JP2869188B2 - Equipment for thermal decomposition treatment of solid substances harmful to the environment - Google Patents

Equipment for thermal decomposition treatment of solid substances harmful to the environment

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Publication number
JP2869188B2
JP2869188B2 JP4508584A JP50858492A JP2869188B2 JP 2869188 B2 JP2869188 B2 JP 2869188B2 JP 4508584 A JP4508584 A JP 4508584A JP 50858492 A JP50858492 A JP 50858492A JP 2869188 B2 JP2869188 B2 JP 2869188B2
Authority
JP
Japan
Prior art keywords
gas
pyrolysis
section
zone
furnace
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 - Lifetime
Application number
JP4508584A
Other languages
Japanese (ja)
Other versions
JPH06506246A (en
Inventor
ショソネ,ピエール
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.)
FURANSEEZU DO TERUMORISU SOC
Original Assignee
FURANSEEZU DO TERUMORISU SOC
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Filing date
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Application filed by FURANSEEZU DO TERUMORISU SOC filed Critical FURANSEEZU DO TERUMORISU SOC
Publication of JPH06506246A publication Critical patent/JPH06506246A/en
Application granted granted Critical
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Anticipated expiration legal-status Critical
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Classifications

    • CCHEMISTRY; METALLURGY
    • C10PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
    • C10BDESTRUCTIVE DISTILLATION OF CARBONACEOUS MATERIALS FOR PRODUCTION OF GAS, COKE, TAR, OR SIMILAR MATERIALS
    • C10B49/00Destructive distillation of solid carbonaceous materials by direct heating with heat-carrying agents including the partial combustion of the solid material to be treated
    • C10B49/02Destructive distillation of solid carbonaceous materials by direct heating with heat-carrying agents including the partial combustion of the solid material to be treated with hot gases or vapours, e.g. hot gases obtained by partial combustion of the charge
    • CCHEMISTRY; METALLURGY
    • C10PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
    • C10BDESTRUCTIVE DISTILLATION OF CARBONACEOUS MATERIALS FOR PRODUCTION OF GAS, COKE, TAR, OR SIMILAR MATERIALS
    • C10B19/00Heating of coke ovens by electrical means
    • CCHEMISTRY; METALLURGY
    • C10PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
    • C10BDESTRUCTIVE DISTILLATION OF CARBONACEOUS MATERIALS FOR PRODUCTION OF GAS, COKE, TAR, OR SIMILAR MATERIALS
    • C10B53/00Destructive distillation, specially adapted for particular solid raw materials or solid raw materials in special form
    • CCHEMISTRY; METALLURGY
    • C10PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
    • C10BDESTRUCTIVE DISTILLATION OF CARBONACEOUS MATERIALS FOR PRODUCTION OF GAS, COKE, TAR, OR SIMILAR MATERIALS
    • C10B7/00Coke ovens with mechanical conveying means for the raw material inside the oven
    • C10B7/14Coke ovens with mechanical conveying means for the raw material inside the oven with trucks, containers, or trays

Abstract

A system for the treatment of solid products whose disposal is detrimental to the environment, comprising a reactor successively incorporating a dehydration zone (1) and a thermolysis zone (2), characterised in that downstream of the thermolysis zone (2) this reactor comprises a cooling zone (3) and in that the dehydration zone is provided with a leakproof entry gate, the cooling zone is provided with a leakproof exit gate, and air locks isolate the thermolysis zone (2), on the one hand from the dehydration zone (1), on the other hand from the cooling zone (3) so as to limit the entries of air into the thermolysis zone during the introduction of the products and during the extraction of the residues, this thermolysis zone (2) being provided with a gas extraction line by virtue of which it is at reduced pressure. <IMAGE>

Description

【発明の詳細な説明】 本発明は、環境に害を与える固体物の熱分解処理用装
置に関する。
Description: TECHNICAL FIELD The present invention relates to an apparatus for thermally decomposing solid substances which cause harm to the environment.

