JP2002326076A - Method for treating waste and equipment therefor - Google Patents

Method for treating waste and equipment therefor

Info

Publication number
JP2002326076A
JP2002326076A JP2001137155A JP2001137155A JP2002326076A JP 2002326076 A JP2002326076 A JP 2002326076A JP 2001137155 A JP2001137155 A JP 2001137155A JP 2001137155 A JP2001137155 A JP 2001137155A JP 2002326076 A JP2002326076 A JP 2002326076A
Authority
JP
Japan
Prior art keywords
waste
system zone
heating
organic
extracted
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
JP2001137155A
Other languages
Japanese (ja)
Other versions
JP4702868B2 (en
Inventor
Masamichi Asano
昌道 浅野
Kimitoshi Ose
公利 小瀬
Hiroki Honda
裕姫 本多
Noriaki Senba
範明 仙波
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
Application filed by Mitsubishi Heavy Industries Ltd filed Critical Mitsubishi Heavy Industries Ltd
Priority to JP2001137155A priority Critical patent/JP4702868B2/en
Publication of JP2002326076A publication Critical patent/JP2002326076A/en
Application granted granted Critical
Publication of JP4702868B2 publication Critical patent/JP4702868B2/en
Anticipated expiration legal-status Critical
Expired - Lifetime 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

Abstract

PROBLEM TO BE SOLVED: To provide a method for treating waste by which waste, particularly organic material-base waste such as garbage or sludge is treated without increasing treatment cost while suppressing the generation of organic halogenated compounds and carbonized materials effectively utilizable as resources are effectively fixed and to provide equipment therefor. SOLUTION: In the method for treating waste while suppressing the generation of organic halogenated compounds, organic waste is supplied to a circulation zone which has a concentration of oxygen limited to <=5% and is heated from the outside, the interior of the circulation zone is kept at 300-800 deg.C and gas resulting from thermal decomposition and carbonized materials both generated from the waste are separately drawn from the terminal side of the circulation zone.

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】本発明は有機ハロゲン化化合
物の生成を抑制した廃棄物、特にごみ、汚泥などの有機
性廃棄物の処理方法及び同装置に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method and an apparatus for treating organic waste such as garbage and sludge, in which the generation of organic halogenated compounds is suppressed.

【0002】[0002]

【従来の技術】ごみ、汚泥などの有機性化合物を主体と
する廃棄物は、ハロゲン化化合物を含有しているので、
空気を支燃剤として、通常の方法で焼却するとダイオキ
シン類など有毒な有機ハロゲン化化合物を発生する。前
記有毒な化合物の発生を抑制するために、従来、燃焼条
件の複雑な制御や発生抑制物質の添加、除害設備の併設
などが試みられている。特に、このダイオキシン類など
の有機ハロゲン化化合物は燃焼温度が300〜850℃
付近の中程度の温度範囲で生成し易いので、この温度を
避けた条件、例えば高温燃焼などの方法がとられてい
る。
2. Description of the Related Art Waste mainly composed of organic compounds such as refuse and sludge contains halogenated compounds.
When incinerated in a usual manner using air as a fuel, toxic organic halogenated compounds such as dioxins are generated. Conventionally, in order to suppress the generation of the toxic compound, attempts have been made to control the combustion conditions in a complicated manner, to add a generation suppressing substance, and to install a detoxification facility. In particular, organic halogenated compounds such as dioxins have a combustion temperature of 300 to 850 ° C.
Since it is easy to generate in the vicinity of a moderate temperature range, a method of avoiding this temperature, for example, a method of high-temperature combustion is used.

【0003】しかし、これら従来の方法では、不均一な
形態の廃棄物を直接燃焼させる以上、必ずしも全体を理
想的な条件で燃焼させるのは困難であり、付帯設備が大
きくなり、且つ高温燃焼に耐える焼却炉とするなど、処
理コストの増大を伴う問題があった。
However, in these conventional methods, it is difficult to burn the whole under ideal conditions more than directly burning the waste in a non-uniform form. There was a problem with an increase in processing costs, such as a tough incinerator.

【0004】[0004]

【発明が解決しようとする課題】本発明はかかる従来の
問題点に鑑みてなされたもので、処理コストの増大を伴
わない、有機ハロゲン化化合物の生成を抑制した廃棄
物、特にごみ、汚泥などの有機性物質を主体とする廃棄
物の処理をして、同時に資源として有効に利用できる炭
化物を有効に固定する方法及び同装置の提供を目的とす
る。
DISCLOSURE OF THE INVENTION The present invention has been made in view of the above-mentioned conventional problems, and does not increase the processing cost and suppresses the production of organic halogenated compounds, particularly wastes, sludge, etc. It is an object of the present invention to provide a method and an apparatus for treating waste mainly composed of organic substances and effectively fixing carbides which can be effectively used as resources at the same time.

