JPS61293297A - Method of reforming combustible gas - Google Patents

Method of reforming combustible gas

Info

Publication number
JPS61293297A
JPS61293297A JP60134967A JP13496785A JPS61293297A JP S61293297 A JPS61293297 A JP S61293297A JP 60134967 A JP60134967 A JP 60134967A JP 13496785 A JP13496785 A JP 13496785A JP S61293297 A JPS61293297 A JP S61293297A
Authority
JP
Japan
Prior art keywords
gas
combustible gas
fed
air
waste
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Pending
Application number
JP60134967A
Other languages
Japanese (ja)
Inventor
Tokio Itasaka
板坂 時夫
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.)
TONAMI DENKI ENG KK
Original Assignee
TONAMI DENKI ENG 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 TONAMI DENKI ENG KK filed Critical TONAMI DENKI ENG KK
Priority to JP60134967A priority Critical patent/JPS61293297A/en
Publication of JPS61293297A publication Critical patent/JPS61293297A/en
Pending legal-status Critical Current

Links

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
    • 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
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W30/00Technologies for solid waste management
    • Y02W30/50Reuse, recycling or recovery technologies
    • Y02W30/78Recycling of wood or furniture waste

Abstract

PURPOSE:To obtain a high-quality gas with high efficiency, by feeding a high- temp. combustible gas produced in a waste treating a high-temp. combustible gas produced in a waste treating apparatus into the bottom of a vertical combustible gas reforming apparatus packed with a granular coke at the upper part of the bed equipped with a heat source. CONSTITUTION:A waste is stored on a roaster 30 provided within a vertical waste treating apparatus. Air is fed via primary and secondary gasifying air inlets 10, 5 while a fuel 9 is burnt with a burner 4 for gasification. The generated high-temp. combustible gas is fed to the bottom of a vertical combustible gas-refoming apparatus 15 via an outlet 6 and a duct 8. Carbon, tar, etc. contained in the gas are oxidized with the air fed through a nozzle 18 of an air pipe 16, and the gas is brought into contact with a granular coke 14 placed on a bed 13 preheated with a heater 12 to allow it to reduce, fed to a gas cooling tower 19 via an outlet 17 to allow it to rapidly cool, fed into a scrubbing tower 20, where it is scrubbed with an alkali to absorb and remove hydrogen chloride, SO2 gas, etc., and taken out of the system via an outlet pipe 21.

Description

【発明の詳細な説明】 〈産業上の利用分野〉 本発明は、可燃性ガスの改質方法に関し、更に詳細には
、廃棄物処理装置から生じ次回燃性ガスを良質化する可
燃性ガスの改質方法に関する。
[Detailed Description of the Invention] <Industrial Application Field> The present invention relates to a method for reforming combustible gas, and more particularly, to a method for reforming combustible gas, which improves the quality of combustible gas generated from waste treatment equipment. Regarding modification methods.

〈従来の技術〉 現代社会においては、各種の都市廃棄物や産業廃棄物が
激増し、これらの処理が重大問題となっている。これら
の都市廃棄物、産業廃棄物は、家庭から発生する雑芥、
プラスチック類、産業系から生ずる廃タイヤ、廃プラス
チック、廃紙、廃木材など多種多様であり、比較的高熱
量の優秀な熱源として利用する価値を有する物質である
から、単にこれらを焼却するのけ社会的損失が大きい。
<Conventional Technology> In modern society, the amount of various municipal wastes and industrial wastes has increased dramatically, and the treatment of these wastes has become a serious problem. These municipal wastes and industrial wastes include household garbage,
There are a wide variety of materials such as plastics, waste tires generated from industrial systems, waste plastics, waste paper, waste wood, etc., and because they have value as an excellent heat source with a relatively high calorific value, it is not enough to simply incinerate them. The social loss is large.