このような固体物は、一般的に貯蔵又は焼却される。
前者の場合において、潜在的な危険は残って地下水汚染
の可能性によって深刻化される。後者の場合において、
焼却温度は、装置の早期消耗及び高い作動コストをもた
らすほど高い。さらに、焼却の生成気体は、管理されず
に大気に排出され、環境を汚染しないような十分な保証
を提供しない。
Such solids are generally stored or incinerated.
In the former case, the potential danger remains and is exacerbated by the potential for groundwater contamination. In the latter case,
The incineration temperature is high enough to result in premature equipment wear and high operating costs. In addition, the products of incineration are released uncontrolled into the atmosphere and do not provide sufficient assurance that they will not pollute the environment.

仏国特許第2106844号は、温度を高める(800から1300
℃に匹敵する)連続部分を具備する生ごみ処理装置を開
示しており、この連続部分を生ごみが多孔性の包装材料
で包装された後通過する。生ごみは、漸次脱水されて燃
焼する。しかしながら、この解決方法は、依然として早
期消耗及び高い作動コストをもたらす高温度を依然とし
て必要とする。
French patent 2106844 raises the temperature (800 to 1300
Disclosed is a garbage disposal apparatus comprising a continuous part (comparable to ° C.), through which the garbage is packaged with a porous packaging material. The garbage is gradually dehydrated and burns. However, this solution still requires high temperatures leading to premature wear and high operating costs.

本発明の目的果て固体物分解の連続的な管理によっ
て、例えば約600℃の適温での熱分解処理を可能にする
ことにより前述の欠点を克服することである。
It is an object of the present invention to overcome the above-mentioned disadvantages by allowing continuous pyrolysis at a suitable temperature, for example at about 600 ° C., by continuous management of solids decomposition.

本発明は、脱水部分及び熱分解部分を連続的に一体化
する炉装置を具備する環境に害を与える固体物の処理用
装置において、前記炉装置が熱分解部分の下流に冷却部
分を有し、脱水部分には気密の入口開閉機構が設けら
れ、冷却部分には気密の出口開閉機構機が設けられ、空
気遮断機構が、固体物の挿入中及び残留物の排出中に熱
分解部分に入る空気を制限するために、一方で脱水部分
から、また他方で冷却部分から熱分解部分を分離し、前
記熱分解部分にはそれを正圧状態に維持する気体排出管
が設けれられていることを特徴とする処理用装置を提供
する。
The present invention relates to an apparatus for treating a solid substance which harms the environment, comprising a furnace apparatus for continuously integrating a dehydration section and a pyrolysis section, wherein the furnace apparatus has a cooling section downstream of the pyrolysis section. The dewatering section is provided with an air-tight opening and closing mechanism, the cooling section is provided with an air-tight opening and closing mechanism, and the air shut-off mechanism enters the pyrolysis section during insertion of solids and discharge of residues. In order to restrict the air, the pyrolysis section is separated from the dewatering section on the one hand and from the cooling section on the other hand, and said pyrolysis section is provided with a gas discharge pipe which keeps it at a positive pressure. And a processing device characterized by the following.

前述された各部分は、結果的に孤立した室に分離され
る。
Each of the aforementioned parts is consequently separated into isolated chambers.

本発明の好適で組み合わせ可能な特徴により、 熱分解部分に遊離酸素は存在しない。 Due to the preferred and combinable features of the present invention, there is no free oxygen in the pyrolysis portion.

熱分解部分は、400℃から750℃の間の温度で800ミリ
バール以下の圧力である。
The pyrolysis section is at a temperature between 400 ° C. and 750 ° C. and a pressure of 800 mbar or less.

本発明の他の好適な特徴により、 処理される固体物はワゴンで炉装置へ挿入され、この
ワゴンは、例えばラック及びピニオン機構又は電磁駆動
装置によって、脱水室から熱分解室へ、また熱分解室か
ら冷却室へ連続的に通過する。ワゴンは、固体残留物、
例えばガラス、金属、石が冷却室からの排出時において
冷却後に容易に除去されるために、それ内に残るように
作られている。
According to another preferred feature of the invention, the solids to be treated are inserted into the furnace unit in a wagon, which is decomposed from the dehydration chamber to the pyrolysis chamber, for example by a rack and pinion mechanism or an electromagnetic drive. It passes continuously from the chamber to the cooling chamber. The wagon is a solid residue,
For example, glass, metal, and stone are made to remain within the cooling chamber as they are easily removed after cooling upon cooling.