【0005】[0005]

【課題を解決するための手段】前記目的を達成するた
め、本発明は、有機ハロゲン化化合物の生成を抑制した
廃棄物の処理方法であって、有機性廃棄物を酸素濃度5
%以下に制限した、外部より加熱する流通系ゾーンに供
給し、該流通系ゾーン内を温度300〜800℃に維持
し、前記廃棄物より発生する熱分解ガスと炭化物を該流
通系ゾーン終端側より分離しながら抜きだすことを特徴
とする。
To achieve the above object, the present invention relates to a method for treating waste in which the production of organic halogenated compounds is suppressed.
% And supplied to an externally heated distribution system zone which is limited to not more than 3%, the temperature in the distribution system zone is maintained at 300 to 800 ° C., and pyrolysis gas and carbide generated from the waste are discharged from the end of the distribution system zone. It is characterized by extracting while separating more.

【0006】本発明では従来技術のような燃焼をさせる
という概念から離れることから始まる。それには、酸素
を制限して、発熱を伴う酸化燃焼ではなく、緩やかな条
件で起こる化学結合の切断を主体とする熱分解が支配的
な反応とすべきであった。そして、該反応が行われてい
るゾーンは常に原料系を供給し、生成系を取り出すこと
を可能とする、流通系ゾーンであるべきであり、該主体
とする吸熱反応である熱分解に必要な熱を外部から供給
する必要があった。
The present invention starts with a departure from the concept of burning as in the prior art. In order to do this, the reaction should be dominated by thermal decomposition, which is based on the breaking of chemical bonds that occurs under mild conditions, rather than oxidative combustion with exothermicity, by limiting oxygen. The zone in which the reaction is performed should always be a flow system zone that enables the supply of the raw material system and the removal of the production system, and is necessary for thermal decomposition, which is an endothermic reaction that is the main component. Heat had to be supplied externally.

【0007】5%以下という若干の酸素は、酸化反応に
関与するが、このように酸素分圧の低い条件での酸化は
燃焼とまでは行かず、発熱反応によって内部から熱を与
える面では寄与するものの、局部的な高温状態はとても
現出しえないので、前記毒性のある有機ハロゲン化物質
の生成には至らない。また、ダイオキシン類などの有機
ハロゲン化物質は一旦生成すると難分解性であるので、
また、炭化物の収量を上げる意味においても全体の温度
を300〜800℃に制限するのが同時に重要な要素で
ある。
Although a small amount of oxygen of 5% or less is involved in the oxidation reaction, the oxidation under such low oxygen partial pressure conditions does not go to combustion, but contributes to the heat supply from the inside by the exothermic reaction. However, local high temperature conditions are not very apparent and do not lead to the production of the toxic organic halogenated substances. Also, organic halogenated substances such as dioxins are hardly decomposable once formed,
Also, from the viewpoint of increasing the yield of carbides, limiting the entire temperature to 300 to 800 ° C. is an important factor at the same time.

【0008】更に本発明の廃棄物の処理方法は、前記方
法で処理するに当たって、前記有機性廃棄物とともに水
蒸気若しくは金属の炭酸塩、酸化物、硫酸塩、水酸化物
から選ばれる少なくとも一つの化合物を供給することを
特徴とする。
In the method for treating waste according to the present invention, at least one compound selected from the group consisting of water vapor and metal carbonates, oxides, sulfates and hydroxides, together with the organic waste. Is supplied.

【0009】水蒸気の添加は、系の酸素分圧を低下する
ことによって、激しい酸化反応を抑制し、更に水が系内
の炭素と反応して、一酸化炭素や水素を生成して、還元
性ガス雰囲気となり、有毒な有機ハロゲン化化合物の生
成を抑制し、原料中の炭素分の固定に寄与する。
The addition of water vapor suppresses a violent oxidation reaction by lowering the oxygen partial pressure of the system, and furthermore, water reacts with carbon in the system to generate carbon monoxide and hydrogen, thereby reducing It becomes a gas atmosphere, suppresses generation of toxic organic halogenated compounds, and contributes to fixation of carbon in the raw material.

【0010】また、金属の炭酸塩、酸化物、ケイ酸塩、
硫酸塩、水酸化物は炭素鎖の切断を助長する触媒作用
や、反応系内の遊離ハロゲンを無機物(金属塩)として
固定する作用があることがわかり、本発明の方法を低温
で速やかに進行させるのに有効である。これら化合物の
例としては、炭酸ソーダ、酸化鉄、水酸化カルシウム、
などがあげられる。
Also, metal carbonates, oxides, silicates,
It was found that sulfates and hydroxides have a catalytic action to promote the cleavage of the carbon chain and an action to fix free halogens in the reaction system as inorganic substances (metal salts). It is effective to make it. Examples of these compounds include sodium carbonate, iron oxide, calcium hydroxide,
And so on.

