted by pyrolysis gas combustion heat (primary), and dropped via a melted ash outlet line 32. A pyrolysis gas burning furnace 34 formed of a combustion duct is disposed at the downstream end of an outlet line 33, sufficient air is supplied from a line 21A to the combustion of the pyrolysis gas to conduct the complete combustion (secondary) of the pyrolysis gas.

Description

【発明の詳細な説明】Detailed Description of the Invention

【0001】[0001]

【発明の属する技術分野】本発明は、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C1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HC1となり(通常、都市ごみ燃焼排ガス中のHC
1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30〜40%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 vinyl chloride plastic, and the combustible content is about 0.2 to 0.
Contains 5%. Then, chlorine contained in PVC plastic mixed in the waste such as municipal waste becomes HC1 by combustion (usually, HC in exhaust gas from combustion of municipal waste is
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 the fuel efficiency is about 30 to 40%, which is significantly lower than the plant power generation efficiency of about 30 to 40%, in which the boiler tube temperature can be set to 500 to 600 ° C. by using heavy oil or LNG, which contains almost no chlorine, as fuel. Was there.

【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同時出願の特許願(整理番号96
P0191)に提案している。かかる基本発明は、略2
00℃〜320℃前後に沸点を有するように加圧させた
蒸気水を用い、該蒸気水の加熱を少なくとも2段階以上
の複数段階とし、前記略沸点温度までの加熱を含塩素熱
エネルギで行ない、前記略沸点温度から所定温度の過熱
蒸気を得る過熱を塩素を含まない脱塩素熱エネルギで行
なう事を特徴とするものである。
In view of the above technical problems, the present inventors simultaneously applied for an invention relating to the production of superheated steam capable of efficiently obtaining high temperature and high pressure superheated steam while preventing high temperature corrosion of a boiler tube due to chlorine. Patent application (reference number 96
P0191). The basic invention is approximately 2
Steam water pressurized to have a boiling point of around 00 ° C. to 320 ° C. is used, the heating of the steam water is performed in a plurality of stages of at least two stages, and heating up to the above-mentioned boiling point temperature is performed with chlorine-containing heat energy. The heating is performed by dechlorination heat energy containing no chlorine to obtain superheated steam at a predetermined temperature from the substantially boiling point.

【0005】かかる基本発明によれば例えば図4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HC1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蒸気
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
下にでき、これを腐食させる事にならない。この場合前
記蒸気水は加圧により沸点を略200℃〜320℃前後
に設定してある為に前記含塩素熱分解ガスの蒸気水への
熱エネルギの付与にバラツキが生じていてもそれは該蒸
気水の潛熱の吸収(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、蒸気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蒸
気水若しくは蒸気を得る事が出来る。
According to such a basic invention, for example, as shown in FIG. 4, even if chlorine-containing pyrolysis gas in which HC1 or the like is contained in the pyrolysis gas by thermally decomposing waste such as municipal waste Since the steam water is heated by the thermal energy of the chlorine-containing pyrolysis gas to a boiling point of about 200 ° C. to 320 ° C., the chlorine-containing pyrolysis gas may act on the tube of the steam generating boiler. The tube surface temperature can be kept below about 350 ° C, and it will not corrode. In this case, since the boiling point of the steam water is set to about 200 ° C. to 320 ° C. by pressurization, even if the heat energy of the chlorine-containing pyrolysis gas is varied in application of heat energy to the steam water, The surface temperature of the heat exchange tube of steam water rises above the chlorine corrosion temperature because it is used to absorb the heat of water (in other words, it is used only for the phase conversion of water to steam and does not act as a temperature rise). Without doing so, it is possible to obtain steam water or steam with a stable heating temperature.

【0006】そして前記略350℃〜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蒸気水若しくは蒸気を二
次〜三次加熱して400〜550℃の過熱蒸気を得ても
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約
30〜40%前後の発電効率を得る事が出来る。
Since the undecomposed residue that has not been decomposed by the thermal decomposition at about 350 ° C. to 500 ° C. has already been dechlorinated, it can be obtained by burning it, for example, 500
Approximately 200 ° C. using heat energy of about 950 ° C.
Even if steam water or steam that is primarily heated to around 320 ° C is secondarily to thirdly heated to obtain superheated steam at 400 to 550 ° C, tube corrosion does not occur. As a result, even when power is generated by incineration of waste, it is possible to obtain a power generation efficiency of about 30 to 40%, which is similar to that of a plant using heavy oil containing little chlorine, LNG, or the like as a fuel.

【0007】そしてかかる発明を具体化させる装置とし
て、温度300℃以上、好ましくは温度350〜500
℃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
する例えば流動床、ロータリキルン、横型スクリュー攪
拌槽等を利用した熱分解手段と、空気によって前記チャ
ー混合物を流動させながら前記未分解残渣を燃焼させる
例えば高速流動床や気泡流動床その他の流動床等からな
るチャー燃焼手段と、前記熱分解ガスを直接若しくは再
燃焼させた後、その熱を利用して約400℃以下、具体
的には200〜320℃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
た燃焼ガスの熱により前記第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
段を含む廃棄物の焼却熱を利用した過熱蒸気製造装置を
前記基本発明にて提案している。
A device for embodying the invention is a temperature of 300 ° C. or higher, preferably a temperature of 350 to 500.
The waste is supplied into the space of ℃ to carry out the thermal decomposition reaction,
Pyrolysis gas generated by the reaction, a char mixture composed of undecomposed residue and fluid medium and incombustibles are separated from each other, for example, a fluidized bed, a rotary kiln, a thermal decomposition means using a horizontal screw stirring tank, and the like by air. A char combustion means for combusting the undecomposed residue while fluidizing the char mixture, such as a high-speed fluidized bed, a bubbling fluidized bed or other fluidized bed, and directly or re-combusting the pyrolysis gas, and then using the heat At about 400 ° C. or less, specifically 200 to 320 ° C., by the first steam producing means and the heat of the combustion gas obtained by the char combustion means. In the above basic invention, there is provided a superheated steam manufacturing apparatus using the incineration heat of waste, which includes a second steam manufacturing means for converting the manufactured hot water or steam into superheated steam. It is draft.