そこで、これらを燃料、熱源として利用することが種々
考えられている。しかしながら、これらを直接燃料とし
て、例えばゼイラ等産業用設備の熱源として用いると、
黒煙や有害ガスの発生等積々の弊害を生ずる。又、これ
らをそれぞれ単独に処理すると各種の専用処理施設が会
費となり、処理が極めて複雑、困難となる岬の事情があ
る。プラスチック、廃タイヤを例に取れば、直接燃焼す
れば高温となって装置の腐食を起したり、又黒煙を生じ
たり高##度の有害ガスが排ガス中に存在し几すするの
で、公害対策、環境保全の面から好ましくない。さらに
、これら廃棄物は、収集、搬入時に各種の廃棄物が雑然
と混在しており、これらの分離、選別等の作業が極めて
煩雑である上、これら混合廃棄物を完全に燃焼すること
は極めて困難で、通常の燃焼方法では不完全燃焼による
悪臭の発生、大量の排ガスの発生、未燃灰の発生等の問
題を生ずる。
Therefore, various attempts have been made to utilize these as fuel and heat sources. However, if these are used directly as fuel, for example as a heat source for industrial equipment such as Zeira,
This causes a number of negative effects such as the generation of black smoke and harmful gases. Furthermore, if each of these is treated individually, various dedicated treatment facilities will be required, making the treatment extremely complicated and difficult. For example, if plastics or waste tires are directly burned, they will reach high temperatures that will corrode equipment, produce black smoke, and contain highly toxic gases in the exhaust gas. Unfavorable from the standpoint of pollution control and environmental conservation. Furthermore, when these wastes are collected and delivered, various kinds of wastes are mixed together, and the work of separating and sorting them is extremely complicated, and it is extremely difficult to completely burn these mixed wastes. Conventional combustion methods cause problems such as the generation of bad odors due to incomplete combustion, the generation of large amounts of exhaust gas, and the generation of unburned ash.

このtめ、上記のような廃棄物を廃棄物処理装置で熱分
解、ガス化させ、この可燃性ガスを燃料として使用する
ことが行われている。
To this end, the above-mentioned wastes are thermally decomposed and gasified in waste treatment equipment, and the flammable gas is used as fuel.

〈発明が解決しようとする問題点〉 上記のように廃棄物処理装置から発生する可燃性ガスは
、配管を通じて炉等の燃焼装置に送られ、ノ々−ナー等
で燃焼せしめられるが、このガス中には通常lO〜30
 ?/Nm”のタール、遊離炭素が含まれており、管路
の閉塞やバーナー・ノズルの詰りを生ずる。このため、
遠隔配管や燃焼装置の保温、管理、保守に非常な手間を
要する上、種々のトラブルの原因となっていた。
<Problems to be solved by the invention> As mentioned above, the flammable gas generated from the waste treatment equipment is sent through piping to a combustion device such as a furnace and burned in a nozzle. Inside is usually lO~30
? /Nm” of tar and free carbon, which can clog pipes and burner nozzles.For this reason,
Insulating, managing, and maintaining remote piping and combustion equipment required a great deal of effort and caused various troubles.

本発明に、以上のような問題点を解消する友め、廃棄物
の熱分解、ガス化の過程を経て発生し次回燃性ガス中の
タール分や遊離炭素等を二次的に再度熱分解してガス化
畜せ、ガス中の炭酸ガス、水蒸気をコークス等と反応さ
せ、全体ガスの発熱量、品質を向上させてガスノ々−ナ
ーによる安定した燃焼全可能にすることを意図したもの
であり、可燃性ガスを精製して各稲の加熱熱源として有
効、適切に利用し得るようにする可燃性ガスの改質方法
を提供しようとするものである。
The present invention solves the above-mentioned problems by secondarily re-pyrolyzing the tar and free carbon in the combustible gas generated through the process of thermal decomposition and gasification of waste. The purpose is to make the carbon dioxide and water vapor in the gas react with coke, etc., to improve the calorific value and quality of the entire gas, and to enable stable combustion using a gas nozzle. The present invention aims to provide a method for reforming combustible gas that purifies the combustible gas so that it can be effectively and appropriately used as a heating heat source for various types of rice.