【0011】更に本発明の廃棄物の処理方法は、前記加
熱流通系ゾーンから抜き出す熱分解ガスを850〜11
00℃で高温燃焼させることを特徴とする。この熱分解
ガスは、未だ、ハロゲン源を持っているため、潜在的に
前記有毒な有機ハロゲン化化合物を生成する原因物質を
含んでいるので、これら化合物を生成しない、また、た
とえ生成していたとしても分解する前記高温域で燃焼さ
せる。これにより、系内に含有しているハロゲンはハロ
ゲン化水素となるので、排気経路でアルカリ性物質など
で中和して容易且つ低コストで除去することが可能とな
る。また得られた高温の排ガスは前記流通ゾーンを外部
から加熱する熱源として有効に利用することができる。
Further, in the method for treating waste according to the present invention, the pyrolysis gas extracted from the heating and flowing system zone may be 850 to 11
It is characterized by high temperature combustion at 00 ° C. Since this pyrolysis gas still has a halogen source, and contains a causative substance that potentially forms the toxic organic halogenated compound, it does not generate these compounds, and even if it did. It burns in the high temperature range where it decomposes. As a result, the halogen contained in the system becomes hydrogen halide, so that it can be easily and inexpensively removed by neutralizing with an alkaline substance in the exhaust path. The obtained high-temperature exhaust gas can be effectively used as a heat source for heating the circulation zone from the outside.

【0012】更に本発明の廃棄物の処理方法は、前記加
熱流通系ゾーンから抜き出す炭素を主体とする炭化物を
250℃以下に急冷して抜きだすことを特徴とする。こ
れは、前記熱分解で固相の方に移行した残存ハロゲン化
物質があった場合、ダイオキシン等有毒ハロゲン化化合
物に転化させないための手段である。高温状態で抜き出
し空気中の酸素と触れさせないためには、本発明のこの
操作が必要となる。
Further, the method for treating waste according to the present invention is characterized in that a carbide mainly composed of carbon extracted from the heating and flowing system zone is rapidly cooled to 250 ° C. or less and extracted. This is a means for preventing any residual halogenated substance which has migrated to the solid phase by the thermal decomposition from being converted into a toxic halogenated compound such as dioxin. This operation of the present invention is necessary so as not to come in contact with oxygen in the extracted air at a high temperature.

【0013】そして本発明は、有機ハロゲン化化合物の
生成を抑制した廃棄物の処理装置であって、有機性廃棄
物の供給手段と、攪拌手段及び外部加熱手段を備え、酸
素濃度を制限した流通系ゾーンと、該流通系ゾーンの終
端側に熱分解ガス及び炭化物の分離抜き出し手段とを有
し、有機性廃棄物を前記加熱流通系ゾーンに供給し、設
定温度範囲に維持することにより前記廃棄物より発生す
る熱分解ガスと炭化物を該流通系ゾーンの終端側より分
離しながら抜きだすことを可能にしたことを特徴とす
る。
The present invention relates to a waste treatment apparatus in which the generation of an organic halogenated compound is suppressed, comprising a means for supplying an organic waste, a stirring means and an external heating means, and a flow restricting the oxygen concentration. System zone, and a means for separating and extracting pyrolysis gas and carbide at the end side of the flow system zone, supplying organic waste to the heating flow system zone, and maintaining the temperature within a set temperature range, thereby disposing the waste. It is characterized in that the pyrolysis gas and carbide generated from the material can be extracted while being separated from the end side of the flow system zone.

【0014】有機性廃棄物の供給手段は、本発明の性格
上、該流通系ゾーンと外気との間がシール性よく保たれ
る構造のもので、供給速度が自在に調節可能なものが好
ましい。そして、原料系の形態が雑多であるので、破
砕、粉砕などの手段を含むことも好ましい。従って、こ
れら好ましい態様の組み合わせとしては、該流通系ゾー
ンの入り口とを接続したスクリューフィーダなどがあげ
られる。
The organic waste supply means has a structure in which the space between the flow system zone and the outside air is kept well-sealed from the viewpoint of the present invention, and it is preferable that the supply rate can be freely adjusted. . Since the form of the raw material system is various, it is preferable to include means such as crushing and pulverization. Therefore, as a combination of these preferred embodiments, there is a screw feeder or the like connected to the entrance of the flow system zone.