【0008】本発明は、かかる基本技術を更に発展さ
せ、前記基本技術に比較して更に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
の製造装置を提供する事にある。本発明の他の目的は、
前記いずれの蒸気製造装置においても、長期に亙って安
定して蒸気の製造を可能にした過熱蒸気の製造にかかる
発明を提供する事にある。又本発明の他の目的は、前記
熱分解ガスの一層の効率利用を図った過熱蒸気の製造装
置を提供する事にある。又本発明の他の目的は、前記熱
分解ガス若しくは燃焼ガスを分離して得られた灰を溶融
して骨材等の製造が可能となる過熱蒸気の製造装置を提
供する事にある。
The present invention further develops such basic technology, and provides a superheated steam production apparatus capable of more efficiently reducing chlorine and obtaining superheated steam at high temperature as compared with the above-mentioned basic technology. is there. Another object of the present invention is to
It is an object of the present invention to provide an invention relating to the production of superheated steam, which enables stable production of steam for a long period of time in any of the above steam production apparatuses. Another object of the present invention is to provide an apparatus for producing superheated steam in which the pyrolysis gas is used more efficiently. Another object of the present invention is to provide a superheated steam production apparatus capable of producing aggregate or the like by melting ash obtained by separating the pyrolysis gas or combustion gas.

【0009】[0009]

【課題を解決するための手段】請求項1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
燃焼エネルギーを利用して200〜320℃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む点は、前記基本技術と同様で
あるが、前記熱分解手段と第1の蒸気製造手段との間
に、前記熱分解ガスの第1次燃焼熱により、チャー燃焼
手段若しくは熱分解手段より取り出された夫々のガスよ
り分離された灰分の溶融分離を行う灰分溶融分離手段を
設けた点を第1の特徴とし、好ましくは前記灰分が分離
された熱分解ガスの2次燃焼を行う2次燃焼手段を設け
たことを第2の特徴とする。
According to the first aspect of the present invention,
Pyrolysis in which waste is supplied into a space having a temperature of 300 ° C. or higher to cause a pyrolysis reaction, and a pyrolysis gas generated by the reaction, a char mixture composed of undecomposed residue and a fluid medium, and an incombustible substance are separated from each other. Means, a char combustion means for combusting the undecomposed residue while flowing a char mixture composed of the undecomposed residue and the fluidized medium taken out from the thermal decomposition means by air, and utilizing combustion energy of the thermally decomposed gas First steam producing means for producing hot water or steam having a temperature of 200 to 320 ° C., and the hot water or steam produced by the first steam producing means by the thermal energy obtained by the char combustion means as superheated steam. A second steam producing means is included, which is similar to the basic technique described above, but the pyrolysis gas is provided between the pyrolysis means and the first steam producing means. The first feature is that an ash melting and separating means for melting and separating the ash separated from each gas taken out from the char combustion means or the thermal decomposition means by the primary combustion heat is provided, and preferably the ash content is A second feature is that a secondary combustion means for performing secondary combustion of the pyrolysis gas separated from is separated.

【0010】かかる発明によれば次のような効果を有す
る。即ち、チャー燃焼手段内では炭化状態にあるチャー
混合物と流動砂の熱接触により燃焼ガス中に灰分が混入
するのを避けられない。これは熱分解手段により得られ
る熱分解ガスについても同様である。そこで前記必要に
応じガス分離した後、若しくはガス分離をしながら灰分
の溶融分離を行う灰分溶融分離手段を設けることによ
り、前記溶融灰を利用して骨材等の製造が可能となる。
更に、熱分解ガスを利用して2次燃焼を行い、該2次燃
焼手段内にボイラ等の第1の蒸気製造手段を配設する事
により、一層効率良くボイラ水の一次加熱が可能であ
る。
According to this invention, the following effects can be obtained. That is, in the char combustion means, it is inevitable that ash is mixed in the combustion gas due to thermal contact between the char mixture in the carbonized state and the fluidized sand. The same applies to the pyrolysis gas obtained by the pyrolysis means. Therefore, after the gas is separated as necessary, or by providing an ash melting / separating means for melting and separating the ash while the gas is being separated, it is possible to manufacture an aggregate or the like using the molten ash.
Further, the secondary combustion is performed by utilizing the pyrolysis gas, and the first steam producing means such as the boiler is provided in the secondary combustion means, whereby the primary heating of the boiler water can be further efficiently performed. .

【0011】さて前記熱分解ガス中に含まれる灰及び燃
焼ガス中に含まれる灰は、廃棄物に対し1割程度であ
り、従ってこれを供給される熱分解ガス全てを使用して
溶融することは必ずしも必要なく、却って過剰熱エネル
ギになりやすい。又前記熱分解ガスを灰が溶融出来るま
での高温燃焼させるために必要な酸素富化空気も多くな
る。そこで請求項2記載の発明は、前記熱分解手段によ
り得られた熱分解ガスを灰分溶融分離手段とともに、そ
の一部を分岐して前記2次燃焼手段に供給することを特
徴とする。
The ash contained in the pyrolysis gas and the ash contained in the combustion gas account for about 10% of the waste. Therefore, the ash contained in the pyrolysis gas should be melted using all the pyrolysis gas supplied. Is not always necessary, but rather tends to become excess heat energy. Also, the oxygen-enriched air required to burn the pyrolysis gas at a high temperature until ash can be melted increases. Therefore, the invention according to claim 2 is characterized in that the pyrolysis gas obtained by the pyrolysis means is supplied to the secondary combustion means together with the ash melting separation means and a part of the gas is branched.

【0012】請求項3記載の発明は、温度300℃以上
の酸素過小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を2次燃焼手
段若しくは熱交換手段に供給するた熱分解ガス出口経路
中に絞り部を設け、該絞り部の入口側と出口側に夫々設
けた圧力取り出し口に少量の空気を適宜流す空気流入手
段を設けた事を特徴とする。
According to a third aspect of the present invention, waste is supplied into an oxygen-deficient space having a temperature of 300 ° C. or higher to cause a pyrolysis reaction, and the pyrolysis gas generated by the reaction is subjected to secondary combustion means or heat exchange. A throttle portion is provided in the pyrolysis gas outlet path supplied to the means, and air inlet means for appropriately flowing a small amount of air is provided at the pressure outlets provided on the inlet side and the outlet side of the throttle portion, respectively. To do.