く問題点を解決するための手段〉 本発明の可燃性ガスの改質方法は、内部にベッドを有し
該ベッドに熱源を備えるとともにベッド上方に粒状コー
クスを充填した竪型可燃性ガス改質装置の下部より、廃
棄物処理装置において発生し次回燃性ガスを冷却するこ
となく高温の状態で送入して上向流として上昇せしめ、
前記熱源によりコークスを赤熱するとともに、ベッド下
方に配置され友ノズルより空気を供給することを特徴と
するものである。
Means for Solving Problems〉 The combustible gas reforming method of the present invention is a vertical combustible gas reforming method that has a bed inside, is equipped with a heat source, and is filled with granular coke above the bed. The next combustible gas generated in the waste treatment equipment is introduced from the bottom of the equipment in a high-temperature state without being cooled and rises as an upward flow.
The coke is heated red-hot by the heat source, and air is supplied from a companion nozzle located below the bed.

〈実施例〉 以下、図面に示した実施例により、本発明方法の構成を
更に詳細に説明する。
<Example> Hereinafter, the structure of the method of the present invention will be explained in more detail with reference to the example shown in the drawings.

第1図に本発明方法に使用される装置の一実施例の系統
説明図であり、本発明の可燃性ガスの改質方法は、廃棄
物処理装置Aにおいて廃棄物を処理して発生した可燃性
ガスを可燃性ガス改質装置Bに送入、通過せしめて改質
処理を行うものである。
FIG. 1 is a system explanatory diagram of one embodiment of the apparatus used in the method of the present invention. The combustible gas is sent to the combustible gas reformer B and passed therethrough for reforming treatment.

廃棄物処理装置へは、廃棄物貯留工程】とガス化反応工
程2と全連続的に行い得る竪型のタンクよりなるもので
、中間やや下部にガス化ロスドル30が設けられており
、このロスドル3o上に廃棄物が貯留される。ロスドル
30H図示しない駆動装置に工り随時揺動、摺動、転動
等の運動を行って廃棄物のガス化を助け、−次ガス化用
空気取入れ口10から廃棄物のガス化、熱分解に必要な
適量の空気を送り込まれてガス化が継続される。
The waste treatment equipment consists of a vertical tank that can carry out the waste storage process and the gasification reaction process 2 completely continuously. Waste is stored on 3o. The Rossdol 30H is equipped with a drive device (not shown) and performs movements such as rocking, sliding, and rolling at any time to assist in the gasification of waste, and then gasifies and thermally decomposes the waste through the air intake port 10 for gasification. Gasification continues by feeding the appropriate amount of air required.

又、二次ガス化用空気取入れ口5から必要量の二次ガス
化用空気を混入し、更にガス化を促進させる。
Further, a necessary amount of air for secondary gasification is mixed in from the air intake port 5 for secondary gasification to further promote gasification.

この逆煙燃焼、上述、下焚方式のガス化工程2において
、廃棄物は空気取入れ口10及び5からの空気により急
速Vr−酸化分解してガス化温度に達しガス化が完了す
る。この場合のガス化は、可燃性ガスを発生させる発生
炉ガス反応、水性ガス反応、及び熱分解生成物の生成で
ある。発生した可燃性ガスは、可燃性ガス出口6より高
温状態のまま可燃性ガス改質装置Bに送り出される。
In this reverse smoke combustion, the above-mentioned under-burning type gasification step 2, the waste is rapidly Vr-oxidized and decomposed by the air from the air intake ports 10 and 5, reaching the gasification temperature and completing the gasification. Gasification in this case is a producer gas reaction that generates combustible gases, a water gas reaction, and the production of pyrolysis products. The generated combustible gas is sent out from the combustible gas outlet 6 to the combustible gas reformer B in a high temperature state.