脱水室及び熱分解室は、純粋な酸素又は空気及び熱分
解による分解の結果として生じる熱分解気体が供給され
る触媒分散パネルとして公知な熱反応装置と、室の内側
又は室の外側壁に取り付けられた電気加熱要素とによっ
て加熱される。
The dehydration and pyrolysis chambers are fitted with a thermal reactor known as a catalyst distribution panel to which pure oxygen or air and pyrolysis gases resulting from pyrolysis decomposition are supplied, and to the inside or outside walls of the chamber. And the electric heating element.

触媒分散パネルにおける熱分解気体の酸化によって発
生する二酸化炭素及び水蒸気は、固体物の熱の伝導及び
放射に貢献する。
Carbon dioxide and water vapor generated by the oxidation of the pyrolysis gas in the catalyst distribution panel contribute to the heat conduction and radiation of the solid matter.

熱分解による分解において形成された熱分解気体及び
触媒分散パネルにおいて形成される触媒酸化気体は、炉
装置からの排出時に気体洗浄装置内で冷却及び浄化さ
れ、この気体浄化装置において、水分は凝縮され、凝縮
不可能な気体及び凝縮された大きな原子量をもつ炭化水
素は分離される。
The pyrolysis gas formed in the pyrolysis and the oxidizing gas formed in the catalyst distribution panel are cooled and purified in the gas cleaning device when discharged from the furnace device, and the water is condensed in the gas cleaning device. Non-condensable gases and condensed hydrocarbons of high atomic weight are separated.

ハロゲン化硫黄化合物は、洗浄水への溶解によって気
体洗浄装置において除去される。
Sulfur halide compounds are removed in the gas scrubber by dissolution in the scrubbing water.

炉装置からの排出時における気体流は、熱分解による
分解中に形成される炭素を乗せてそれが冷却される気体
洗浄装置に向かう。
Upon discharge from the furnace apparatus, the gas stream is directed to a gas scrubber where the carbon formed during pyrolysis decomposition is loaded and cooled.

大きな原子量をもつ炭化水素及び炭素は、気体洗浄装
置からの排出時に沈殿タンクにおいて洗浄水から沈殿除
去された後、回収される。
Hydrocarbons and carbons with large atomic weights are recovered after being settled out of the wash water in a settling tank upon discharge from the gas scrubber.

気体洗浄装置からの排出時における気体流は、真空ポ
ンプによて吸い込まれる。
The gas flow at the time of discharge from the gas cleaning device is sucked by a vacuum pump.

真空ポンプからの気体は、二酸化炭素を除去するため
に、例えば炭酸カリウムの水溶液を有する気体洗浄装置
に送られる。
The gas from the vacuum pump is sent to a gas scrubber having, for example, an aqueous solution of potassium carbonate to remove carbon dioxide.

ハロゲン化硫黄化合物及び二酸化炭素の浄化された熱
分解気体は、炉装置を加熱するのに使用され、余剰分は
次の使用のために貯蔵される。
The purified pyrolysis gases of the sulfur halide compounds and carbon dioxide are used to heat the furnace equipment and the excess is stored for subsequent use.

熱分解室における熱的反応速度は、電気的な加熱、一
般的な温度測定による触媒加熱、気体流量、及び電流制
御装置を調整することによって管理される。
The rate of thermal reaction in the pyrolysis chamber is controlled by adjusting electrical heating, catalyst heating by common temperature measurements, gas flow rates, and current controllers.

本発明の目的、特徴、及び利点は、次の添付図面を参
照して限定されない例として与えられた以下の記述から
明らかになる。
Objects, features and advantages of the present invention will become apparent from the following description, given by way of non-limiting example with reference to the following accompanying drawings.

図1は、本発明による装置の平面図である。 FIG. 1 is a plan view of an apparatus according to the present invention.

図2は、この装置の炉の入口部分の正面図である。 FIG. 2 is a front view of an inlet portion of a furnace of the apparatus.

図3は、図2のA−A横断断面図である。 FIG. 3 is a sectional view taken along line AA of FIG.