【0013】さて、灰分の溶融に必要な熱分解ガスの流
量を計測して、制御するために熱分解ガスの経路中にオ
リフィス等の差圧計を配し、その流量(流速)測定を行
なう必要がある。このため前記熱分解手段よりの出口経
路中にオリフィス等の差圧計(絞り)を配し、流量測定
を行なう必要があるが、前記熱分解手段よりの出口ガス
はその出口温度が350〜500℃前後の為に、タール
分を含んだガスが出てくる場合があり、そのタール分が
絞り部や圧力タップ(細孔状の圧力取り出し口)に付着
し、円滑な流量測定が困難になる。そこで本発明は、絞
り部の入口側と出口側に夫々設けた圧力取り出し口に少
量の空気(支燃性ガスを含む気体の意味で空気という言
葉を用いている。)を適宜流す空気流入手段を設けるこ
とにより、前記タール分を燃焼させて付着等を防止し
て、安定して圧力を測定できる。
Now, in order to measure and control the flow rate of the pyrolysis gas required for melting the ash, a differential pressure gauge such as an orifice is arranged in the path of the pyrolysis gas to measure the flow rate (flow velocity). There is. Therefore, it is necessary to arrange a differential pressure gauge (throttle) such as an orifice in the outlet path from the thermal decomposition means to measure the flow rate. The outlet gas from the thermal decomposition means has an outlet temperature of 350 to 500 ° C. The gas containing the tar component may come out due to the front and rear, and the tar component adheres to the throttle portion and the pressure tap (the pressure outlet of the pore shape), which makes it difficult to measure the flow rate smoothly. Therefore, in the present invention, an air inflow means for appropriately flowing a small amount of air (the word "air" is used to mean a gas containing a combustion-supporting gas) to the pressure outlets provided on the inlet side and the outlet side of the throttle portion. By providing the above, the tar content can be burned to prevent adhesion and the pressure can be stably measured.

【0014】請求項4記載の発明は、前記熱分解手段に
より得られた熱分解ガスの一部を分岐して熱分解手段の
入口側に供給することを特徴とする。かかる発明によれ
ば、前記熱分解手段により得られた熱分解ガスの一部を
分岐して熱分解手段の入口側に供給するものであるため
に、言換えれば350℃〜500℃の高温の可燃性ガス
を熱分解手段に循環供給する事が出来るために、熱分解
ガスが空気又は燃焼排ガス中のN2、CO2,H2O等の
不活性ガスでの希釈を最小限に抑えて、単位容積当りの
発熱量を高くし、灰溶融炉31の温度保持が容易にな
る。
The invention according to claim 4 is characterized in that a part of the pyrolysis gas obtained by the pyrolysis means is branched and supplied to the inlet side of the pyrolysis means. According to this invention, a part of the pyrolysis gas obtained by the pyrolysis means is branched and supplied to the inlet side of the pyrolysis means. In other words, at a high temperature of 350 ° C. to 500 ° C. Since the combustible gas can be circulated and supplied to the thermal decomposition means, the thermal decomposition gas can be diluted with the inert gas such as N 2 , CO 2 , H 2 O in the air or the combustion exhaust gas to a minimum. Further, the calorific value per unit volume is increased, and the temperature of the ash melting furnace 31 can be easily maintained.

【0015】[0015]

【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 figure, 1 is a pyrolysis furnace composed of a fluidized bed, and a dispersion plate 3 such as a perforated plate is used to disperse fluidized sand or the like. Fluid medium 2-
1 is stored, and the wastes such as fluidized sand and municipal waste are input from the waste supply line 4 and the sand circulation (return) line 5, and the combustion exhaust gas supplied from the combustion exhaust gas inlet line 6 (this thermal decomposition Since the furnace is basically not a combustion but a thermal decomposition, most of the gas supplied is the combustion exhaust gas that consumed oxygen, but a small amount of air is added to control the temperature.) A fluidized bed space of 300 ° C. or higher is generated to cause a thermal decomposition reaction of waste, and the thermal decomposition gas generated by the reaction is discharged from the thermal decomposition gas outlet line 7
The char mixture consisting of undecomposed residue and fluidized sand is separated from the char mixture take-out line 9 and the incombustible is taken out from the non-combustible take-out line 8, respectively.

【0016】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好ましい。これ
は、加温すべきボイラ水を100Kgf/cm2前後に
加圧してその沸点を309℃前後に設定している為に、
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。又熱
分解炉1出口側の熱分解ガス出口ライン7には図3に示
す差圧計測手段100が形成してもよく、特に図2に示
すように熱分解ガス出口ライン7をライン7’、7−1
として分岐する場合は差圧計測手段100により分岐流
量を測定する必要がある。この差圧計測手段100は、
熱分解炉1より取り出された熱分解ガスの流量(流速)
を測定するとともに、前記差圧計測手段100を形成す
る絞り部110の入口側と出口側に夫々設けた圧力取り
出し口109、109に少量の空気を適宜流すことによ
り、熱分解ガス中に含まれるタール等を燃焼させ、絞り
部110及び圧力取り出し口109におけるタール付着
防止やコーキング防止を図る。
At this time, it is preferable to perform the thermal decomposition so that the thermal calorie ratio of the thermal decomposition gas and the char mixture is "about 7 (pyrolysis gas): about 3 (char mixture)". This is because the boiler water to be heated is pressurized to around 100 Kgf / cm 2 and its boiling point is set to around 309 ° C.
For the pyrolysis gas, the water-cooled wall boiler 36 and the first boiler 24
Then, the ratio of the calorie that rises boiler water from room temperature to "boiling point 309 ° C + latent heat of vaporization" in other words at 309 ° C until it almost vaporizes, and the calorie that raises the raised steam from boiling point 309 ° C to 500 ° C are It is about 7: 3. Further, the differential pressure measuring means 100 shown in FIG. 3 may be formed in the thermal decomposition gas outlet line 7 on the outlet side of the thermal decomposition furnace 1. In particular, as shown in FIG. 7-1
When branching as, it is necessary to measure the branch flow rate by the differential pressure measuring means 100. This differential pressure measuring means 100 is
Flow rate (flow velocity) of the pyrolysis gas extracted from the pyrolysis furnace 1
Is measured, and a small amount of air is appropriately made to flow through the pressure outlets 109, 109 provided on the inlet side and the outlet side of the throttle portion 110 forming the differential pressure measuring means 100, respectively, so as to be contained in the pyrolysis gas. By burning tar or the like, it is possible to prevent tar from adhering to the throttle portion 110 and the pressure outlet 109 and prevent coking.