【0015】そして、前記流通系ゾーンは供給手段と接
続された、原料の供給される入口があり、熱分解ガス及
び炭化物を抜き出す出口のある、確定した、一定容積の
反応ゾーンであり、攪拌手段及び外部加熱手段を付帯す
る。攪拌手段は反応ゾーンそのものが揺動、回転などし
て滞留物が攪拌されてもよいし、攪拌機などで滞留物が
攪拌されるタイプてもよい。また、外部加熱手段とは熱
を外から供給する意味であって、例えば高温ガス源に接
続された該流通系ゾーンを取り巻くジャケットであって
もよい、また同様に高温ガス源に接続された該流通系ゾ
ーン内部にコイル状に配置された管であってもよい。
The flow system zone is a defined, constant volume reaction zone having an inlet for supplying raw materials and an outlet for extracting pyrolysis gas and carbide, which is connected to the supply means. And external heating means. The stirrer may be a type in which the remaining material is stirred by the reaction zone itself swinging or rotating, or the remaining material may be stirred by a stirrer or the like. Further, the external heating means means to supply heat from the outside, and may be, for example, a jacket surrounding the circulation system zone connected to a high-temperature gas source, or the jacket connected to a high-temperature gas source. It may be a tube arranged in a coil shape inside the flow system zone.

【0016】前記分離抜き出し手段は、例えば、該流通
系ゾーン終端側出口付近に設けられた固気分離ポートに
接続された、分解ガス排出配管、及び炭化物排出口であ
る。炭化物排出口には排出用のスクリューコンベヤが付
帯していてもよい。
The separation / extraction means is, for example, a cracked gas discharge pipe and a carbide discharge port connected to a solid-gas separation port provided near the outlet on the end of the flow system zone. A screw conveyor for discharge may be attached to the carbide discharge port.

【0017】更に本発明の廃棄物の処理装置は、前記加
熱流通系ゾーンより抜き出す熱分解ガスを高温燃焼させ
ることのできる高温燃焼炉を更に備えたことを特徴とす
る。この高温燃焼炉は例えば、前記加熱流通系ゾーンよ
り抜き出す熱分解ガスを導入する配管及び空気若しくは
酸素富化空気送入配管に接続して、該熱分解ガスを高温
で燃焼させるバーナーを備え、燃焼排ガスを排出する出
口を有する燃焼炉である。例えば、高温の燃焼排ガスの
用途によっては、若しくはバーナ閉塞防止の目的から、
燃焼炉入り口の経路に除塵器を設け分解ガスに随伴する
固体粒子を排除してから、高温燃焼炉に供給することも
可能である。
Further, the waste treatment apparatus of the present invention is further characterized by further comprising a high-temperature combustion furnace capable of burning the pyrolysis gas extracted from the heating and circulation system zone at a high temperature. The high-temperature combustion furnace includes, for example, a burner connected to a pipe for introducing a pyrolysis gas extracted from the heating and circulation system zone and a pipe for feeding air or oxygen-enriched air to burn the pyrolysis gas at a high temperature. It is a combustion furnace having an outlet for discharging exhaust gas. For example, depending on the application of high-temperature flue gas, or for the purpose of preventing burner blockage,
It is also possible to provide a dust remover in the path at the entrance of the combustion furnace to remove solid particles accompanying the decomposition gas before supplying the gas to the high-temperature combustion furnace.

【0018】更に本発明の廃棄物の処理装置は、前記加
熱流通系ゾーンより抜き出す炭化物を急冷して抜きだす
ことのできる炭化物急冷手段を更に備えたことを特徴と
する。該急冷手段は、炭化物抜き出し経路に設けた例え
ば熱交換器で、抜き出し途上の炭化物が熱交換器の伝熱
面に接触して冷却されるよう構成すればよい。該伝熱面
の他方の面は水などの低温媒体で冷却して、除熱する。
Further, the waste treatment apparatus of the present invention is characterized by further comprising carbide quenching means capable of quenching and extracting the carbide extracted from the heating / circulating system zone. The quenching means may be constituted, for example, by a heat exchanger provided in the carbide extraction path, so that the carbide being extracted is brought into contact with the heat transfer surface of the heat exchanger and cooled. The other surface of the heat transfer surface is cooled by a low-temperature medium such as water to remove heat.

【0019】冷却効率の点から、熱交換器の伝熱面積は
限られた空間の中で大きい方がよい。したがって、例え
ば、管路の径を拡大して、その外部を囲繞した冷却ジャ
ケットや、経路に挿入した多管式熱交換器、若しくはフ
ィン付きチューブ等とすることができる。
From the viewpoint of cooling efficiency, the heat transfer area of the heat exchanger is preferably large in a limited space. Therefore, for example, it is possible to increase the diameter of the conduit to provide a cooling jacket surrounding the outside thereof, a multi-tubular heat exchanger inserted into the passage, a finned tube, or the like.