この廃棄物処理装置におけるスタート時の着火及び予熱
は、着火燃焼ノ々−ナー4を用い着火用燃料(主に都市
ガス、灯油等)9を燃焼させる。ガス化跡の残渣ilt
廃棄物残渣取出しロアより取り出される。
For ignition and preheating at the start of this waste treatment apparatus, an ignition fuel (mainly city gas, kerosene, etc.) 9 is combusted using an ignition combustion nozzle 4. Gasification residue ilt
It is taken out from the waste residue removal lower.

廃棄物処理装置Aにおいて発生するガスは、通常の場合
、廃棄物の不均質性、形状の不定等による燃焼速度の不
均一のためカーゼン、炭酸ガス、水蒸気などを含んで汚
れガスと称され、発熱量も変動し、火炎伝播速度も異な
り、これを燃料として使用する場合、使用条件に種々制
約を受けることとなる。
The gas generated in the waste treatment equipment A is usually called a dirty gas because it contains carbon dioxide, carbon dioxide, water vapor, etc. due to the non-uniform combustion rate due to the non-uniformity of the waste and the irregular shape of the waste. The calorific value varies, the flame propagation speed also varies, and when using this as a fuel, there are various restrictions on usage conditions.

上記ガス化工程2から生ずる高温可燃性汚れガスを可燃
性ガスダクト8を通じて可燃性ガス改質装置Bに送入す
る。この可燃性ガス改質装[Bの目的ニ、タール、カー
ぜンのガス化、炭酸ガス、水蒸気の還元反応による可燃
ガス化を主とし、硫化水素やアンモニア、塩化水素等の
有害物質の還元、酸化をも考慮したものである。
The high temperature combustible dirty gas generated from the gasification step 2 is fed into the combustible gas reformer B through the combustible gas duct 8. This flammable gas reforming system [Purpose of B (2) mainly involves the gasification of tar, carbon dioxide, and combustible gasification through the reduction reaction of carbon dioxide and water vapor, and the reduction of harmful substances such as hydrogen sulfide, ammonia, and hydrogen chloride. , oxidation is also taken into account.

竪型タンク状のガス改質塔15よりなる可燃性ガス改質
装#Bの下部に設けられた可燃性ガスλ口11より導入
されt可燃性ガスは、ガス改質用空気管16より取シ込
まれfc極く少量の酸化剤としての空気により、カーゼ
ン、タール類の酸化を促進される。前記空気管16の上
方には熱源ヒーター12が設けられており、更にその上
方にペッドI3が設けられ、ベッド13上に粒状コーク
スが充填されている。熱源ヒーター12はスタート時予
熱を行い、可燃性ガス改質装置Bを600〜700℃以
上に保つとともに、ベッド13上のコークス充填層14
を予熱、加熱し、還元反応が迅速に行えるようにする。
The combustible gas introduced from the flammable gas λ port 11 provided at the bottom of the flammable gas reforming system #B consisting of the vertical tank-shaped gas reforming tower 15 is taken out from the gas reforming air pipe 16. The oxidation of carzene and tars is promoted by a very small amount of air as an oxidizing agent. A heat source heater 12 is provided above the air pipe 16, a ped I3 is provided above the ped I3, and a bed 13 is filled with granular coke. The heat source heater 12 preheats the combustible gas reformer B at a temperature of 600 to 700°C or higher at the start, and also heats the coke packed bed 14 on the bed 13.
Preheat and heat so that the reduction reaction can occur quickly.

ガス改質塔15上部の改質可燃性ガス出口17より出友
可燃性ガスに、ガス冷却塔19で常温まで急冷され、ガ
ス洗浄塔20でアルカリ洗浄等を行って塩化水素や亜硫
酸ガスを吸収除去きれ、改質清浄ガス出口管21より糸
外に取り出される。
The reformed combustible gas outlet 17 at the top of the gas reforming tower 15 converts it into Izumo combustible gas, which is rapidly cooled to room temperature in the gas cooling tower 19 and subjected to alkali cleaning etc. in the gas cleaning tower 20 to absorb hydrogen chloride and sulfur dioxide gas. Once removed, the reformed clean gas is taken out from the thread through the outlet pipe 21.