図4は、支持部材へのパネル4の取り付けを示す拡大
図である。
FIG. 4 is an enlarged view showing attachment of the panel 4 to the support member.

図1は、本装置の主な計画を示しており、図2から4
は所定の詳細構造を示している。
FIG. 1 shows a main plan of the present apparatus, and FIGS.
Indicates a predetermined detailed structure.

本発明による装置は、処理される固体物が挿入され、
これらの固体物が脱水される室1と、部分的又は完全に
脱水さた固体物が熱分解温度、例えば約600℃(一般的
には400℃から750℃の間)の温度に加熱される熱分解室
2と、熱処理の固体残留物が常温に冷却される冷却室3
とを一つの装置に組み合わせる炉装置を具備する。この
炉装置における熱的交換は、600℃の平均温度で絶対的
に遊離酸素の存在なしに有利に実行される。
The device according to the invention has a solid object to be treated inserted therein,
The chamber 1 in which these solids are dewatered and the partially or completely dewatered solids are heated to a pyrolysis temperature, for example a temperature of about 600 ° C (typically between 400 ° C and 750 ° C) A pyrolysis chamber 2 and a cooling chamber 3 in which the solid residue of the heat treatment is cooled to room temperature.
And a furnace device for combining the above into one device. The heat exchange in this furnace arrangement is advantageously carried out at an average temperature of 600 ° C. and absolutely without the presence of free oxygen.

凝縮不可能な気体、より大きな原子量をもつ炭化水
素、炭素等の分解生成物は、この装置からの排出時に連
続的に監視され、必要ならばさらなる処理のために循環
される。
Decomposition products such as non-condensable gases, hydrocarbons with higher atomic weights, carbon, etc. are continuously monitored as they leave the unit and are recycled if necessary for further processing.

この温度における作動は、装置のいかなる重大な消耗
をも引き起こすことはなく、それにより、その寿命は延
長して作動コストは低減される。
Operation at this temperature does not cause any significant wear of the device, thereby extending its life and reducing operating costs.

各室は、押し上げ装置により作動されるギロチン式ド
ア23によって実質的に密閉されて互いに分離され、室1
及び2の間のドアと室2及び3の間のドアは、密閉され
たハウジング内で垂直に動き、持ち上げ装置はパッキン
によって密閉される。さらに、密閉さたドアが室1への
入口と室3からの出口に設けられ、それにより、脱水部
分1及び冷却部分は、外部及び/又は熱分解部分2から
計画的に分離される。これらのドアは、垂直又は水平に
動いてもよいが、炉装置の大きさ、利用空間、及び設計
者の意図に依存して回動されるように代えてもよい。
Each chamber is substantially sealed and separated from each other by a guillotine door 23 operated by a push-up device.
2 and the door between chambers 2 and 3 move vertically in a sealed housing and the lifting device is sealed by packing. Furthermore, closed doors are provided at the entrance to the chamber 1 and at the exit from the chamber 3, whereby the dewatering section 1 and the cooling section are deliberately separated from the external and / or pyrolysis section 2. These doors may move vertically or horizontally, but may alternatively be pivoted depending on the size of the furnace equipment, the space used and the intention of the designer.

入口及び出口ドアによって提供される密閉性は、外部
と室2内よりかなり低い適温の部分1及び3との間に存
在することが理解される。
It is understood that the seal provided by the inlet and outlet doors exists between the outside and the warmer parts 1 and 3 which are considerably lower than in the chamber 2.

室2へ空気が入ることを避けるために、空気遮断装置
を介して固体物が挿入され、また残留物が排出され、こ
の空気遮断装置は、固定物が脱水室へ挿入される時に熱
分解室から脱水室を、また残留物が第3室から排出され
る時に冷却室から熱分解室を、選択的に分離する。
In order to prevent air from entering the chamber 2, solids are inserted through the air shut-off device and the residue is discharged, and the air shut-off device is connected to the pyrolysis chamber when the fixed object is inserted into the dewatering chamber. From the cooling chamber as the residue is discharged from the third chamber.

炉装置の室1及び2は、熱損失を低減するために断熱
される(品目27)。
Chamber units 1 and 2 are insulated to reduce heat loss (item 27).