【0020】更に本発明の廃棄物の処理装置は、前記加
熱流通系ゾーンが外熱式キルンであることを特徴とす
る。
Further, the waste treatment apparatus of the present invention is characterized in that the heating and circulation system zone is an externally heated kiln.

【0021】[0021]

【発明の実施の形態】次に本発明の実施の形態を図面を
参照しながら、例示的に説明する。但し本実施の形態に
記載される製品の寸法、形状、材質、その相対配置等は
特に特定的な記載がない限りは本発明の範囲をそれのみ
に限定する趣旨ではなく、単なる説明例に過ぎない。
DESCRIPTION OF THE PREFERRED EMBODIMENTS Next, embodiments of the present invention will be illustratively described with reference to the drawings. However, the dimensions, shapes, materials, relative arrangements, and the like of the products described in the present embodiment are not intended to limit the scope of the present invention thereto, unless otherwise specified, but are merely illustrative examples. Absent.

【0022】図1は本発明の一例を示すプロセスフロー
図である。図1において、貯留された有機性廃棄物10
1は破砕機及びスクリューフィーダにより構成された供
給手段111により、破砕された後、加熱流通ゾーンで
ある外熱式キルン112中に連続的に供給される。また
破砕機の投入口から、廃棄物の0.3%ほどの炭酸ソー
ダを触媒として、同時に連続的に供給する。そして外熱
式キルン112の加熱ジャケット113中に高温排ガス
104を流通して内部を加熱する。昇温途上の十分低温
の間に、キルン内部は窒素若しくは水蒸気でフラッシュ
して、内部の空気の一部を置換し、酸素濃度を5%以下
に抑える。外熱式キルンの内温は300〜800℃に制
御し、炭化物を分離抜き出し手段114の下部に導き、
熱分解ガス102を上部から取り出す。分離抜き出し手
段114の下部からは、有機性廃棄物の供給量とバラン
スしてキルン内容量が定常状態になるよう、炭化物を抜
き出す。分離抜き出し手段の下部には急冷手段として熱
交換器115を備え、抜き出し時に急冷する。
FIG. 1 is a process flow chart showing an example of the present invention. In FIG. 1, the stored organic waste 10
After being crushed by a supply means 111 constituted by a crusher and a screw feeder, 1 is continuously supplied into an externally heated kiln 112 which is a heating and distribution zone. Also, about 0.3% of the waste is supplied as a catalyst simultaneously and continuously from the inlet of the crusher. Then, the high-temperature exhaust gas 104 flows through the heating jacket 113 of the externally heated kiln 112 to heat the inside. During a sufficiently low temperature during the heating, the inside of the kiln is flushed with nitrogen or water vapor to replace a part of the air inside and keep the oxygen concentration at 5% or less. The internal temperature of the external heat type kiln is controlled at 300 to 800 ° C., and the carbide is guided to the lower part of the separation and extraction means 114,
The pyrolysis gas 102 is taken out from above. Carbides are extracted from the lower part of the separation and extraction means 114 so that the kiln capacity is in a steady state in balance with the supply amount of organic waste. A heat exchanger 115 is provided below the separating and extracting means as a quenching means, and is rapidly cooled at the time of extraction.

【0023】熱分解ガス102は飛散粒子を含んでいる
ので、バグフィルタ116で除塵した後、高温燃焼炉1
17で燃焼させる。高温焼却炉117での燃焼用空気若
しくは酸素富化空気106は別の経路で該炉117まで
導く。
Since the pyrolysis gas 102 contains scattered particles, after the dust is removed by the bag filter 116, the high-temperature combustion furnace 1
Burn at 17. The combustion air or oxygen-enriched air 106 in the high temperature incinerator 117 is led to the furnace 117 by another route.

【0024】高温燃焼炉117で得られた高温排ガスの
一部104は、外熱式キルン112の加熱ジャケット1
13に導き、分解に必要な熱供給に用い、加熱ジャケッ
ト113出口から排出する未だ温度の高い、熱供給後の
ガス107は高温燃焼炉117から排出する高温ガスの
一部と合流させてボイラ加熱用ガス105とする。
A part 104 of the high-temperature exhaust gas obtained in the high-temperature combustion furnace 117 is supplied to the heating jacket 1 of the external heating kiln 112.
13, which is used for heat supply necessary for decomposition, and the gas 107 after the heat supply, which is still high in temperature and discharged from the outlet of the heating jacket 113, is combined with a part of the high-temperature gas discharged from the high-temperature combustion furnace 117 to heat the boiler. For the use gas 105.

