JP3074617B2 - Superheated steam generation method and device by refuse incineration - Google Patents

Superheated steam generation method and device by refuse incineration

Info

Publication number
JP3074617B2
JP3074617B2 JP07234794A JP23479495A JP3074617B2 JP 3074617 B2 JP3074617 B2 JP 3074617B2 JP 07234794 A JP07234794 A JP 07234794A JP 23479495 A JP23479495 A JP 23479495A JP 3074617 B2 JP3074617 B2 JP 3074617B2
Authority
JP
Japan
Prior art keywords
char
superheated steam
refuse
fluidized bed
combustion
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
Application number
JP07234794A
Other languages
Japanese (ja)
Other versions
JPH0960847A (en
Inventor
香津雄 堤
康史 榊田
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.)
Kawasaki Motors Ltd
Original Assignee
Kawasaki Jukogyo KK
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
Application filed by Kawasaki Jukogyo KK filed Critical Kawasaki Jukogyo KK
Priority to JP07234794A priority Critical patent/JP3074617B2/en
Publication of JPH0960847A publication Critical patent/JPH0960847A/en
Application granted granted Critical
Publication of JP3074617B2 publication Critical patent/JP3074617B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

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Classifications

    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02EREDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
    • Y02E50/00Technologies for the production of fuel of non-fossil origin
    • Y02E50/30Fuel from waste, e.g. synthetic alcohol or diesel

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、塩素化合物を含む
ごみの焼却による過熱蒸気発生方法及び装置、詳しく
は、脱塩剤を用いることなく、ごみを不完全燃焼させ
て、ごみの一部をチャーにするとともに、このチャーに
含まれる灰に塩素分を固定化させ、このチャーを燃焼さ
せてHCl濃度のきわめて少ない燃焼ガスを発生させ、
このガスで過熱蒸気を発生させる方法及び装置に関する
ものである。なお、チャーは水分を含んでいないので、
チャーを低温で燃焼させれば、燃焼ガス中にHClはほ
とんど含まれない。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method and an apparatus for generating superheated steam by incinerating refuse containing chlorine compounds. More specifically, the present invention relates to a method for incompletely burning refuse without using a desalinating agent to remove a part of the refuse. Along with the char, the chlorine contained in the ash contained in the char is fixed, and the char is burned to generate a combustion gas having an extremely low HCl concentration.
The present invention relates to a method and an apparatus for generating superheated steam with this gas. Since the char does not contain moisture,
If the char is burned at a low temperature, the combustion gas contains almost no HCl.

【0002】[0002]

【従来の技術】ごみを過剰空気で燃焼させると、ごみ中
の塩化ビニール、食塩などの塩素化合物中のClと水分
中のHとが反応してHClガスとなって、排ガス中に含
まれるようになり、このHClガスが熱交換器などを腐
食させるという問題がある。このため、従来から、ごみ
を450〜550℃の低温で燃焼させ、その中へCa
O、CaCO3 、Ca(OH)2 、Na2 CO3 などを
入れて、CaO+2HCl→CaCl2 +H2 Oの反応
などを起こさせて燃焼ガスからHClをCaCl2 とし
て取り除く方法が知られている(例えば、特開平6−2
01114号公報参照)。従来の方法では、1500pp
m のHClを含む排ガスを排出するごみを、流動層で燃
焼させ、その中にCaOなどを投入すると、550℃で
100ppm 程度にまで脱塩される。
2. Description of the Related Art When refuse is burned with excess air, Cl in chlorine compounds such as vinyl chloride and salt in the refuse reacts with H in moisture to form HCl gas, which is contained in the exhaust gas. Therefore, there is a problem that the HCl gas corrodes a heat exchanger and the like. For this reason, conventionally, refuse is burned at a low temperature of 450 to 550 ° C.
A method is known in which O, CaCO 3 , Ca (OH) 2 , Na 2 CO 3, etc. are added to cause a reaction such as CaO + 2HCl → CaCl 2 + H 2 O to remove HCl as CaCl 2 from the combustion gas ( For example, JP-A-6-2
01114). In the conventional method, 1500pp
The refuse which discharges the exhaust gas containing HCl of m 2 is burned in a fluidized bed, and CaO or the like is charged into the refuse to desalinate to about 100 ppm at 550 ° C.