室1および2には、任意の適当な公知の種類の加熱手
段が設けられ、この二つの例4及び5が示されている。
室2内の温度は、例えば約600℃に保持され、一方室1
内は、100℃以上の低温度、例えば約120℃に保持され
る。
Chambers 1 and 2 are provided with any suitable known type of heating means, two examples 4 and 5 being shown.
The temperature in the chamber 2 is maintained, for example, at about 600 ° C.
The inside is kept at a low temperature of 100 ° C. or more, for example, about 120 ° C.

供給気体の触媒酸化が実行可能な温度に触媒分散パネ
ル4を加熱するための加熱要素25を組み込む触媒分散パ
ネル4は、室1及び2の天井に示されているが、同様
に、適当に側壁に取り付けられてもよい。これらのパネ
ルは外部から密閉されたハウジング内に存在する。図4
は、炉装置の内壁へのパネル4の固定の仕方と、シール
部材26の配置を示しており、このシール部材は、供給混
合気体(好ましくは、酸素と熱分解気体)を酸化させる
触媒パネル4を通し強制的に流すように機能する。室3
は、固体残留物を冷却するための、また触媒分散パネル
に供給された気体を加熱するための熱を回収するための
装置(図示せず)を備えるようにしてもよい。
The catalyst distribution panel 4, which incorporates a heating element 25 for heating the catalyst distribution panel 4 to a temperature at which catalytic oxidation of the feed gas is feasible, is shown at the ceiling of the chambers 1 and 2, but likewise suitably at the side walls It may be attached to. These panels reside in a housing that is sealed from the outside. FIG.
Shows how the panel 4 is fixed to the inner wall of the furnace apparatus and the arrangement of the seal member 26. This seal member is used to oxidize the mixed gas mixture (preferably, oxygen and pyrolysis gas). It works to force it to flow through. Room 3
The apparatus may include a device (not shown) for cooling the solid residue and for recovering heat for heating the gas supplied to the catalyst distribution panel.

電気加熱要素5は変換器6に接続され、本実施例にお
いて、これらの要素はシールされた貫通リード線を介す
る電気的接続により炉装置の内側に(外側に代えてもよ
い)壁に取り付けられて示されている。
The electric heating element 5 is connected to a transducer 6, which in this embodiment is mounted on the wall inside the furnace apparatus (alternatively outside) by means of an electrical connection via sealed through leads. Shown.

室2内の圧力は、800ミリバール以下の値、正確には5
00ミリバールに保持される。この圧力は、好ましくは、
室1、2、及び3において同じである。
The pressure in chamber 2 should be less than 800 mbar, exactly 5
It is kept at 00 mbar. This pressure is preferably
Same for chambers 1, 2, and 3.

室2から出る混合気体は、それを沈殿装置13へ排出
し、また水槽14から冷却された水が供給される気体洗浄
装置9へ流入し、この気体洗浄装置において、沈殿タン
ク13からの水は一般的な方法で処理される。タンク13の
水溶液から分離された凝縮された炭化水素及び炭素は、
貯蔵タンク17へ送られ、そこから必要とされる時に取り
出される。
The gas mixture exiting the chamber 2 discharges it into the settling device 13 and flows into the gas washing device 9 to which cooled water is supplied from the water tank 14, where the water from the settling tank 13 Processed in a general manner. The condensed hydrocarbons and carbon separated from the aqueous solution in the tank 13 are:
It is sent to a storage tank 17, from which it is removed when needed.

タンク9からの排出時に凝縮されない気体は、浄化タ
ンク11へ排出されるようにポンプ装置10によって吸い込
まれ、この浄化タンクにおいて、二酸化炭素は、タンク
14からの水に例えば炭酸カリウムを加えることによって
除去される。タンク11から出る時に、浄化された気体
は、圧縮器12によって圧縮されてタンク16に貯蔵され
る。
Gas that is not condensed when discharged from the tank 9 is sucked by the pump device 10 so as to be discharged to the purification tank 11, in which carbon dioxide is removed from the tank.
The water from 14 is removed, for example, by adding potassium carbonate. Upon exiting the tank 11, the purified gas is compressed by the compressor 12 and stored in the tank 16.