【0017】図3(A)はオリフィスを用いて形成した
差圧計測手段で、101、101’は出口ライン7を形
成する配管、102はフランジ、103はオリフィスプ
レート、104は差圧計、105、106、107、1
08は空気導入管、109は圧力取り出し口としての圧
力タップ、110は絞り部、111は空気量調整弁、1
12はフローメータその他の流量計である。圧力タップ
109はAーA線断面図で示すように、周方向に90°
づつ変角させた位置に、4個設ける。図3(B)はラッ
パ状の絞り部110を用いて形成した差圧計測手段10
0で、その構成は図3(A)と同様である。
FIG. 3A shows a differential pressure measuring means formed by using an orifice, 101 and 101 'are pipes forming the outlet line 7, 102 is a flange, 103 is an orifice plate, 104 is a differential pressure gauge, and 105, 106, 107, 1
08 is an air introduction pipe, 109 is a pressure tap as a pressure outlet, 110 is a throttle part, 111 is an air amount adjusting valve, 1
12 is a flow meter and other flow meters. The pressure tap 109 is 90 ° in the circumferential direction as shown in the sectional view taken along the line AA.
Four pieces are provided at different positions. FIG. 3B shows a differential pressure measuring means 10 formed by using a trumpet-shaped throttle portion 110.
0, the configuration is the same as in FIG.

【0018】熱分解ガス出口ライン7よりの熱分解ガ
ス、又図2のように分岐され前記差圧計測手段100を
通過後の熱分解ガスは、灰溶融炉31に導入される。前
記灰溶融炉31は、例えば旋回流により砂混合熱分解ガ
ス灰を旋回分離させながら、該灰溶融炉31内に空気若
しくは酸素富化空気を前記熱分解ガスと共に、ライン3
0より導入して該熱分解ガス燃焼熱により1300℃以
上として灰分を溶融して、該溶融した灰分を溶融灰出口
ライン32を介して水貯溜部32Aに落下させ、数mm
程度の水冷スラッグを生成し、該スラッグを建築用骨材
として利用するように構成する。又前記灰溶融炉31に
はサイクロン16の出口ライン18/ダストライン29
を介して灰が導入され、又、ライン14の不燃物も又は
/及びバブフィルターや電気集塵機の捕集灰も、これも
溶融分離される。
The pyrolysis gas from the pyrolysis gas outlet line 7 or the pyrolysis gas that has been branched as shown in FIG. 2 and passed through the differential pressure measuring means 100 is introduced into the ash melting furnace 31. The ash melting furnace 31 swirls and separates the sand-mixed pyrolysis gas ash by, for example, a swirl flow, and air or oxygen-enriched air is introduced into the ash melting furnace 31 together with the pyrolysis gas in a line 3
0, and the ash content is melted at 1300 ° C. or higher by the heat of combustion of the pyrolysis gas, and the melted ash content is dropped through the molten ash outlet line 32 into the water storage section 32A, and is heated for several mm.
It is configured to generate a degree of water-cooled slug and utilize the slug as a building aggregate. Further, the ash melting furnace 31 has a cyclone 16 outlet line 18 / dust line 29.
The ash is introduced via the ash, and the incombustibles in the line 14 and / or the ash collected by the bubb filter or the electrostatic precipitator are also separated by melting.

【0019】又、前記灰溶融炉31の出口ライン33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空気をライン21
Aより供給して該熱分解ガスの完全燃焼を行う。従って
本実施例によれば前記サイクロン16で分離した灰分及
び/又はライン14の不燃物は前記した灰溶融炉31に
導入する事により、前記溶融灰を利用して骨材等の製造
が可能となる。又、熱分解ガス燃焼炉34及び第1ボイ
ラ24に導入される熱分解ガス中に灰分等が混入される
ことなく長期に亙って安定して蒸気製造が可能になると
ともに、又熱分解ガス燃焼炉34及び第1ボイラ24に
導入される熱分解ガス温度を略800〜900℃(最大
950℃前後)程度に高く設定できるために、該ボイラ
等で製造されるボイラ水/蒸気を更に多量に製造でき
る。
At the downstream end of the outlet line 33 of the ash melting furnace 31, a pyrolysis gas combustion furnace 34 composed of a combustion duct is provided.
Is provided, and sufficient air is supplied to the pyrolysis gas through a line 21.
A to complete combustion of the pyrolysis gas. Therefore, according to the present embodiment, by introducing the ash separated by the cyclone 16 and / or the incombustibles in the line 14 into the ash melting furnace 31, it is possible to use the molten ash to manufacture an aggregate or the like. Become. Further, ash etc. are not mixed in the pyrolysis gas introduced into the pyrolysis gas combustion furnace 34 and the first boiler 24, which enables stable steam production over a long period of time, and also the pyrolysis gas. Since the temperature of the pyrolysis gas introduced into the combustion furnace 34 and the first boiler 24 can be set as high as approximately 800 to 900 ° C. (around 950 ° C. at the maximum), a larger amount of boiler water / steam produced by the boiler or the like can be produced. Can be manufactured.

