JPH10238728A - Heat treatment facility for waste and method therefor - Google Patents
Heat treatment facility for waste and method thereforInfo
- Publication number
- JPH10238728A JPH10238728A JP10050063A JP5006398A JPH10238728A JP H10238728 A JPH10238728 A JP H10238728A JP 10050063 A JP10050063 A JP 10050063A JP 5006398 A JP5006398 A JP 5006398A JP H10238728 A JPH10238728 A JP H10238728A
- Authority
- JP
- Japan
- Prior art keywords
- pyrolysis furnace
- waste
- gas
- process gas
- screw housing
- 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.)
- Withdrawn
Links
Classifications
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23G—CREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
- F23G5/00—Incineration of waste; Incinerator constructions; Details, accessories or control therefor
- F23G5/20—Incineration of waste; Incinerator constructions; Details, accessories or control therefor having rotating or oscillating drums
-
- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10B—DESTRUCTIVE DISTILLATION OF CARBONACEOUS MATERIALS FOR PRODUCTION OF GAS, COKE, TAR, OR SIMILAR MATERIALS
- C10B1/00—Retorts
- C10B1/10—Rotary retorts
-
- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10B—DESTRUCTIVE DISTILLATION OF CARBONACEOUS MATERIALS FOR PRODUCTION OF GAS, COKE, TAR, OR SIMILAR MATERIALS
- C10B53/00—Destructive distillation, specially adapted for particular solid raw materials or solid raw materials in special form
-
- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10J—PRODUCTION OF PRODUCER GAS, WATER-GAS, SYNTHESIS GAS FROM SOLID CARBONACEOUS MATERIAL, OR MIXTURES CONTAINING THESE GASES; CARBURETTING AIR OR OTHER GASES
- C10J3/00—Production of combustible gases containing carbon monoxide from solid carbonaceous fuels
- C10J3/58—Production of combustible gases containing carbon monoxide from solid carbonaceous fuels combined with pre-distillation of the fuel
- C10J3/60—Processes
- C10J3/64—Processes with decomposition of the distillation products
- C10J3/66—Processes with decomposition of the distillation products by introducing them into the gasification zone
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23G—CREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
- F23G5/00—Incineration of waste; Incinerator constructions; Details, accessories or control therefor
- F23G5/02—Incineration of waste; Incinerator constructions; Details, accessories or control therefor with pretreatment
- F23G5/027—Incineration of waste; Incinerator constructions; Details, accessories or control therefor with pretreatment pyrolising or gasifying stage
- F23G5/0273—Incineration of waste; Incinerator constructions; Details, accessories or control therefor with pretreatment pyrolising or gasifying stage using indirect heating
-
- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10J—PRODUCTION OF PRODUCER GAS, WATER-GAS, SYNTHESIS GAS FROM SOLID CARBONACEOUS MATERIAL, OR MIXTURES CONTAINING THESE GASES; CARBURETTING AIR OR OTHER GASES
- C10J2200/00—Details of gasification apparatus
- C10J2200/15—Details of feeding means
- C10J2200/158—Screws
-
- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10J—PRODUCTION OF PRODUCER GAS, WATER-GAS, SYNTHESIS GAS FROM SOLID CARBONACEOUS MATERIAL, OR MIXTURES CONTAINING THESE GASES; CARBURETTING AIR OR OTHER GASES
- C10J2300/00—Details of gasification processes
- C10J2300/09—Details of the feed, e.g. feeding of spent catalyst, inert gas or halogens
- C10J2300/0953—Gasifying agents
- C10J2300/0959—Oxygen
-
- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10J—PRODUCTION OF PRODUCER GAS, WATER-GAS, SYNTHESIS GAS FROM SOLID CARBONACEOUS MATERIAL, OR MIXTURES CONTAINING THESE GASES; CARBURETTING AIR OR OTHER GASES
- C10J2300/00—Details of gasification processes
- C10J2300/18—Details of the gasification process, e.g. loops, autothermal operation
- C10J2300/1861—Heat exchange between at least two process streams
- C10J2300/1869—Heat exchange between at least two process streams with one stream being air, oxygen or ozone
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23G—CREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
- F23G2201/00—Pretreatment
- F23G2201/10—Drying by heat