【0003】[0003]

【発明が解決しようとする課題】上記のように、従来の
方法では、脱塩剤としてCaO、CaCO3 、Ca(O
H)2 、Na2 CO3 などを必要とするので、メンテナ
ンスコストがかかる。また、反応を起こさせるために低
温燃焼を余儀なくされ、燃焼効率が低いという問題があ
る。本発明者は、上記の問題点を解決するために、種々
の実験、研究を重ねた結果、ごみを不完全燃焼(空気不
足や低温燃焼)させることにより、ごみの一部をチャー
にすると、このチャーの中にも塩素分は含まれている
が、水分がないので、チャーを低温で燃焼させた場合
は、燃焼ガス中にHClはほとんど含まれないことを見
い出した。また、空気を必要空気量以下(空気比1以
下)しか投入せず、ごみのガス化反応(部分燃焼、還元
燃焼)を起こさせると、ごみ中のClはHClに転換せ
ず、NaCl、KCl、CaCl 2 等の塩化物となって
灰の中に残留することを見い出した。
As described above, in the conventional method, CaO, CaCO 3 , Ca (O
H) 2 , Na 2 CO 3, etc. are required, so maintenance costs are incurred. Further, there is a problem that low-temperature combustion is inevitable in order to cause a reaction, and combustion efficiency is low. The present inventor, in order to solve the above problems, as a result of repeated experiments and research, as a result of incomplete combustion (lack of air or low-temperature combustion) of the garbage, when some of the garbage is char, This char also contains chlorine, but since there is no moisture, it was found that when the char was burned at a low temperature, HCl was hardly contained in the combustion gas. In addition, when air is injected only in a required air amount or less (air ratio is 1 or less) and a gasification reaction (partial combustion, reduction combustion) of the garbage is caused, Cl in the garbage is not converted into HCl, and NaCl, KCl , CaCl 2, etc., and remained in the ash.

【0004】本発明は、上記の知見に基づいてなされた
もので、本発明の目的は、ごみを不完全燃焼させること
によって、ごみの一部を塩素分を含むチャーにし、この
チャーを燃焼させて、熱交換器の腐食を生じさせること
なく、高温蒸気を発生させることにある。
[0004] The present invention has been made based on the above findings, and an object of the present invention is to partially burn refuse into char containing chlorine and burn the char by burning the refuse incompletely. To generate high-temperature steam without causing corrosion of the heat exchanger.

【0005】[0005]

【課題を解決するための手段】上記の目的を達成するた
めに、本発明のごみ焼却による過熱蒸気発生方法は、塩
素化合物を含むごみをごみ焼却炉で不完全燃焼させるこ
とにより、ごみの一部をチャーにしてチャーに含まれる
灰に塩素分を固定化させるとともに、塩化水素濃度の少
ない可燃性ガスを得、前記チャーをチャー燃焼炉で低温
燃焼させて塩化水素濃度の少ない燃焼ガスを発生さ
せ、この燃焼ガスで過熱蒸気を発生させるように構成さ
れる。不完全燃焼は、空気比0.25〜0.95、望ま
しくは0.5〜0.7の範囲で部分燃焼させるか、又は
/及び500〜750℃、望ましくは550〜700℃
の範囲で低温燃焼させることにより行われる。空気比が
上記の範囲未満の場合は、ガス化反応が不十分で、流動
層温度も低くなるという不都合があり、一方、上記の範
囲を超える場合は、チャーの生成量が減り、過熱に必要
な熱量以下となる不都合がある。また、不完全燃焼温度
が上記の範囲未満の場合は、チャー生成が不十分で、水
素分を含むチャーとなる不都合があり、一方、上記の範
囲を超える場合は、チャーの炭素結晶化(グラファイト
化)がすすみ、難燃性のチャーとなる不都合がある。
In order to achieve the above object, a method for generating superheated steam by incineration of refuse according to the present invention comprises the steps of incompletely burning refuse containing chlorine compounds in a refuse incinerator to reduce waste. Part of the char and included in the char
The chlorine content is fixed to the ash and the hydrogen chloride concentration is low.
Give no combustible gas, a low temperature the char in the char combustion furnace
In by burning of generating less combustion gas having hydrogen chloride concentration
The combustion gas is configured to generate superheated steam. The incomplete combustion is partially burned in an air ratio of 0.25 to 0.95, preferably 0.5 to 0.7 or / and 500 to 750 ° C, preferably 550 to 700 ° C.
By performing low temperature combustion in the range of When the air ratio is less than the above range, there is a disadvantage that the gasification reaction is insufficient and the temperature of the fluidized bed is lowered. There is an inconvenience that the heat amount is not more than a large amount. When the incomplete combustion temperature is lower than the above range, char formation is insufficient, and there is a disadvantage that the char contains hydrogen. On the other hand, when the temperature exceeds the above range, carbon crystallization (graphite) of the char may occur. Has the disadvantage of becoming flame-retardant char.