【0025】高温のボイラ加熱用ガス105はボイラ1
22に導かれ、ここで蒸気を発生する熱源として使用さ
れ、発生した蒸気は蒸気タービン式発電機119を駆動
し、復水機120により凝縮した水を再びボイラに戻
し、循環せしめる。
High-temperature boiler heating gas 105 is supplied to boiler 1
The steam condensed by the condenser 120 is returned to the boiler and circulated by the steam turbine generator 119 which is used as a heat source for generating steam.

【0026】ボイラ加熱用ガス105はボイラ122で
熱交換してボイラからの排ガスとなり、バグフィルタ1
21で除塵後、煙突118から排出される。
The boiler heating gas 105 exchanges heat with the boiler 122 to become exhaust gas from the boiler.
After the dust is removed at 21, it is discharged from the chimney 118.

【0027】以上本例のプロセスにより、有機性廃棄物
を有毒な有機ハロゲン化化合物の生成を抑制して処理
し、炭素を主体とする、資源として有効利用の出来る炭
化物を取得し、発生する熱源によりボイラを稼動しター
ビン発電機を運転してエネルギーを有効に回収できる。
しかも、装置としてコンパクトで、特に特殊な材料を必
要としないプラントとすることができ、コストも低廉で
ある。
According to the process of the present embodiment, the organic waste is treated by suppressing the generation of toxic organic halogenated compounds to obtain a carbon-based carbide which can be effectively used as a resource and to generate a heat source. Thus, the boiler can be operated and the turbine generator can be operated to effectively recover energy.
Moreover, the plant can be made compact as a device that does not particularly require special materials, and the cost is low.

【0028】[0028]

【発明の効果】以上説明したように、本発明により、処
理コストの増大を伴わない、有機ハロゲン化化合物の生
成を抑制した廃棄物、特にごみ、汚泥などの有機性物質
を主体とする廃棄物の処理をして、同時に資源として有
効に利用できる炭化物を有効に固定する方法及び同装置
の提供が可能となった。
As described above, according to the present invention, waste which suppresses generation of an organic halogenated compound, particularly waste mainly composed of organic substances such as garbage and sludge, without increasing the treatment cost. And a method and apparatus for effectively fixing carbides that can be effectively used as resources at the same time.

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

【図1】 本発明の一例を示すプロセスフロー図であ
る。
FIG. 1 is a process flow chart showing an example of the present invention.

【符号の説明】[Explanation of symbols]

101 有機性廃棄物 102 熱分解ガス 103 炭化物 104 高温排ガス 105 ボイラ加熱用ガス 106 空気若しくは酸素富化空気 107 熱供給後のガス 111 供給手段(破砕機+スクリューフィーダ) 112 加熱流通系ゾーン(外熱式キルン) 113 加熱ジャケット 114 分離抜き出し手段 115 急冷手段(熱交換器) 116 バグフィルタ 117 高温燃焼炉 118 煙突 119 蒸気タービン発電機 120 複水器 121 バグフィルタ 122 ボイラ Reference Signs List 101 Organic waste 102 Pyrolysis gas 103 Carbide 104 High temperature exhaust gas 105 Boiler heating gas 106 Air or oxygen-enriched air 107 Gas after heat supply 111 Supply means (crusher + screw feeder) 112 Heat distribution zone (external heat) 113) Heating jacket 114 Separation / extraction means 115 Quenching means (heat exchanger) 116 Bag filter 117 High temperature combustion furnace 118 Chimney 119 Steam turbine generator 120 Duplexer 121 Bag filter 122 Boiler

───────────────────────────────────────────────────── フロントページの続き (72)発明者 本多 裕姫 横浜市金沢区幸浦一丁目8番地1 三菱重 工業株式会社横浜研究所内 (72)発明者 仙波 範明 横浜市金沢区幸浦一丁目8番地1 三菱重 工業株式会社横浜研究所内 Fターム(参考) 3K061 NA07 NA13 4D004 AA00 AA46 AB06 BA03 CA26 CA32 CB09 CC12 DA03 DA06 DA10 4D059 AA00 BB03 BB06 BB14 EA09 EA10 EB09 EB10  ──────────────────────────────────────────────────続 き Continuing on the front page (72) Inventor Hiroki Honda 1-8-1, Koura, Kanazawa-ku, Yokohama-shi Mitsubishi Heavy Industries, Ltd. Yokohama Research Laboratory (72) Inventor Noriaki Senba 1-8-8 Koura, Kanazawa-ku, Yokohama-shi 1 Mitsubishi Heavy Industries, Ltd. Yokohama Research Laboratory F term (reference) 3K061 NA07 NA13 4D004 AA00 AA46 AB06 BA03 CA26 CA32 CB09 CC12 DA03 DA06 DA10 4D059 AA00 BB03 BB06 BB14 EA09 EA10 EB09 EB10