【0020】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加熱し約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又
は/及びボイラを配設し、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、前記第2ス−パヒ−タ29−1の代わりに水冷
壁ボイラの加熱に供しても良い。
Numeral 10 is a char combustion furnace consisting of a bubbling fluidized bed furnace, and a char mixture supplied from a char mixture take-out line 9 on a dispersion plate 11 arranged at the bottom and a sand circulation line 19-2 / 19-1. The fluidized sand circulated between the auxiliary char combustion furnace 10B and the auxiliary char combustion furnace 10B is stored. Then, air is supplied from an air supply line 12 below the dispersion plate 11 and heated to 700 to 800 ° C. in the fluidized bed 2-3 to burn undecomposed residue, and further air supply to the middle region of the char combustion furnace 10. About 800 ~
A combustion gas of around 1300 ° C. is generated, and a second superheater 29-1 or / and a boiler is arranged in the upper region of the char combustion furnace 10, and a line is provided from a second steam producing means (first superheater 20). Along with the superheat of the superheated steam introduced through 28-1, the combustion gas which has risen unnecessarily high at around 950 to 1300 ° C is dropped to 800 to 950 ° C. Incidentally, instead of the second superheater 29-1, a water-cooled wall boiler may be heated.

【0021】尚前記のように燃焼ガス温度を800〜9
50℃に落としても第1スーパヒータ20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。そして前記チャー燃焼炉10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。
As described above, the combustion gas temperature is set to 800-9.
Even if the temperature is lowered to 50 ° C, there is no problem in maintaining the steam temperature in the first superheater 20 at 400 to 520 ° C. Then, the small incombustibles that are not burned in the char combustion furnace 10 are taken out from the incombustibles taking-out line 14.

【0022】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、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2
9−2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。
On the other hand, the char combustion furnace 10 is additionally provided with a sub char combustion furnace 10B as a sub fluidized bed, and the sub char combustion furnace 10B is provided via a sand circulation line 19-2 / 19-1.
And the third superheater 2 in the flowing medium of the auxiliary char combustion furnace 10B.
9-2, and is connected to the outlet side of the second superheater 29-1 via the line 28-2.

【0023】尚、副チャー燃焼炉10Bは、独立して設
けてもよいが、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。
The auxiliary char combustion furnace 10B may be provided independently, but a fluidized medium path 19-1 / for returning the fluidized medium heated by the char combustion furnace 10 to the pyrolysis furnace 1
It is preferable to interpose the auxiliary char combustion furnace 10B provided with the third super heater 29-2 in the No. 5 chamber.

【0024】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
気・固分離装置例えば必要に応じサイクロン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 super heater 29-1 is introduced from the sand / combustion gas outlet line 15 into a gas / solid separation device, for example, a cyclone 16 as required, where it is burned with dust and ash. Gas is separated from the gas, and the combustion gas is introduced into the first super heater 20 through the gas outlet line 17.

【0025】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。25は、排ガス排
出ラインである。
Reference numeral 20 is a first superheater and 24 is a first boiler. In the first boiler 24, the pyrolysis gas taken out from the pyrolysis gas outlet line 7 is 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 together with the combustion exhaust gas that has been burned inside and discharged from the boiler gas outlet 22 of the first superheater 20 and taken in through the boiler water inlet 26 is heated to around 300 ° C. From the boiler exit line 27 to the first super heater 2
Supply steam or heated water to 0. 25 is an exhaust gas discharge line.

【0026】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 the water-cooled wall boiler 36 in the combustion gas combustion furnace 34 via the branch line 26 'and supplies steam or heated water to the first super heater 20 via the 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.

【0027】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309℃前後に維持でき、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 temperatures of the water-cooled wall boiler 36 and the first boiler 24 can be maintained at around 309 ° C. following the heated water, and chlorine or HCl can be added to the heat-decomposed pyrolysis gas. Corrosion does not occur even if it is included.

【0028】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、400〜550℃前後
の過熱蒸気を製造し、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
〜550℃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, 27 'of the first boiler 24 and the water-cooled wall boiler 36 and heated by the water-cooled wall boiler 36 are taken out via the branch steam line 27'. Introduced steam / heated water is heated by the combustion gas supplied through the combustion gas line 17 to produce superheated steam of about 400 to 550 ° C., and the second from the steam outlet line 28-1. Introduced in series to the superheater 29-1, and further to the third superheater 29-2 from the line 28-2, respectively.
The superheated steam superheated to ˜550 ° C. is taken out and sent to the generator.

【0029】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C1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を流動させた流
動床内で、温度300〜500℃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。
Although the operation of the above-described embodiment has already been described along with its structure, a brief repetitive explanation will be made. In the waste such as municipal solid waste supplied to the pyrolysis furnace 1, chlorine-containing organic compounds such as vinyl chloride plastic are mixed. The content of C1 in the combustible content is about 0.2 to 0.5%. Then, municipal waste is supplied from the waste supply line 4 and high-temperature circulating fluidized sand is supplied from the fluidized sand circulation line 5 to the pyrolysis furnace 1, respectively, and a slight temperature adjustment is made to the combustion exhaust gas from the lower air or the combustion exhaust gas inlet line 6. By treating at a temperature of 300 to 500 ° C. in a fluidized bed in which the working air is supplied to fluidize the fluidized sand 2, an undecomposed residue containing substantially no chlorine is obtained from the char mixture withdrawing line 9. That is, the chlorine contained in the waste is substantially contained in the pyrolysis gas and is discharged to the pyrolysis gas outlet line 7. The large incombustibles separated by the thermal decomposition reaction in the thermal decomposition furnace 1 are taken out of the furnace through the incombustibles extraction line 8.

【0030】さて、図5に示すように前記熱分解炉によ
り得られた熱分解ガスの一部を灰溶融炉31の上流側
で、分岐ライン7ー2を介して熱分解炉の分散板3下方
の入口側に供給するように構成してもよい。これにより
ライン7−1の熱分解ガスが流動化ガス(N2、CO2
2O主成分の不活性ガス)で希釈されないので高カロ
リガスとなり、灰溶融炉31の温度を容易に1300〜
1500℃にすることが出来る。
Now, as shown in FIG. 5, a part of the pyrolysis gas obtained by the pyrolysis furnace is provided upstream of the ash melting furnace 31 through the branch line 7-2 to the dispersion plate 3 of the pyrolysis furnace. It may be configured to supply to the lower inlet side. As a result, the pyrolysis gas in line 7-1 becomes a fluidizing gas (N 2 , CO 2 ,
Since it is not diluted with (inert gas containing H 2 O as a main component), it becomes a high calorie gas, and the temperature of the ash melting furnace 31 can be easily adjusted to 1300 to 1300.
It can be 1500 ° C.