本実施例において、圧縮された気体は、さらに任意の
供給手段18からの圧縮空気、又は適用に依存して外部貯
蔵装置からの純粋な酸素を受け入れる混合器15を介して
触媒分散パネル4に供給される。混合気体は熱回収装置
7を通して流れ、この熱回収装置において、混合気体は
触媒の酸化反応の熱的な平衡を改善するために加熱され
る。図1は室1からの触媒反応気体の排出を示してい
る。これらの気体は、本質的に脱水及び触媒酸化からの
結果として二酸化炭素及び水蒸気を具備し、熱回収装置
7を通して冷却される。これらは、ポンプ装置8によっ
て吸い込まれ、煙突19へ排出する。
In this embodiment, the compressed gas is further supplied to the catalyst distribution panel 4 via a mixer 15 which receives compressed air from any supply means 18 or, depending on the application, pure oxygen from an external storage device. Is done. The gas mixture flows through a heat recovery device 7, in which the gas mixture is heated to improve the thermal equilibrium of the oxidation reaction of the catalyst. FIG. 1 shows the exhaust of the catalytic reaction gas from the chamber 1. These gases comprise carbon dioxide and water vapor essentially as a result of dehydration and catalytic oxidation and are cooled through the heat recovery unit 7. These are sucked by the pump device 8 and discharged to the chimney 19.

図2は、処理される固体物が設置されるワゴン20を示
し、このワゴンはラック及びピニオン装置21によって一
つの室から次の室へ動かされる。
FIG. 2 shows a wagon 20 in which the solids to be treated are installed, which wagon is moved from one chamber to the next by a rack and pinion device 21.

各ワゴンは駆動軸22によって同時に動かされる。 Each wagon is moved simultaneously by a drive shaft 22.

気体は、気体流れに炭素を乗せるために、室の端部に
おいて床の溝24によって室1及び2から排出される。
Gas is exhausted from chambers 1 and 2 by floor grooves 24 at the end of the chamber to entrain carbon in the gas stream.

気体洗浄装置は一般的なものである。 Gas cleaning devices are common.

上述された装置は、以下の利点を有する。 The device described above has the following advantages.

この装置は、炉装置の断面積又は炉装置の長さを変化
させることによって、又は必要とされる時に平行な複数
の炉装置を使用することによって、任意の量の固体物に
適用することができる。
This device can be applied to any quantity of solids by changing the cross-sectional area of the furnace device or the length of the furnace device, or by using multiple furnace devices in parallel when needed. it can.

本発明による装置は、良好な環境状態の保護の基で除
去される固体物を処理することができる。
The device according to the invention is capable of treating solids that are removed under the protection of good environmental conditions.

熱分解の生成物は、全ての汚染物が浄化され、任意の
次の使用以前に管理可能である。水溶液状態の水は、炭
化水素及び炭素が沈殿除去された後、一般的に処理され
る。ガラス、金属等の色々な不活性物は、最適な衛生状
態の基で再利用されることが可能である。熱分解炉装置
において蒸発しない重金属は、冷却後ワゴンで回収され
る。蒸発した重金属は、気体洗浄装置又は沈殿タンクで
の沈殿で回収される。
The product of the pyrolysis is cleansed of all contaminants and can be controlled before any subsequent use. Water in the form of an aqueous solution is generally treated after hydrocarbons and carbon have been precipitated and removed. Various inerts, such as glass, metal, etc., can be recycled under optimal hygiene. Heavy metals that do not evaporate in the pyrolysis furnace are collected by a wagon after cooling. The evaporated heavy metal is recovered by settling in a gas scrubber or settling tank.

最後に、本発明による装置は、炭素及び二酸化炭素の
形状で回収されたエネルギを貯蔵できること、又はいつ
の日にか他の場所でこれらを消費するために輸送できる
ことにより、並外れてエネルギを回収することができ
る。
Lastly, the device according to the invention is capable of storing energy recovered in the form of carbon and carbon dioxide, or being transported to consume them somewhere else, someday, thereby providing extraordinary energy recovery. Can be.