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23G—CREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
- F23G2201/00—Pretreatment
- F23G2201/40—Gasification
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23G—CREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
- F23G2205/00—Waste feed arrangements
- F23G2205/12—Waste feed arrangements using conveyors
- F23G2205/121—Screw conveyor
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23L—SUPPLYING AIR OR NON-COMBUSTIBLE LIQUIDS OR GASES TO COMBUSTION APPARATUS IN GENERAL ; VALVES OR DAMPERS SPECIALLY ADAPTED FOR CONTROLLING AIR SUPPLY OR DRAUGHT IN COMBUSTION APPARATUS; INDUCING DRAUGHT IN COMBUSTION APPARATUS; TOPS FOR CHIMNEYS OR VENTILATING SHAFTS; TERMINALS FOR FLUES
- F23L2900/00—Special arrangements for supplying or treating air or oxidant for combustion; Injecting inert gas, water or steam into the combustion chamber
- F23L2900/07005—Injecting pure oxygen or oxygen enriched air
-
- Y—GENERAL 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
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02E—REDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
- Y02E20/00—Combustion technologies with mitigation potential
- Y02E20/12—Heat utilisation in combustion or incineration of waste
-
- Y—GENERAL 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
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02E—REDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
- Y02E20/00—Combustion technologies with mitigation potential
- Y02E20/34—Indirect CO2mitigation, i.e. by acting on non CO2directly related matters of the process, e.g. pre-heating or heat recovery
-
- Y—GENERAL 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
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02P—CLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
- Y02P20/00—Technologies relating to chemical industry
- Y02P20/10—Process efficiency
- Y02P20/129—Energy recovery, e.g. by cogeneration, H2recovery or pressure recovery turbines
Landscapes
- Chemical & Material Sciences (AREA)
- Engineering & Computer Science (AREA)
- Oil, Petroleum & Natural Gas (AREA)
- Organic Chemistry (AREA)
- Mechanical Engineering (AREA)
- General Engineering & Computer Science (AREA)
- Materials Engineering (AREA)
- Combustion & Propulsion (AREA)
- Gasification And Melting Of Waste (AREA)
- Processing Of Solid Wastes (AREA)
Abstract
Description
【0001】[0001]
【発明の属する技術分野】本発明は廃棄物を熱処理する
ための設備および方法に関する。The present invention relates to an apparatus and a method for heat treating waste.
【0002】[0002]
【従来の技術】廃棄物の熱処理の分野においては乾留燃
焼法が知られている。この方法で作動する設備は例えば
ヨーロッパ特許出願公開第A0302310号明細書あ
るいは1996年シーメンス社発行の社報「乾留燃焼
法、方法説明書(Die Schwel-Brenn-Anlage 、eine Ver
fahrensbeschreibung )」に開示されている。乾留燃焼
法は主に二つの段階から成っている。その第1の段階に
おいて供給された廃棄物あるいは塵芥は乾留室あるいは
また加熱室(熱分解炉)に入れられ、乾留され即ち酸素
に乏しい雰囲気内において300〜600℃の温度で熱
処理される。この熱処理によって乾留室の中にプロセス
ガスおよび熱分解残留物が生ずる。熱分解残留物は可燃
部分と不燃部分から成っている。例えば金属やガラスの
ような不燃部分の有用物質は選別され、後から行われる
リサイクルプロセスにほぼ完全に選別して送られる。乾
留燃焼法の第2の段階において、可燃性の熱分解残留物
はプロセスガスと一緒に高温燃焼室の中で約1200℃
の温度で燃焼される。2. Description of the Related Art In the field of heat treatment of waste, a dry distillation combustion method is known. Equipment operating in this manner is described, for example, in EP-A-030310 or in the company report published by Siemens AG in 1996, entitled "Distillation Combustion Method, Instruction Manual (Die Schwel-Brenn-Anlage, eine Ver.
fahrensbeschreibung) ". The carbonization combustion method mainly consists of two stages. The waste or refuse supplied in the first stage is placed in a carbonization chamber or a heating chamber (pyrolysis furnace) and carbonized, that is, heat-treated at a temperature of 300 to 600 ° C. in an oxygen-poor atmosphere. This heat treatment produces process gases and pyrolysis residues in the carbonization chamber. The pyrolysis residue consists of combustible and non-combustible parts. Useful materials in non-combustible parts, such as metals and glass, are sorted and sent almost completely to a later recycling process. In the second stage of the carbonization combustion process, the flammable pyrolysis residue is combined with the process gas in a hot combustion chamber at about 1200 ° C.