【0006】ごみ焼却及びチャー燃焼をロータリーキル
ン式炉やストーカ式炉で行ってもよいが、流動層炉で行
うことがより好ましい。また、ごみ焼却炉の流動層温度
を500〜750℃、望ましくは550〜700℃の範
囲に制御する方法は、空気比を小さくしたり、流動層内
に伝熱管を入れたり、流動層内に水を注入して冷却する
方法が採用される。なお、流動層を冷却しない場合は、
流動層温度が750℃以上にまで上昇してしまうので好
ましくない。
The waste incineration and char combustion may be carried out in a rotary kiln furnace or stoker furnace, but more preferably in a fluidized bed furnace. In addition, the method of controlling the temperature of the fluidized bed of the refuse incinerator to 500 to 750 ° C., preferably 550 to 700 ° C. reduces the air ratio, puts a heat transfer tube in the fluidized bed, A method of injecting water and cooling is adopted. If the fluidized bed is not cooled,
It is not preferable because the temperature of the fluidized bed rises to 750 ° C. or more.

【0007】本発明のごみ焼却による過熱蒸気発生装置
は、塩素化合物を含むごみを不完全燃焼させる流動層ご
み焼却炉と、このごみ焼却炉の流動層から不完全燃焼物
を抜き出して大塊不燃物と灰中に塩素分が固定化された
チャーとに分級する分級機と、このごみ焼却炉からのチ
ャーを含む可燃性ガスを導入して灰中に塩素分が固定化
されたチャーと塩化水素濃度の少ない可燃性ガスとを分
離するダスト分離器と、このダスト分離器及び前記分級
機からのチャーを低温で燃焼させて塩化水素濃度の少な
い燃焼ガスを発生させる流動層チャー燃焼炉と、このチ
ャー燃焼炉の流動層内に設けられた過熱蒸気発生管と、
からなることを特徴としている。上記の装置において、
過熱蒸気発生管をチャー燃焼炉の流動層内に設ける代り
に、チャー燃焼炉のフリーボードに設けることも可能で
ある。
[0007] A superheated steam generator for incineration of waste according to the present invention comprises a fluidized bed incinerator for incompletely burning waste containing chlorine compounds, and an incompletely combusted material extracted from the fluidized bed of the incinerator for large incombustibility. objects and the chlorine content in the ash immobilized <br/> char and secondary classification to classifier, chlorine is immobilized in the ash by introducing a combustible gas containing char from the incinerators
A dust separator which is char and separating the less inflammable gases hydrogen chloride concentration, low hydrogen chloride concentration char from the dust separator and the classifier is burned at a low temperature
A fluidized bed char combustion furnace Ru to generate combustion gases have a superheated steam generation tube provided in the fluidized bed of the char combustion furnace,
It is characterized by consisting of. In the above device,
Instead of providing the superheated steam generation tube in the fluidized bed of the char combustion furnace, it is also possible to provide it on a free board of the char combustion furnace.