上記記載が限定しない例として与えられ、多数の変更
が本発明の範囲から逸脱することなく当業者により提案
されることは言うまでもない。
It goes without saying that the above description has been given by way of non-limiting example and that numerous modifications can be proposed by a person skilled in the art without departing from the scope of the present invention.

Claims (10)

(57)【特許請求の範囲】(57) [Claims] 【請求項1】脱水部分(1)及び熱分解部分(2)を連
続的に一体化する炉装置を具備する環境に害を与える固
体物の処理用装置において、前記炉装置が熱分解部分
(2)の下流に冷却部分(3)を有し、脱水部分には気
密の入口開閉機構が設けられ、冷却部分には気密の出口
開閉機構機が設けられ、空気遮断機構が、固体物の挿入
中及び残留物の排出中に熱分解部分に入る空気を制限す
るために、一方で脱水部分(1)から、また他方で冷却
部分(3)から熱分解部分(2)を分離し、前記熱分解
部分(2)にはそれを正圧状態に維持する気体排出管が
設けられていることを特徴とする処理用装置。
1. An apparatus for treating a solid which is harmful to the environment, comprising a furnace device for continuously integrating a dewatering section (1) and a pyrolysis section (2), wherein the furnace apparatus comprises a pyrolysis section (1). A cooling part (3) is provided downstream of 2), an airtight inlet opening / closing mechanism is provided in the dewatering part, an airtight outlet opening / closing mechanism is provided in the cooling part, and an air shutoff mechanism is provided for inserting solid objects. In order to limit the air entering the pyrolysis section during the discharge of the medium and residues, the pyrolysis section (2) is separated from the dehydration section (1) on the one hand and from the cooling section (3) on the other hand, A processing apparatus characterized in that the decomposition part (2) is provided with a gas discharge pipe for maintaining the decomposition part at a positive pressure.
【請求項2】熱分解部分(2)は遊離酸素無く維持され
る請求項1に記載の装置。
2. The apparatus according to claim 1, wherein the pyrolysis section is maintained free of oxygen.
【請求項3】熱分解部分(2)は400℃から750℃の間の
温度で800ミリバール以下の圧力であることを特徴とす
る請求項1又は2に記載の装置。
3. The device according to claim 1, wherein the pyrolysis section is at a temperature between 400 ° C. and 750 ° C. and a pressure of 800 mbar or less.
【請求項4】固体物は、ラック及びピニオン装置のよう
な機構(21)によって炉装置を通して動かされるワゴン
(20)によって運搬されることを特徴とする請求項1か
ら3のいずれかに記載の装置。
4. A device according to claim 1, wherein the solids are conveyed by a wagon (20) which is moved through the furnace device by a mechanism (21) such as a rack and pinion device. apparatus.
【請求項5】脱水室(1)及び熱分解部分(2)は、触
媒分散パネル(4)を有する加熱手段によって加熱され
ることを特徴とする請求項1から4のいずれかに記載の
装置。
5. The apparatus according to claim 1, wherein the dehydration chamber and the pyrolysis section are heated by heating means having a catalyst distribution panel. .
【請求項6】触媒分散パネルは、熱分解部分から少なく
とも一部の気体が供給されることを特徴とする請求項5
に記載の装置。
6. The catalyst dispersing panel according to claim 5, wherein at least a part of the gas is supplied from a pyrolysis portion.
An apparatus according to claim 1.
【請求項7】触媒酸化によって発生する水蒸気は、処理
される固体物の伝導及び放射による加熱に貢献すること
を特徴とする請求項5及び6に記載の装置。
7. Apparatus according to claim 5, wherein the steam generated by the catalytic oxidation contributes to the conduction and radiation heating of the solids to be treated.
【請求項8】熱分解による分解処理で形成される熱分解
気体及び触媒酸化処理で形成される気体は、ハロゲン化
硫黄化合物及び二酸化炭素を除去するために気体洗浄装
置において冷却及び浄化されることを特徴とする請求項
1から7のいずれかに記載の装置。
8. A pyrolysis gas formed by a decomposition process by thermal decomposition and a gas formed by a catalytic oxidation process are cooled and purified in a gas cleaning device to remove sulfur halide compounds and carbon dioxide. Apparatus according to any of the preceding claims, characterized in that:
【請求項9】気体洗浄装置の排出時における気体は真空
ポンプ装置によって吸い込まれることを特徴とする請求
項8に記載の装置。
9. The apparatus according to claim 8, wherein the gas when the gas cleaning apparatus is discharged is sucked by a vacuum pump device.
【請求項10】熱的反応速度は、電気的加熱、一般的な
温度測定を使用する触媒加熱、気体流量、及び電流制御
装置を制御することによって管理されることを特徴とす
る請求項1から9のいずれかに記載の装置
10. The method of claim 1, wherein the thermal reaction rate is controlled by controlling electrical heating, catalyst heating using general temperature measurement, gas flow, and current control. An apparatus according to any one of claims 9
JP4508584A 1991-03-20 1992-03-19 Equipment for thermal decomposition treatment of solid substances harmful to the environment Expired - Lifetime JP2869188B2 (en)