このようにして取り出された改質清浄ガスは、通常のガ
スバーナー等で燃焼させ熱源として極めて有効に利用す
ることができる。
The reformed clean gas extracted in this way can be burned in a normal gas burner or the like and can be used extremely effectively as a heat source.

上記ガス改質工程中の加熱酸化工程38においては、可
燃性ガスダクト8より送入される可燃性ガスの必要とす
る燃焼空気量の5〜10%の範囲内の空気を、ガス改質
用空気管16から連続又は断続的に送入する。このこと
にエリ、可燃性ガスの一部が燃焼し、発熱反応によりベ
ッド及びコークス層の温度を高温に保つこととなる C十02→CO2 H2+/20鵞→)I20 等の反応により、酸化反応が進行する。
In the heating oxidation step 38 in the gas reforming step, air within the range of 5 to 10% of the amount of combustion air required by the combustible gas sent from the combustible gas duct 8 is used as the gas reforming air. It is fed continuously or intermittently through tube 16. In addition, part of the combustible gas is burned, and an exothermic reaction keeps the temperature of the bed and coke layer at a high temperature. progresses.

第2図(A)H可燃性ガス改質装置の断面を示したもの
で、熱源ヒーター12は電源端子23に接続されており
、外部から電力全負荷されて抵抗発熱体の発熱によシコ
ークスベッド13ft加熱保温し、上記反応を安定化す
る。
Figure 2 (A) shows a cross section of the H combustible gas reformer.The heat source heater 12 is connected to the power supply terminal 23, and when the electric power is fully loaded from the outside, the heat generated by the resistance heating element causes coke. A 13ft bed was heated and kept warm to stabilize the above reaction.

このように加熱されて800〜900℃に達した可燃性
ガスは次の吸熱還元工程39Vc導入され、ベッド13
に支持されtコークス充填層14中に至り、コークスを
触媒として 0+OCh→200 0+H20→OO+ I(2 の反応及びペッド13の触媒効果によりタール分等も熱
分解してCH4やHzが生じ、これらの吸熱還元反応に
より器内温度に下降して出口温度が600℃以下となっ
て上記反応が終結する。
The combustible gas heated in this way and reaching 800 to 900°C is introduced into the next endothermic reduction step 39Vc, and is transferred to the bed 13.
The reaction of 0+OCh → 200 0+H20 → OO+ I (2) and the catalytic effect of the ped 13 thermally decomposes the tar content and generates CH4 and Hz. Due to the endothermic reduction reaction, the temperature drops to the inside temperature of the vessel, and the outlet temperature becomes 600° C. or less, and the above reaction is terminated.

以上のように、可燃性ガス改質装置BH1下段で酸化発
熱反応を利用してタール、カーゼンの酸化熱分解を行い
、上段でコークス及びベッド全高温条件下に保持してガ
スの吸熱還元反応を進行させ、ガスの品位改善を行うも
のである。ガス中のタール、カーゼン、重炭化水素類は
熱分解されてHz + OH4100等の安定燃焼し易
い可燃ガスに変成され、ガス発熱量の均一化が達成され
る。
As described above, in the lower stage of the combustible gas reformer BH1, tar and casene are oxidized and thermally decomposed using an oxidative exothermic reaction, and in the upper stage, the coke and bed are all kept under high temperature conditions to perform an endothermic reduction reaction of the gas. This is to improve the quality of the gas. Tar, carzene, and heavy hydrocarbons in the gas are thermally decomposed and converted into a combustible gas such as Hz + OH4100 that can be stably combusted, and the gas calorific value can be made uniform.