【0031】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は、差圧計測手段100の絞り
部110を通過する事により、その入口側と出口側の圧
力タップ109より取り出した圧力を差圧計104で検
知し、そのガス流量(流速)を測定し灰溶融炉に必要な
熱分解ガスを供給する。そしてかかる差圧計測手段10
0の場合、熱分解ガス中のタール分が圧力タップ109
の入口部や絞り部110に付着する。そこで本実施例に
おいては空気量調整弁111、空気導入管105〜10
8を介して流量計112により制御された常に少量の空
気を供給して、該空気により前記付着タールを燃焼さ
せ、絞り部110や出口ライン7におけるタール付着防
止やコーキングを防止する。
The pyrolysis gas taken out from the pyrolysis outlet line 7 of the pyrolysis furnace 1 is taken out from the pressure taps 109 on the inlet side and the outlet side of the differential pressure measuring means 100 by passing through the throttle portion 110. The pressure difference is detected by the differential pressure gauge 104, the gas flow rate (flow velocity) is measured, and the necessary thermal decomposition gas is supplied to the ash melting furnace. And the differential pressure measuring means 10
In the case of 0, the tar content in the pyrolysis gas is the pressure tap 109.
Adheres to the entrance portion and the narrowed portion 110. Therefore, in this embodiment, the air amount adjusting valve 111 and the air introducing pipes 105 to 10
A small amount of air controlled by the flow meter 112 is constantly supplied via 8 to burn the adhered tar by the air to prevent the tar from adhering to the throttle portion 110 and the outlet line 7 and preventing coking.

【0032】前記灰溶融炉31では、前記したように前
記熱分解ガスとともに、サイクロン16の出口ライン1
8/ダストライン29を介して燃焼ガスの灰が導入さ
れ、ライン30より導入した空気若しくは酸素富化空気
を前記熱分解ガスと共に燃焼して灰分を溶融して、該溶
融した灰分を水貯溜部32Aに落下させ、数mm程度の
水冷スラッグを生成し、該スラッグを建築用骨材として
利用する。又、前記灰溶融炉31の出口ライン33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21Aより空
気を供給して該熱分解ガスの完全燃焼を行う。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及び第一ボイラ24に導入さ
れ沸点200〜309℃近くまで立上げる蒸気/ボイラ
水を多量に製造できる。
In the ash melting furnace 31, the outlet line 1 of the cyclone 16 together with the pyrolysis gas as described above.
8 / The ash of the combustion gas is introduced through the dust line 29, the air or the oxygen-enriched air introduced through the line 30 is burned together with the pyrolysis gas to melt the ash, and the molten ash is stored in the water storage section. It is dropped to 32 A to generate a water-cooled slug of about several mm, and the slug is used as a building aggregate. Further, a pyrolysis gas combustion furnace 34 composed of a combustion duct is disposed at the downstream end of the outlet line 33 of the ash melting furnace 31, and air is supplied to the pyrolysis gas from a sufficient line 21A to perform the pyrolysis. Complete gas combustion. As a result, since the temperature of the pyrolysis gas in the pyrolysis combustion furnace 34 can be set high, a large amount of steam / boiler water that is introduced into the water-cooled wall boiler 36 and the first boiler 24 and rises up to a boiling point of near 200 to 309 ° C. can be produced. .

【0033】又熱分解燃焼炉34内で水冷壁ボイラ36
と熱交換した熱分解ガスは、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HC1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及び第1ボイラ24では高温の過熱蒸気は得
られないが、約200〜320℃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400〜550
℃の高温の過熱蒸気を得ることができる。
In the pyrolysis combustion furnace 34, a water-cooled wall boiler 36 is also provided.
The pyrolysis gas that has exchanged heat with is supplied from the first boiler gas inlet 23 to the first boiler 24 together with the combustion exhaust gas from the first super heater boiler gas outlet line 22. Since the gas introduced into the pyrolysis combustion furnace 34 and the first boiler 24 contains HC1 in an amount of about 500 to 1000 ppm, the flow rate of boiler water is adjusted to adjust the water-cooled wall boiler 36 and the first boiler 24. The tube surface temperature is about 350, which is the same as the conventional one
C. or lower to suppress high-temperature corrosion. Therefore, high-temperature superheated steam cannot be obtained in the water-cooled wall boiler 36 and the first boiler 24, but since it can be heated up to about 200 to 320 ° C., it can be further heated to the super heaters 29-1 and 29- after the first super heater 20. If heated at 2, about 400-550
It is possible to obtain superheated steam at a high temperature of ° C.

【0034】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又は/及びライン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1
2、13の空気および砂循環ライン19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 undecomposed residue, and a char mixture containing substantially no chlorine is obtained.
In the combustion furnace 10, the air is supplied to the lower part of the combustion furnace 10 and burned by the air supplied from the air supply line 12 through the dispersion plate 11. In this case, the amount of air supplied from the air supply line 12 is adjusted so that the undecomposed residue is burned while flowing the fluidized sand. Air supply line 1 for complete combustion
3 or / and further air may be supplied from the line 19-3. The temperature of the combustion furnace 10 rises due to the combustion exothermic reaction. This temperature value is the char mixture take-out line 9
Calorific value of undecomposed residue and air supply line 1
Depending on the amount and temperature of the air of 2 and 13 and the fluidized sand in the sand circulation line 19, the temperature may become as high as around 1000 to 1200 ° C.

【0035】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。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 super heater 29-1 exchanges heat with the superheated steam from the first super heater 20 through the line 28-1 to generate a combustion gas of 800 to 950.
It is easy to reach ℃. The incombustibles reduced in size by melting glass, cans, and the like are extracted from the incombustibles take-out line 14.