Claims (8)

【特許請求の範囲】[Claims] 【請求項1】 有機ハロゲン化化合物の生成を抑制した
廃棄物の処理方法であって、有機性廃棄物を酸素濃度5
%以下に制限した、外部より加熱する流通系ゾーンに供
給し、該流通系ゾーン内を温度300〜800℃に維持
し、前記廃棄物より発生する熱分解ガスと炭化物を該流
通系ゾーン終端側より分離しながら抜きだすことを特徴
とする廃棄物の処理方法。
1. A method for treating waste in which generation of an organic halogenated compound is suppressed, wherein the organic waste has an oxygen concentration of 5%.
% And supplied to an externally heated distribution system zone which is limited to not more than 3%, the temperature in the distribution system zone is maintained at 300 to 800 ° C., and pyrolysis gas and carbide generated from the waste are discharged from the end of the distribution system zone. A waste disposal method characterized by extracting while separating more.
【請求項2】 前記有機性廃棄物とともに水蒸気若しく
は金属の炭酸塩、酸化物、硫酸塩、ケイ酸塩、水酸化物
から選ばれる少なくとも一つの化合物を供給することを
特徴とする請求項1記載の廃棄物の処理方法。
2. The method according to claim 1, wherein at least one compound selected from the group consisting of water vapor and metal carbonates, oxides, sulfates, silicates and hydroxides is supplied together with the organic waste. Waste treatment method.
【請求項3】 前記加熱流通系ゾーンから抜き出す熱分
解ガスを850〜1100℃で高温燃焼させることを特
徴とする請求項1記載の廃棄物の処理方法。
3. The method for treating waste according to claim 1, wherein the pyrolysis gas extracted from the heating circulation system zone is burned at a high temperature of 850 to 1100 ° C.
【請求項4】 前記加熱流通系ゾーンから抜き出す炭化
物を250℃以下に急冷して抜きだすことを特徴とする
請求項1記載の廃棄物の処理方法。
4. The waste treatment method according to claim 1, wherein the carbides extracted from the heating and circulation system zone are rapidly cooled to 250 ° C. or less and extracted.
【請求項5】 有機ハロゲン化化合物の生成を抑制した
廃棄物の処理装置であって、有機性廃棄物の供給手段
と、攪拌手段及び外部加熱手段を備え、酸素濃度を制限
した流通系ゾーンと、該流通系ゾーンの終端側に熱分解
ガス及び炭化物の分離抜き出し手段とを有し、有機性廃
棄物を前記加熱流通系ゾーンに供給し、設定温度範囲に
維持することにより前記廃棄物より発生する熱分解ガス
と炭化物を該流通系ゾーンの終端側より分離しながら抜
きだすことを可能にしたことを特徴とする廃棄物の処理
装置。
5. A waste treatment apparatus in which generation of an organic halogenated compound is suppressed, comprising a means for supplying organic waste, a stirring means and an external heating means, and a flow system zone having a restricted oxygen concentration. Having a means for separating and extracting pyrolysis gas and carbides at the end side of the flow system zone, supplying organic waste to the heating flow system zone, and generating the organic waste from the waste by maintaining the temperature within a set temperature range. A waste pyrolysis gas and carbides separated from the end of the flow system zone while being extracted.
【請求項6】 前記加熱流通系ゾーンより抜き出す熱分
解ガスを高温燃焼させることのできる高温燃焼炉を更に
備えたことを特徴とする請求項5記載の廃棄物の処理装
置。
6. The waste treatment apparatus according to claim 5, further comprising a high-temperature combustion furnace capable of burning the pyrolysis gas extracted from the heating circulation system zone at a high temperature.
【請求項7】 前記加熱流通系ゾーンより抜き出す炭化
物を急冷して抜きだすことのできる炭化物急冷手段を更
に備えたことを特徴とする請求項5記載の廃棄物の処理
装置。
7. The waste treatment apparatus according to claim 5, further comprising a carbide quenching means capable of quenching and extracting the carbide extracted from the heating and circulation system zone.
【請求項8】 前記加熱流通系ゾーンが外熱式キルンで
あることを特徴とする請求項5乃至7いずれかの項記載
の廃棄物の処理装置。
8. The apparatus for treating waste according to claim 5, wherein the heating / circulating system zone is an external heat type kiln.
JP2001137155A 2001-05-08 2001-05-08 Organic waste processing method and processing equipment Expired - Lifetime JP4702868B2 (en)