すなわち、本発明方法は、廃棄物処理装置Aと可燃性ガ
ス改質装置Bとを組み合わせて、600〜900℃の比
較的低温度でクリンカトラブルや高温腐食の少ない条件
下で各種高分子プラスチック廃棄物や廃タイヤ、木材チ
ップ、廃木材などを処理し、廃資源を熱として有効に利
用できるようにするもので、混合処理にも単独処理にも
最適のものである。しかも、本方法に用いられる装置の
器内には熱トラブルや腐食の原因となる機械部分が少な
く安全確実に操業できるし、廃棄物処理装置は上述、上
質燃焼で燃焼速度の制御が容易であり、可燃性ガス改質
装置t−It固定層としてのコークスに可燃性ガスを接
触させるので熱効率も高く掃留時間も充分取れる。従っ
て、各工程の酸化発熱、吸熱還元反応等を設定条件通り
実施することが可能である。
That is, the method of the present invention combines waste treatment equipment A and combustible gas reformer B to dispose of various polymer plastics at relatively low temperatures of 600 to 900°C and under conditions with little clinker trouble or high-temperature corrosion. It processes waste materials, waste tires, wood chips, waste wood, etc., and enables the effective use of waste resources as heat, making it ideal for both mixed processing and single processing. Moreover, the equipment used in this method has fewer mechanical parts that can cause thermal troubles and corrosion, and can be operated safely and reliably.The waste treatment equipment uses high-quality combustion, as mentioned above, and the combustion rate can be easily controlled. In the t-It combustible gas reformer, the combustible gas is brought into contact with the coke as the fixed bed, so the thermal efficiency is high and the scavenging time is sufficient. Therefore, it is possible to carry out the oxidation exothermic reaction, endothermic reduction reaction, etc. in each step according to the set conditions.

第2図(B)に可燃性ガス改質装置の他の実施例を示し
た断面図で、熱源ヒータとして電気抵抗発熱体を用いず
、加熱酸化工程38に都市ガス又は灯油上燃料ガス(油
)入口管28から導入し、加熱兼分解用ノズル29で燃
焼させ、外部供給燃料を熱源として運転するものである
。この外部供給燃料による加熱方式の場合は、ガス改質
基15を2基設置し、交互に加熱酸化、吸熱還元と切り
変えて運転することも可能であり、大型容量の場合に好
ましい方法である。なお、第2図(A)及び(B)にお
いて、22はヒーター支持具、24#′iコークス充填
用マンホール、25はアッシュ?I除口、26はアッシ
ュ取り出し口、27は耐火断熱材である。
FIG. 2(B) is a sectional view showing another embodiment of the combustible gas reformer, in which an electric resistance heating element is not used as the heat source heater, and the heating oxidation step 38 is performed using city gas or fuel gas (oil) on kerosene. ) The fuel is introduced through the inlet pipe 28 and combusted in the heating/decomposition nozzle 29, and is operated using externally supplied fuel as the heat source. In the case of this heating method using externally supplied fuel, it is also possible to install two gas reforming units 15 and operate by alternately switching between heating oxidation and endothermic reduction, which is a preferable method in the case of large capacity. . In addition, in FIGS. 2(A) and (B), 22 is a heater support, 24#'i is a coke filling manhole, and 25 is an ash? 26 is an ash outlet, and 27 is a fireproof insulation material.