Burned at a temperature of
【0003】公知の熱分解炉は、長手方向に延びその長
手軸線を中心として例えば2〜4rpmで回転する円筒
状の加熱室である。この加熱室はその回転運動によって
廃棄物をその長手方向に搬送できるようにするためにそ
の長手方向において水平線に対して傾斜している。従っ
て熱分解炉内において廃棄物は搬入部から排出部に搬送
され、その搬送中に乾留される。廃棄物はその搬入部で
熱分解炉の中に入れられ、搬出部で熱分解炉から出され
る。A known pyrolysis furnace is a cylindrical heating chamber that extends in the longitudinal direction and rotates about its longitudinal axis at, for example, 2 to 4 rpm. The heating chamber is inclined with respect to the horizontal in its longitudinal direction so that its rotational movement allows waste to be transported in its longitudinal direction. Therefore, the waste is transported from the loading section to the discharging section in the pyrolysis furnace, and carbonized during the transport. The waste is put into the pyrolysis furnace at the entrance and discharged from the pyrolysis furnace at the exit.
【0004】この公知の設備においては、熱分解炉内に
熱分解の際に生ずるプロセスガスも同様に搬出部におい
て熱分解炉から取り出される。従って熱分解炉内におけ
るプロセスガスおよび廃棄物の搬送は同方向に行われ
る。この結果、搬入部には比較的冷たい廃棄物が存在
し、その上に比較的冷たい水蒸気飽和プロセスガスが存
在する。このために搬入部の近くにおける乾燥過程は困
難になる。搬出部で排出されるプロセスガスは乾燥過程
の際に廃棄物から蒸発した水分を含んでいるので、全て
の水蒸気をまず乾留室内でそこにかかる300〜600
℃のプロセス温度に加熱しなければならない。このため
に廃棄物の乾燥および熱分解にとって必要なエネルギー
が増加する。更に水蒸気の濃度が高いために、この不活
性成分としての水蒸気を高温燃焼室の中でプロセスガス
の可燃成分を燃焼する際にエネルギーを供給することな
しに、追加的に約1200℃まで加熱しなければならな
いので、プロセスガスの発熱量が減少される。In this known facility, the process gas generated during the pyrolysis in the pyrolysis furnace is likewise taken out of the pyrolysis furnace at the carry-out section. Therefore, the transport of the process gas and the waste in the pyrolysis furnace is performed in the same direction. As a result, relatively cool waste is present at the carry-in point, and relatively cool steam-saturated process gas is present thereon. This makes the drying process near the loading section difficult. Since the process gas discharged from the carry-out section contains water evaporated from the waste during the drying process, all the steam is first introduced into the carbonization chamber by 300-600.
It must be heated to a process temperature of ° C. This increases the energy required for drying and pyrolysis of the waste. Further, due to the high concentration of steam, the steam as an inert component is additionally heated to about 1200 ° C. without supplying energy when burning the combustible components of the process gas in the high temperature combustion chamber. The heating value of the process gas is reduced.
【0005】[0005]
【発明が解決しようとする課題】本発明の課題は設備の
運転にとって必要なエネルギーが減少されるような廃棄
物の熱処理設備を提供することにある。更に本発明の課
題はそのような廃棄物の熱処理方法を提供することにあ
る。SUMMARY OF THE INVENTION It is an object of the present invention to provide a waste heat treatment facility in which the energy required for the operation of the facility is reduced. It is a further object of the present invention to provide such a heat treatment method for waste.