Applications Claiming Priority (2)

Application Number Priority Date Filing Date Title
FR91/03675 1991-03-20
FR9103675A FR2674149B1 (en) 1991-03-20 1991-03-20 SYSTEM FOR THE TREATMENT BY THERMOLYSIS, IN TOTAL OXYGEN ABSENCE OF SOLID PRODUCTS WHOSE REJECTION IS HARMFUL FOR THE ENVIRONMENT.

Publications (2)

Publication Number Publication Date
JPH06506246A JPH06506246A (en) 1994-07-14
JP2869188B2 true JP2869188B2 (en) 1999-03-10

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EP (1) EP0505278B1 (en)
JP (1) JP2869188B2 (en)
AT (1) ATE113309T1 (en)
CA (1) CA2105289C (en)
DE (1) DE69200560T2 (en)
DK (1) DK0505278T3 (en)
ES (1) ES2062871T3 (en)
FR (1) FR2674149B1 (en)
RU (1) RU2097402C1 (en)
WO (1) WO1992016599A1 (en)

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FR2705103B1 (en) * 1993-05-11 1995-08-04 Thermolyse Ste Francaise PROCESS AND PLANT FOR THE TREATMENT, BY VACUUM THERMOLYSIS, OF SOLID PRODUCTS, WITH CONTINUOUS SEPARATION AND RECOVERY OF A LIQUID FRACTION OF THESE PRODUCTS.
GB2280451B (en) * 1993-06-29 1998-01-28 Leybold Durferrit Gmbh Process for embrittling and crushing of plastics/rubber
DE4418562A1 (en) * 1993-06-29 1995-01-12 Leybold Durferrit Gmbh Method and device for treating material consisting essentially of plastic or rubber
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EP0672743B2 (en) * 1994-03-18 2001-05-16 Dieter Uschkoreit Process and apparatus for the thermal treatment of materials containing vaporizable substances
DE69628356T2 (en) * 1995-01-25 2004-04-29 I.T.B. S.R.L. Method and device for the pyrolytic treatment of waste containing organic material, in particular the treatment of household waste
FR2735707A1 (en) 1995-06-20 1996-12-27 Minghi Osvald Rehabilitation process for treating polluted soils in-situ
EP0783456B1 (en) * 1995-06-28 2001-10-17 Liquid Carbonic Industrias S/A Process for the realization of endothermic decomposition of pyrites, producing gases and solid residues
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KR100282759B1 (en) 1996-10-15 2001-05-02 쏘시에뜨 프랑세즈 드 떼르몰리즈 Waste treatment facility by hot gas injection into treated material and recycle of generated pyrolysis gas
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Also Published As

Publication number Publication date
FR2674149A1 (en) 1992-09-25
ATE113309T1 (en) 1994-11-15
CA2105289C (en) 2001-03-13
WO1992016599A1 (en) 1992-10-01
FR2674149B1 (en) 1994-04-15
CA2105289A1 (en) 1992-09-21
ES2062871T3 (en) 1994-12-16
EP0505278B1 (en) 1994-10-26
DE69200560T2 (en) 1995-04-27
DK0505278T3 (en) 1995-01-02
EP0505278A1 (en) 1992-09-23
JPH06506246A (en) 1994-07-14
DE69200560D1 (en) 1994-12-01
RU2097402C1 (en) 1997-11-27

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