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Country Link
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Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2006082045A (en) * 2004-09-17 2006-03-30 Toru Kubota Treatment method for recycling of contaminant and its apparatus
JP2010125392A (en) * 2008-11-27 2010-06-10 Ihi Corp Sludge heating treatment method and sludge heating treatment apparatus
CN103100552A (en) * 2013-01-22 2013-05-15 蒲仁建 Method and system for carrying out thermal treatment on household garbage by using brick kiln
JP2014042908A (en) * 2012-07-28 2014-03-13 Sankyo Erec Co Ltd Method and apparatus for treating garbage

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* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR102534259B1 (en) * 2022-10-11 2023-05-30 주식회사 동남테크 Carbon dioxide capture system for animals and plants waste matter carbonization apparatus

Citations (11)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH0947795A (en) * 1995-08-09 1997-02-18 Kubota Corp Device for carbonizing and regenerating organic waste
JPH09235559A (en) * 1996-02-22 1997-09-09 Noel Krc Energ & Umwelttechnik Gmbh Utilization of residue and waste in terms of material and energy in upright furnace
JPH1076138A (en) * 1996-09-04 1998-03-24 Tadahiro Omi Treatment of waste gas containing halogen compound
JPH10235308A (en) * 1997-02-24 1998-09-08 Meidensha Corp Dechlorination treatment of moisture-containing matter to be treated
JPH1114021A (en) * 1997-06-23 1999-01-22 Mitsui Eng & Shipbuild Co Ltd Waste disposal equipment
JP2000104082A (en) * 1998-09-30 2000-04-11 Kawasaki Steel Corp Method and apparatus for producing refuse derived solid fuel
JP2000296378A (en) * 1999-04-13 2000-10-24 Mitsubishi Heavy Ind Ltd Waste treatment
JP2001021126A (en) * 1999-07-09 2001-01-26 Takuma Co Ltd Apparatus for dry distilating, thermal cracking, melting and igniting waste material
JP2001031411A (en) * 1999-07-21 2001-02-06 Sanada Tire Hanbai Kk Method for producing carbon raw material and device therefor
JP2001065831A (en) * 1999-08-24 2001-03-16 Meidensha Corp Method for heat treating matter to be treated
JP2001082714A (en) * 1999-09-08 2001-03-30 Ishikawajima Harima Heavy Ind Co Ltd Waste thermal decomposition gasification device

Patent Citations (11)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH0947795A (en) * 1995-08-09 1997-02-18 Kubota Corp Device for carbonizing and regenerating organic waste
JPH09235559A (en) * 1996-02-22 1997-09-09 Noel Krc Energ & Umwelttechnik Gmbh Utilization of residue and waste in terms of material and energy in upright furnace
JPH1076138A (en) * 1996-09-04 1998-03-24 Tadahiro Omi Treatment of waste gas containing halogen compound
JPH10235308A (en) * 1997-02-24 1998-09-08 Meidensha Corp Dechlorination treatment of moisture-containing matter to be treated
JPH1114021A (en) * 1997-06-23 1999-01-22 Mitsui Eng & Shipbuild Co Ltd Waste disposal equipment
JP2000104082A (en) * 1998-09-30 2000-04-11 Kawasaki Steel Corp Method and apparatus for producing refuse derived solid fuel
JP2000296378A (en) * 1999-04-13 2000-10-24 Mitsubishi Heavy Ind Ltd Waste treatment
JP2001021126A (en) * 1999-07-09 2001-01-26 Takuma Co Ltd Apparatus for dry distilating, thermal cracking, melting and igniting waste material
JP2001031411A (en) * 1999-07-21 2001-02-06 Sanada Tire Hanbai Kk Method for producing carbon raw material and device therefor
JP2001065831A (en) * 1999-08-24 2001-03-16 Meidensha Corp Method for heat treating matter to be treated
JP2001082714A (en) * 1999-09-08 2001-03-30 Ishikawajima Harima Heavy Ind Co Ltd Waste thermal decomposition gasification device

Cited By (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2006082045A (en) * 2004-09-17 2006-03-30 Toru Kubota Treatment method for recycling of contaminant and its apparatus
JP4599127B2 (en) * 2004-09-17 2010-12-15 株式会社リバース Processing method and apparatus for waste recycling
JP2010125392A (en) * 2008-11-27 2010-06-10 Ihi Corp Sludge heating treatment method and sludge heating treatment apparatus
JP2014042908A (en) * 2012-07-28 2014-03-13 Sankyo Erec Co Ltd Method and apparatus for treating garbage
CN103100552A (en) * 2013-01-22 2013-05-15 蒲仁建 Method and system for carrying out thermal treatment on household garbage by using brick kiln
CN103100552B (en) * 2013-01-22 2015-04-01 蒲仁建 Method and system for carrying out thermal treatment on household garbage by using brick kiln

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