第3図は可燃性ガス改質装置の自己清浄再生法を説明す
る断面図である。可燃性ガス改質装置Bは、廃棄物処理
装置人から発生した汚れた可燃性ガスを一定時間処理す
ると、ベッドやコークスにカージン、タールが付着して
汚染される。夜間或いは定期点検停止前に、廃棄物処理
装置人の運転を停止しt後、制御盤36を操作して全自
動運転方式により点火用パイロットバーナー31を作動
させ、点火用空気電磁弁3り、点火用ガス電磁弁33、
燃料パイプ34、燃焼用空気パイプ35を用いて加熱兼
分解用ノズル29に点火し、付着したカージン、タール
、ダスト等を焼成()9−ニング)する。この場合、温
度計37でコークス層内を定温に保つよう温度制御する
。なお、本図には示されていないが、焼成時の排ガス用
逃し弁、焼成後の!スト排除の几めの構造等が付設され
ている。燐酸用空気はガス改質用空気管16を用いて送
られるが、焼成効率向上の几めに供給空気の中に加湿用
水40を霧化蒸発させて加湿することも併せ行われる。
FIG. 3 is a sectional view illustrating a self-cleaning regeneration method for a combustible gas reformer. When the combustible gas reformer B processes dirty combustible gas generated from the waste treatment equipment for a certain period of time, the bed and coke become contaminated with cardin and tar. At night or before regular inspection stops, after stopping the operation of the waste treatment equipment, operate the control panel 36 to operate the ignition pilot burner 31 in a fully automatic operation mode, and open the ignition air solenoid valve 3. Ignition gas solenoid valve 33,
The heating and decomposition nozzle 29 is ignited using the fuel pipe 34 and the combustion air pipe 35, and the adhered cargin, tar, dust, etc. are burned out. In this case, the temperature within the coke layer is controlled using a thermometer 37 to maintain a constant temperature. Although not shown in this figure, there is a relief valve for exhaust gas during firing, and a relief valve for exhaust gas after firing. The structure is designed to eliminate strikes. The phosphoric acid air is sent using the gas reforming air pipe 16, but in order to improve the firing efficiency, humidification water 40 is also atomized and evaporated into the supplied air to humidify it.

これにより、焼成がより効果的に迅速に進行する。この
際、コークス自身も若干消耗することとなる。
This allows firing to proceed more effectively and quickly. At this time, the coke itself will also be slightly consumed.

〈発明の効果〉 以上の説明より明らかなとおり、本発明方法に、廃棄物
処理装置において廃棄物、特にプラスチック類、高分子
化合物、廃タイヤ、ビム等の高発熱量を保有する廃棄物
や廃木材、チップなどをガス化して可燃性ガスを発生さ
せ、その可燃性ガスの顕熱と補助熱源ヒーターと空気混
入による部分燃焼との三つの機能を有効適切に組み合わ
せてガスの改質を行うものであり、I 000 KOa
 J/ Nm!の発生ガス中のタール、カージンを二次
的にガス化し、トラブルの少ないクリーンガスに変成す
るものである。従って、本発明方法を実施することによ
って、従来のタール、カージンによる管路の閉塞やノズ
ルの詰り等の問題は根本的に解消され、需要者の利便は
図りしれない。
<Effects of the Invention> As is clear from the above explanation, the method of the present invention can be applied to wastes, especially wastes and wastes having a high calorific value such as plastics, polymer compounds, waste tires, bim, etc. A device that generates flammable gas by gasifying wood, chips, etc., and reforming the gas by effectively and appropriately combining three functions: the sensible heat of the flammable gas, an auxiliary heat source heater, and partial combustion by mixing air. and I 000 KOa
J/ Nm! This system secondarily gasifies tar and cardin in the generated gas and transforms it into clean gas with fewer troubles. Therefore, by carrying out the method of the present invention, the conventional problems such as blockage of pipes and clogging of nozzles due to tar and cardin are fundamentally solved, and the convenience of users is immense.