【0036】尚、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600〜850℃、一方熱分解炉1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。
Since the fluidized medium of the char combustion furnace 10 circulates between the fluidized medium of the pyrolysis furnace 1, the temperature of the fluidized medium of the char combustion furnace 10 is about 600 to 850 ° C., while the fluidized medium of the pyrolysis furnace 1 is Has a large heat drop between the two, and therefore, when the fluidized medium of the char combustion furnace 10 is directly introduced into the pyrolysis furnace 1 side, the heat drop causes the thermal decomposition in the pyrolysis furnace 1 to occur. There is a risk that the temperature will rise and heat fluctuations will occur, and thus the adjustment of the amount of the fluid medium to be returned will be complicated.

【0037】そこで、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、ライン12’により空気を導入し、流動させながら
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50
0℃前後に安定して制御が可能である。
Therefore, the fluidized medium path 19 for returning the fluidized medium heated from the char combustion furnace 10 to the pyrolysis furnace 1
By interposing the auxiliary char combustion furnace 10B provided with the third super heater 29-2 in -1/5, the fluidized medium heated to 700 to 800 ° C in the first char combustion furnace 10 is supplied through the line 12 '. The third super heater 29-2 is introduced in the auxiliary char combustion furnace 10B while introducing and flowing air.
The temperature is reduced to 500 to 700 ° C by heat removal by
Since the fluidized medium dropped to ˜700 ° C. can be returned to the thermal decomposition furnace 1, a gentle thermal gradient can be achieved. As a result, the thermal decomposition temperature in the thermal decomposition furnace 1 can be changed from 350 ° C. to 50 ° C.
Stable control is possible around 0 ° C.

【0038】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。
そして出口ライン18から取り出された高温の灰は前記
した灰溶融炉31に送給される。
On the other hand, 800 to 9 produced in the char combustion furnace 10.
A combustion gas having a high temperature of 50 ° C. and substantially containing no chlorine is introduced into a cyclone 16 through a combustion gas outlet line 15, dust and ash are separated and taken out from an outlet line 18, and exhaust gas is taken out from a gas outlet line 17. It is.
The high-temperature ash taken out of the outlet line 18 is sent to the ash melting furnace 31 described above.

【0039】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400〜550℃とすることができ、第1スー
パヒータボイラ蒸気出口28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 from the gas outlet line 17 of the cyclone 16 is introduced into the first super heater 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 if the surface temperature of the boiler tube is 350 ° C or higher, high temperature corrosion is significantly reduced. Therefore, the temperature of the fluid in the tube can be set to about 400 to 550 ° C., and high-temperature superheated steam can be stably obtained from the first superheater boiler steam outlet 28.

【0040】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 oxygen amount of the flowing gas supplied from the combustion exhaust 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 24, and a part of the fluidized sand at a high temperature of about 500 to 700 ° C. from the auxiliary char combustion means 10B is partially fed to the sand circulation line 5
It is supplied from and used as a heat source.

【0041】尚、11、3−1、3−2は分散板、2−
1、2−2、2−3は流動床である。
In addition, 11, 3-1, 3-2 are dispersion plates, 2-
1, 2-2 and 2-3 are fluidized beds.

【0042】さて図2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既に前記
実施例の説明で説明されているが、主に前記図1の実施
例との相違点を説明するに、前記熱分解炉1により得ら
れた熱分解ガスの一部を灰溶融炉31の上流側で、分岐
ライン7’を介して熱分解ガス燃焼炉34に供給するよ
うに構成している。即ち前記熱分解ガスや燃焼ガス中に
含まれる灰は、廃棄物に対し1割程度であり、従ってこ
れを供給される熱分解ガス全てを使用して溶融すること
は必ずしも必要なく、却って過剰設備の熱エネルギにな
ることを防止する。この為前記した熱分解ガス出口ライ
ン7の分岐された灰溶融炉31上流側若しくは分岐ライ
ン7’に前記図3に示す差圧計測手段100を配し、そ
の流量調整を行う必要がある。
FIG. 2 shows an apparatus for producing superheated steam using the heat of incineration of waste according to another embodiment of the present invention, which has already been explained in the explanation of the above-mentioned embodiment. To explain the difference from the example, a part of the pyrolysis gas obtained by the pyrolysis furnace 1 is supplied upstream of the ash melting furnace 31 to the pyrolysis gas combustion furnace 34 via a branch line 7 ′. It is configured to do. That is, the ash contained in the pyrolysis gas or combustion gas is about 10% of the waste, and therefore it is not always necessary to use all of the pyrolysis gas supplied to melt the ash. To prevent it from becoming heat energy. Therefore, it is necessary to arrange the differential pressure measuring means 100 shown in FIG. 3 on the upstream side of the ash melting furnace 31 where the pyrolysis gas outlet line 7 is branched or on the branch line 7 ′ to adjust the flow rate thereof.

【0043】[0043]

【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。又本発明によれば、前記いずれの蒸気製造装置
においても、長期に亙って安定して蒸気の製造を可能に
する。又本発明によれば、前記熱分解ガス若しくは燃焼
ガスを分離して得られた灰を溶融して骨材等の製造が可
能となる。等の種々の著効を有す。
As described above, according to the present invention, when the waste is burned to obtain the superheated steam without using the expensive high-grade material, the high temperature and high pressure of the boiler tube are prevented while preventing the high temperature corrosion of the boiler tube due to chlorine. Superheated steam can be obtained efficiently. Further, according to the present invention, any of the above-mentioned steam production apparatuses enables stable production of steam over a long period of time. Further, according to the present invention, it is possible to melt the ash obtained by separating the pyrolysis gas or the combustion gas to produce an aggregate or the like. And so on.

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

【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 a superheated steam manufacturing apparatus using heat of incineration of waste according to a second embodiment of the present invention.

【図3】図3は熱分解ガス出口ラインに配設した差圧計
測手段で、(A)はオリフィスを用いて形成した差圧計
測手段、(B)はラッパ状絞りを用いて形成した差圧計
測手段である。
FIG. 3 is a differential pressure measuring means arranged in a pyrolysis gas outlet line, (A) is a differential pressure measuring means formed by using an orifice, and (B) is a differential pressure measuring means formed by using a trumpet-shaped diaphragm. It is a pressure measuring means.