【0008】[0008]

【発明の実施の形態】図1は本発明のごみ焼却による過
熱蒸気発生方法を実施する装置の一例を示している。本
例は、ごみ焼却炉10及びチャー燃焼炉12として流動
層炉を用いる場合は示している。流動層14は灰と珪砂
が流動媒体となっており、この流動層14にごみが投入
され不完全燃焼される。16はごみホッパーである。風
箱18に空気比0.25〜0.95、望ましくは0.5
〜0.7の範囲の空気を供給し、空気分散板20を通し
て流動層14内に分散・噴出させて流動媒体を流動化さ
せるとともに、流動層内に伝熱管を設けて熱回収する
か、又は流動層内に注水することにより、流動層温度を
500〜750℃、望ましくは550〜700℃の範囲
に制御する。灰中のNa2 O、K2 Oなどの酸化アルカ
リ金属、CaOなどの酸化アルカリ土類金属などがごみ
中のClと反応して、NaCl、KCl、CaCl2
どの塩化物となって固定化されてチャー中に含まれ、可
燃性ガス中のHClは大幅に減少する。この可燃性ガス
中には、Clを含むダスト(チャー)及び少量のHCl
が含有されることになる。
DESCRIPTION OF THE PREFERRED EMBODIMENTS FIG. 1 shows an example of an apparatus for carrying out a method for generating superheated steam by incineration of waste according to the present invention. This example shows a case where a fluidized bed furnace is used as the refuse incinerator 10 and the char combustion furnace 12. The fluidized bed 14 is made of ash and silica sand as a fluidized medium, and refuse is injected into the fluidized bed 14 and incompletely burned. 16 is a garbage hopper. An air ratio of 0.25 to 0.95, preferably 0.5
The air in the range of ~ 0.7 is supplied and dispersed and ejected into the fluidized bed 14 through the air dispersion plate 20 to fluidize the fluidized medium, and a heat transfer tube is provided in the fluidized bed to recover heat, or By pouring water into the fluidized bed, the temperature of the fluidized bed is controlled in the range of 500 to 750 ° C, preferably 550 to 700 ° C. Alkali metal oxides such as Na 2 O and K 2 O in ash and alkaline earth metal oxides such as CaO react with Cl in garbage to be fixed as chlorides such as NaCl, KCl and CaCl 2 . The HCl contained in the char is greatly reduced in the combustible gas. This combustible gas contains dust (char) containing Cl and a small amount of HCl.
Will be contained.

【0009】Clが固定化された灰を含むチャーは、大
塊不燃物とともに流動層14から抜き出され、振動篩な
どの分級機22で大塊不燃物と、Clが固定化された灰
を含むチャーとに分級され、このチャーはチャーホッパ
ー24を経てブロワ26からの空気でチャー燃焼炉12
の流動層28に気流搬送されて燃焼される。30は排出
機、32は風箱、34は空気分散板である。ごみ焼却炉
10の流動層14からの可燃性ガスはフリーボード36
を通過して、サイクロンなどのダスト分離器38に導入
され、ここでClを10%前後含む灰を含有するチャー
と可燃性ガスとが分離される。可燃性ガスにはCO、H
2 などが含まれる。可燃性ガスには、さらにCH3 、C
2 6 などが含まれることもある。この可燃性ガスは、
HCl濃度がきわめて少ないので、他の燃焼炉又は燃焼
器(図示略)で燃焼させた後、ボイラ又はタービン(図
示略)に送り込まれて、熱回収又は動力回収がなされ
る。
The char containing ash having Cl immobilized thereon is extracted from the fluidized bed 14 together with the large incombustible material, and the large incombustible material and the ash having Cl immobilized thereon are separated by a classifier 22 such as a vibrating sieve. The char is divided into the char and the char combustion furnace 12 by the air from the blower 26 through the char hopper 24.
Is transported by airflow to the fluidized bed 28 and burned. Reference numeral 30 denotes a discharger, 32 denotes a wind box, and 34 denotes an air distribution plate. The combustible gas from the fluidized bed 14 of the refuse incinerator 10 is supplied to a free board 36.
, And is introduced into a dust separator 38 such as a cyclone, where char containing ash containing about 10% Cl and combustible gas are separated. Combustible gas includes CO, H
2 etc. are included. Combustible gases further include CH 3 and C
2 H 6 and the like may be included. This flammable gas is
Since the HCl concentration is extremely low, it is burned in another combustion furnace or combustor (not shown) and then sent to a boiler or turbine (not shown) to recover heat or power.