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

第1図は本発明方法に使用される装置の一実施例の系統
説明図、第2図は本発明方法に使用される可燃性ガス改
質装置の断面図、第3図は可燃性ガス改質装置の自己清
浄再生法を説明する断面図である。 A・・廃棄物処理装置、B・・可燃性ガス改質装置、1
・・廃棄物貯留タンク、2・・ガス化反応工程、11・
・可燃性ガス入口、12・・熱源ヒーター、13・・ベ
ッド、14・・コークス充填層、16・・ガス改質用空
気管、18・・ガス改質用空気ノズル、29・・加熱兼
分解用ノズル。 特許出願人 株氏会社 トナミ電機エンジニアリング代
理人 弁理士  志 村 正 和 II i 図
Fig. 1 is a system explanatory diagram of an embodiment of the apparatus used in the method of the present invention, Fig. 2 is a sectional view of a combustible gas reformer used in the method of the present invention, and Fig. 3 is a sectional view of a combustible gas reformer used in the method of the present invention. FIG. 2 is a cross-sectional view illustrating a self-cleaning regeneration method for a quality device. A...Waste treatment equipment, B...Flammable gas reformer, 1
・・Waste storage tank, 2・・Gasification reaction process, 11・
・Flammable gas inlet, 12. Heat source heater, 13. Bed, 14. Coke packed bed, 16. Air pipe for gas reforming, 18. Air nozzle for gas reforming, 29. Heating and decomposition. Nozzle for. Patent applicant: Tonami Electric Engineering Co., Ltd. Agent: Patent attorney: Tadashi Shimura Kazu II Figure

Claims (1)

【特許請求の範囲】[Claims] 内部にベツドを有し該ベツドに熱源を備えるとともにベ
ツド上方に粒状コークスを充填した竪型可燃性ガス改質
装置の下部より、廃棄物処理装置において発生した可燃
性ガスを冷却することなく高温の状態で送入して上向流
として上昇せしめ、前記熱源によりコークスを赤熱する
とともに、ベツド下方に配置されたノズルより空気を供
給することを特徴とする可燃性ガスの改質方法。
The combustible gas generated in the waste treatment equipment is heated to high temperature without being cooled from the lower part of the vertical combustible gas reformer, which has a bed inside and is equipped with a heat source and is filled with granular coke above the bed. A method for reforming a combustible gas, characterized in that the coke is fed in a state in which it rises as an upward flow, the coke is red-hot by the heat source, and air is supplied from a nozzle arranged below the bed.
JP60134967A 1985-06-20 1985-06-20 Method of reforming combustible gas Pending JPS61293297A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP60134967A JPS61293297A (en) 1985-06-20 1985-06-20 Method of reforming combustible gas

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP60134967A JPS61293297A (en) 1985-06-20 1985-06-20 Method of reforming combustible gas

Publications (1)

Publication Number Publication Date
JPS61293297A true JPS61293297A (en) 1986-12-24

Family

ID=15140777

Family Applications (1)

Application Number Title Priority Date Filing Date
JP60134967A Pending JPS61293297A (en) 1985-06-20 1985-06-20 Method of reforming combustible gas

Country Status (1)

Country Link
JP (1) JPS61293297A (en)

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2006348155A (en) * 2005-06-15 2006-12-28 Yanmar Co Ltd Gas reformer and gas-reforming method
WO2008083574A1 (en) * 2006-12-28 2008-07-17 Jiule Zhou A dry coal powder gasification furnace
KR101069574B1 (en) 2009-03-31 2011-10-05 서울시립대학교 산학협력단 Dual biomass gasifier with carbonaceous absorbent and apparatus having the dual biomass gasifier

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2006348155A (en) * 2005-06-15 2006-12-28 Yanmar Co Ltd Gas reformer and gas-reforming method
WO2008083574A1 (en) * 2006-12-28 2008-07-17 Jiule Zhou A dry coal powder gasification furnace
JP2010514858A (en) * 2006-12-28 2010-05-06 ゾウ,ジウレ Pulverized coal gas stove
AU2007343509B2 (en) * 2006-12-28 2011-10-06 Jiule Zhou A dry coal powder gasification furnace
KR101069574B1 (en) 2009-03-31 2011-10-05 서울시립대학교 산학협력단 Dual biomass gasifier with carbonaceous absorbent and apparatus having the dual biomass gasifier

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