【図4】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. 4 is a graph showing a procedure for producing superheated steam using waste heat of incineration according to the basic configuration of the present invention.

【図5】本発明の第3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. 5 is a system diagram showing an apparatus for producing superheated steam using incineration heat of waste according to a third embodiment of the present invention.

【符号の説明】[Explanation of symbols]

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) 31 灰溶融炉 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) 1 Pyrolysis Furnace (Pyrolysis Means) 10 Combustion Furnace (Char Combustion Means) 11 Dispersion Plate 20 First Superheater (Second Steam Manufacturing Means) 29-1 Second Superheater (Second Steam Manufacturing Means) 20-2 3 Super Heater (Second Steam Production Means) 24 First Boiler (First Steam Production Means) 31 Ash Melting Furnace 34 Pyrolysis Gas Combustion Furnace 36 Water Cooled Wall Boiler (First Steam Production Means)

フロントページの続き (51)Int.Cl.6 識別記号 庁内整理番号 FI 技術表示箇所 F23G 5/48 ZAB F23G 5/48 ZAB F23J 1/00 F23J 1/00 B Front page continuation (51) Int.Cl. 6 Identification number Office reference number FI Technical display location F23G 5/48 ZAB F23G 5/48 ZAB F23J 1/00 F23J 1/00 B

Claims (4)

【特許請求の範囲】[Claims] 【請求項1】 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、 前記熱分解手段と第1の蒸気製造手段との間に、前記熱
分解ガスの第1次燃焼熱により、チャー燃焼手段若しく
は熱分解手段より取り出された夫々のガスより分離され
た灰分の溶融分離を行う灰分溶融分離手段を設けるとと
もに、好ましくは前記灰分が分離された熱分解ガスの2
次燃焼を行う2次燃焼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. A waste material is supplied into a space having a temperature of 300 ° C. or higher to cause a pyrolysis reaction, and a pyrolysis gas generated by the reaction, a char mixture composed of an undecomposed residue and a fluid medium and an incombustible material are separated. Thermal decomposition means for separating from each other, char combustion means for combusting the undecomposed residue while flowing a char mixture consisting of the undecomposed residue and the fluidized medium taken out by the thermal decomposition means with air, and the thermally decomposed gas About 400 using the combustion heat energy of
A first steam producing means for producing hot water or steam having a temperature of not higher than 0 ° C .; and a second steam producing means for superheating the hot water or steam produced by the first steam producing means by the heat energy obtained by the char combustion means. Including steam producing means, and separating the respective gases taken out from the char combustion means or the pyrolytic means by the primary combustion heat of the pyrolytic gas between the pyrolytic means and the first vapor producing means. An ash-melting / separating means for melting and separating the separated ash is provided, and preferably 2 ash of the pyrolysis gas from which the ash is separated is provided.
A superheated steam manufacturing apparatus utilizing the heat of incineration of waste, which is provided with a secondary combustion means for performing a secondary combustion.
【請求項2】 前記熱分解手段により得られた熱分解ガ
スを灰分溶融分離手段とともに、その一部を分岐して前
記2次燃焼手段に供給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 waste according to claim 1, wherein the pyrolysis gas obtained by the pyrolysis means is supplied to the secondary combustion means together with the ash melting and separating means and a part of the gas is branched. Superheated steam production equipment that uses the heat of incineration.
【請求項3】 温度300℃以上の酸素過小空間内に廃
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を2次燃焼手段若しくは熱交換手段
に供給するため熱分解ガス出口経路中に絞り部を設け、
該絞り部の入口側と出口側に夫々設けた圧力取り出し口
に少量の空気(支燃性ガスを含む気体)を適宜流す空気
流入手段を設けて差圧を計測して熱分解ガスの流量を計
測する事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. Heat is supplied to a secondary combustion means or a heat exchange means by supplying waste to an under-oxygenated space having a temperature of 300 ° C. or higher to cause a thermal decomposition reaction, and thermally decomposing gas generated by the reaction. A throttling part is provided in the decomposition gas outlet path,
An air inflow means for appropriately flowing a small amount of air (gas containing a combustion-supporting gas) is provided at the pressure outlets provided on the inlet side and the outlet side of the throttle portion to measure the differential pressure to measure the flow rate of the pyrolysis gas. A superheated steam manufacturing device that uses the heat of incineration of waste, which is characterized by measuring.
【請求項4】 前記熱分解手段により得られた熱分解ガ
スの一部を分岐して熱分解手段の入口側に供給すること
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。
4. The heat of incineration of waste according to claim 1, wherein a part of the pyrolysis gas obtained by the pyrolysis means is branched and supplied to the inlet side of the pyrolysis means. Superheated steam production equipment.
JP06909096A 1996-02-29 1996-02-29 Superheated steam production equipment using waste incineration heat Expired - Fee Related JP3285752B2 (en)

Priority Applications (7)

Application Number Priority Date Filing Date Title
JP06909096A JP3285752B2 (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
JP06909096A JP3285752B2 (en) 1996-02-29 1996-02-29 Superheated steam production equipment using waste incineration heat

Publications (2)

Publication Number Publication Date
JPH09236221A true JPH09236221A (en) 1997-09-09
JP3285752B2 JP3285752B2 (en) 2002-05-27

Family

ID=13392559

Family Applications (1)

Application Number Title Priority Date Filing Date
JP06909096A Expired - Fee Related JP3285752B2 (en) 1996-02-29 1996-02-29 Superheated steam production equipment using waste incineration heat

Country Status (1)

Country Link
JP (1) JP3285752B2 (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH11248121A (en) * 1998-03-02 1999-09-14 Ishikawajima Harima Heavy Ind Co Ltd Municipal refuse incinerator and its operation method

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH11248121A (en) * 1998-03-02 1999-09-14 Ishikawajima Harima Heavy Ind Co Ltd Municipal refuse incinerator and its operation method

Also Published As

Publication number Publication date
JP3285752B2 (en) 2002-05-27

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