【0010】ダスト分離器38で分離されたClを含む
灰を含有するダスト(チャー)は、チャー燃焼炉12の
流動層28へ供給されて燃焼される。この流動層28内
には過熱蒸気発生管40が設けられており、例えば、4
50℃前後の水蒸気が供給されて600℃前後の高温の
過熱蒸気が発生するように構成されている。なお、流動
層28の温度は800℃前後である。流動層28へ供給
されるチャー中には塩素分が含まれているが、水分は含
まれておらず、低温で燃焼すると、CaCl2 +H2
→2HCl+CaOなどの反応は生じず、燃焼ガス中に
HClは殆ど含まれない。この燃焼ガスはフリーボード
42を通過してサイクロンなどのダスト分離器44へ導
入されてダストが除去された後、系外へ排出される。
The dust (char) containing ash containing Cl separated in the dust separator 38 is supplied to the fluidized bed 28 of the char combustion furnace 12 and burned. A superheated steam generating tube 40 is provided in the fluidized bed 28, for example, 4
It is configured such that steam of about 50 ° C. is supplied to generate high-temperature superheated steam of about 600 ° C. The temperature of the fluidized bed 28 is around 800 ° C. The char supplied to the fluidized bed 28 contains chlorine, but does not contain moisture, and when burned at a low temperature, CaCl 2 + H 2 O
→ No reaction such as 2HCl + CaO occurs and HCl is hardly contained in the combustion gas. This combustion gas passes through the free board 42 and is introduced into a dust separator 44 such as a cyclone to remove dust, and then discharged outside the system.

【0011】図1では、過熱蒸気発生管を流動層内に設
ける場合について説明したが、図2に示すように、過熱
蒸気発生管40aをフリーボード42に設けることも可
能である。
In FIG. 1, the case where the superheated steam generation pipe is provided in the fluidized bed has been described. However, as shown in FIG. 2, the superheated steam generation pipe 40a can be provided in the free board 42.

【0012】[0012]

【実施例】【Example】

実施例1 図1に示す装置を用いて、Cl10wt%を含むごみを焼
却した。このごみをごみ焼却炉10の流動層14で、空
気比λ=0.6、流動層14温度700℃(流動層14
内に伝熱管を設け、この伝熱管に水を通すことにより制
御した)の条件で不完全燃焼させると、発熱量約400
0kcal/kgのダスト(チャー)がサイクロン38で捕集
された。このチャーをチャー燃焼炉12の流動層28で
700℃で燃焼させ、450℃の水蒸気を600℃の過
熱水蒸気にすることができた。燃焼ガス中のHCl濃度
は20ppm であった。また、ごみ焼却炉出口のサイクロ
ンからの可燃性ガス(740℃)中のHCl濃度は20
ppm であった。
Example 1 Using the apparatus shown in FIG. 1, refuse containing 10 wt% of Cl was incinerated. The refuse is treated in the fluidized bed 14 of the refuse incinerator 10 with an air ratio λ = 0.6, a fluidized bed 14 temperature of 700 ° C.
A heat transfer tube was provided inside the heat transfer tube and water was passed through the heat transfer tube.)
0 kcal / kg of dust (char) was collected in cyclone 38. This char was burned at 700 ° C. in the fluidized bed 28 of the char combustion furnace 12 to convert 450 ° C. steam into 600 ° C. superheated steam. The HCl concentration in the combustion gas was 20 ppm. The HCl concentration in the combustible gas (740 ° C.) from the cyclone at the waste incinerator outlet is 20%.
ppm.

【0013】[0013]

【発明の効果】本発明は上記のように構成されているの
で、つぎのような効果を奏する。 (1) 脱塩剤を用いることなく、ごみを不完全燃焼さ
せてごみの一部をチャーにするとともに、このチャーに
含まれる灰に塩素分を固定化させ、このチャーを燃焼さ
せてHCl濃度のきわめて少ない燃焼ガスを発生させ、
この燃焼ガスで伝熱管を加熱して過熱蒸気を発生させる
ので、過熱蒸気発生管などの伝熱管の腐食を大幅に軽減
することができる。 (2) 脱塩剤を用いることなく、ごみを不完全燃焼さ
せると同時にHClをきわめて少量しか含まない可燃性
ガスを得ることができ、この可燃性ガスを再度燃焼させ
て、ボイラやタービンなどにガスを送り込むことによ
り、ボイラやタービンの腐食を抑制しつつ、熱回収又は
動力回収を行うことができる。
As described above, the present invention has the following effects. (1) Without using a desalinating agent, incomplete combustion of garbage to make a part of the garbage into char, fix the chlorine content in ash contained in this char, burn this char, and burn HCl Generates very little combustion gas,
Since the heat transfer tube is heated by this combustion gas to generate superheated steam, corrosion of the heat transfer tube such as the superheated steam generation tube can be significantly reduced. (2) It is possible to obtain flammable gas containing only a very small amount of HCl at the same time as incompletely burning garbage without using a desalinating agent. This flammable gas is burned again and used for boilers and turbines. By feeding gas, heat recovery or power recovery can be performed while suppressing corrosion of the boiler or turbine.

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

【図1】本発明のごみ焼却による過熱蒸気発生方法を実
施する装置の一例を示す系統図である。
FIG. 1 is a system diagram showing an example of an apparatus for implementing a method for generating superheated steam by incineration of waste according to the present invention.

【図2】本発明の方法を実施する装置の他の例を示す系
統図である。
FIG. 2 is a system diagram showing another example of an apparatus for performing the method of the present invention.

【符号の説明】[Explanation of symbols]

10 ごみ焼却炉 12 チャー燃焼炉 14 流動層 16 ごみホッパー 18 風箱 20 空気分散板 22 分級機 24 チャーホッパー 26 ブロワ 28 流動層 30 排出機 32 風箱 34 空気分散板 36 フリーボード 38 ダスト分離器 40 過熱蒸気発生管 40a 過熱蒸気発生管 42 フリーボード 44 ダスト分離器 Reference Signs List 10 refuse incinerator 12 char combustion furnace 14 fluidized bed 16 refuse hopper 18 wind box 20 air dispersion plate 22 classifier 24 char hopper 26 blower 28 fluidized bed 30 discharger 32 wind box 34 air dispersion plate 36 free board 38 dust separator 40 Superheated steam generation pipe 40a Superheated steam generation pipe 42 Free board 44 Dust separator

───────────────────────────────────────────────────── フロントページの続き (51)Int.Cl.7 識別記号 FI F23G 5/14 ZAB B09B 3/00 ZAB F27B 15/00 303F (56)参考文献 特開 平5−93513(JP,A) 特開 平6−265121(JP,A) 特開 平7−71735(JP,A) 特開 平7−35322(JP,A) 実開 昭60−148830(JP,U) (58)調査した分野(Int.Cl.7,DB名) F23G 7/00 B09B 3/00 F23G 5/027 F23G 5/14 F27B 15/00 F23G 5/30 F23C 11/02 ────────────────────────────────────────────────── ─── Continuation of the front page (51) Int.Cl. 7 Identification code FIF23G 5/14 ZAB B09B 3/00 ZAB F27B 15/00 303F (56) References JP-A-5-93513 (JP, A) JP-A-6-265121 (JP, A) JP-A-7-71735 (JP, A) JP-A-7-35322 (JP, A) JP-A-60-148830 (JP, U) (58) Int.Cl. 7 , DB name) F23G 7/00 B09B 3/00 F23G 5/027 F23G 5/14 F27B 15/00 F23G 5/30 F23C 11/02

Claims (5)

(57)【特許請求の範囲】(57) [Claims] 【請求項1】 塩素化合物を含むごみをごみ焼却炉で不
完全燃焼させることにより、ごみの一部をチャーにし
チャーに含まれる灰に塩素分を固定化させるとともに、
塩化水素濃度の少ない可燃性ガスを得、前記チャーをチ
ャー燃焼炉で低温で燃焼させて塩化水素濃度の少ない燃
焼ガスを発生させ、この燃焼ガスで過熱蒸気を発生させ
ることを特徴とするごみ焼却による過熱蒸気発生方法。
Claims: 1. Incomplete combustion of waste containing chlorine compounds in a waste incinerator to turn part of the waste into char
While immobilizing chlorine in the ash contained in the char,
A flammable gas having a low hydrogen chloride concentration is obtained, and the char is burned at a low temperature in a char combustion furnace to produce a fuel having a low hydrogen chloride concentration.
A method for generating superheated steam by incineration of refuse, comprising generating a combustion gas and generating superheated steam with the combustion gas .
【請求項2】 不完全燃焼を、空気比0.25〜0.9
5の範囲で部分燃焼させるか、又は/及び500〜75
0℃の範囲で低温燃焼させることにより行う請求項1記
載のごみ焼却による過熱蒸気発生方法。
2. The method according to claim 1, wherein the incomplete combustion is performed at an air ratio of 0.25 to 0.9.
Partial combustion in the range of 5 or / and 500-75
The method for generating superheated steam by incineration of refuse according to claim 1, wherein the method is carried out by burning at a low temperature within a range of 0 ° C.
【請求項3】 ごみ焼却及びチャー燃焼を流動層で行う
請求項1又は2記載のごみ焼却による過熱蒸気発生方
法。
3. The method for generating superheated steam by incineration of refuse according to claim 1, wherein refuse incineration and char combustion are performed in a fluidized bed.
【請求項4】 塩素化合物を含むごみを不完全燃焼させ
る流動層ごみ焼却炉と、 このごみ焼却炉の流動層から不完全燃焼物を抜き出して
大塊不燃物と灰中に塩素分が固定化されたチャーとに分
級する分級機と、 このごみ焼却炉からのチャーを含む可燃性ガスを導入し
灰中に塩素分が固定化されたチャーと塩化水素濃度の
少ない可燃性ガスとを分離するダスト分離器と、 このダスト分離器及び前記分級機からのチャーを低温で
燃焼させて塩化水素濃度の少ない燃焼ガスを発生させ
流動層チャー燃焼炉と、 このチャー燃焼炉の流動層内に設けられた過熱蒸気発生
管と、 からなることを特徴とするごみ焼却による過熱蒸気発生
装置。
4. A fluidized bed refuse incinerator for incompletely burning refuse containing chlorine compounds, and an incompletely burned substance is extracted from the fluidized bed of the refuse incinerator to fix chlorine in large incombustibles and ash. A classifier that classifies the char and the char whose chlorine content is fixed in the ash by introducing flammable gas containing char from the refuse incinerator and the hydrogen chloride concentration
A dust separator for separating a less flammable gases, the dust separator and fluidized bed char combustion furnace to the char from the classifier by <br/> burned at low temperatures Ru generates less combustion gas having a hydrogen chloride concentration And a superheated steam generation pipe provided in a fluidized bed of the char combustion furnace.
【請求項5】 過熱蒸気発生管をチャー燃焼炉の流動層
内に設ける代りに、チャー燃焼炉のフリーボードに設け
た請求項4記載のごみ焼却による過熱蒸気発生装置。
5. The superheated steam generator according to claim 4, wherein the superheated steam generation pipe is provided on a free board of the char combustion furnace instead of being provided in the fluidized bed of the char combustion furnace.
JP07234794A 1995-08-21 1995-08-21 Superheated steam generation method and device by refuse incineration Expired - Fee Related JP3074617B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP07234794A JP3074617B2 (en) 1995-08-21 1995-08-21 Superheated steam generation method and device by refuse incineration

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP07234794A JP3074617B2 (en) 1995-08-21 1995-08-21 Superheated steam generation method and device by refuse incineration

Publications (2)

Publication Number Publication Date
JPH0960847A JPH0960847A (en) 1997-03-04
JP3074617B2 true JP3074617B2 (en) 2000-08-07

Family

ID=16976503

Family Applications (1)

Application Number Title Priority Date Filing Date
JP07234794A Expired - Fee Related JP3074617B2 (en) 1995-08-21 1995-08-21 Superheated steam generation method and device by refuse incineration

Country Status (1)

Country Link
JP (1) JP3074617B2 (en)

Families Citing this family (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR100447009B1 (en) * 2000-05-24 2004-09-04 제이에프이 엔지니어링 가부시키가이샤 Treatment method of waste and apparatus thereof
KR20020027697A (en) * 2000-10-04 2002-04-15 김창길 a useless tire incinerator
JP6070580B2 (en) * 2014-01-14 2017-02-01 Jfeスチール株式会社 Method and system for reducing the molecular weight of organic substances

Also Published As

Publication number Publication date
JPH0960847A (en) 1997-03-04

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