【0006】[0006]
【課題を解決するための手段】本発明の最初の課題は請
求項1に記載の設備によって解決される。本発明に基づ
く廃棄物の熱処理設備は、廃棄物を搬送し乾留するため
の長手方向に延びる熱分解炉を有し、この熱分解炉がそ
の一端に廃棄物の搬入部を、反対側端に乾留の際に生ず
る熱分解残留物の搬出部を有し、前記搬入部に熱分解炉
の中で生じたプロセスガスの出口が配置されている。こ
の処置によって、熱分解炉内で生じたプロセスガスの少
なくとも一部が廃棄物の搬送方向と逆向きに導かれる。
これによって搬入部における比較的冷たい廃棄物の上に
高温の乾燥プロセスガスが存在するので、廃棄物は搬入
部において既に有効に乾燥され加熱される。従って乾留
過程の開始は搬入部の近くに移動される。更に水蒸気の
少なくとも一部が搬入部で取り出されるので、この水蒸
気を熱分解炉の中およびそれに続く高温燃焼室の中にお
けるプロセス温度に加熱する必要がなくなるので、設備
の運転にとって必要なエネルギーが減少される。SUMMARY OF THE INVENTION The first object of the present invention is solved by a device according to claim 1. The waste heat treatment equipment according to the present invention has a longitudinally extending pyrolysis furnace for transporting and carbonizing the waste, the pyrolysis furnace having a waste carry-in section at one end thereof and an opposite end at the opposite end. It has a discharge section for the pyrolysis residue generated during the carbonization, and an outlet for the process gas generated in the pyrolysis furnace is arranged at the input section. By this measure, at least a part of the process gas generated in the pyrolysis furnace is guided in a direction opposite to the direction in which the waste is transported.
As a result, the waste is already effectively dried and heated at the input, since the hot drying process gas is present on the relatively cold waste at the input. Therefore, the start of the carbonization process is moved closer to the loading section. Furthermore, since at least a portion of the steam is removed at the inlet, it is not necessary to heat this steam to the process temperature in the pyrolysis furnace and subsequently in the hot combustion chamber, thus reducing the energy required for the operation of the installation. Is done.
【0007】本発明の有利な実施態様において、熱分解
炉はその中に開口する酸素含有ガスの供給配管に接続さ
れている。このような供給配管は例えばドイツ特許出願
公開第4327953A1号明細書で知られている。本
発明をこの処置と組み合わせることによって、熱分解炉
内で生ずるプロセスガスおよび熱分解残留物を部分的に
酸化する個所も搬入部に移動され、熱分解炉の中央範囲
で既に廃棄物が追加的に加熱されるという利点が得られ
る。In an advantageous embodiment of the invention, the pyrolysis furnace is connected to an oxygen-containing gas supply line opening therein. Such a supply line is known, for example, from DE-A 43 27 953 A1. By combining the present invention with this measure, the point of partial oxidation of the process gases and pyrolysis residues generated in the pyrolysis furnace is also moved to the input, where additional waste already exists in the central area of the pyrolysis furnace. The advantage of being heated to a low temperature.
【0008】特に供給配管に酸素含有ガスを加熱するた
めの熱交換器が接続されていると有利である。It is particularly advantageous if a heat exchanger for heating the oxygen-containing gas is connected to the supply line.
【0009】本発明の有利な実施態様においては、熱分
解炉に前置接続された廃棄物用スクリューコンベヤのス
クリューハウジングは少なくともその長さの一部にわた
ってプロセスガスで加熱される。これにより廃棄物は熱
分解炉の中に入る前に予め加熱されることになる。In an advantageous embodiment of the invention, the screw housing of the waste screw conveyor upstream of the pyrolysis furnace is heated with the process gas at least over a part of its length. This results in the waste being preheated before entering the pyrolysis furnace.
【0010】特にスクリューハウジングは少なくともそ
の長さの一部にわたってプロセスガスを案内する通路の
中に配置されている。このようにしてスクリューハウジ
ングは全周が加熱され、プロセスガスから廃棄物への熱
搬送が改良される。[0010] In particular, the screw housing is arranged in a passage for guiding the process gas over at least a part of its length. In this way, the screw housing is heated all around and the heat transfer from the process gas to the waste is improved.
【0011】好適にはスクリューハウジングは少なくと
もその長さの一部が、熱分解炉の外で発生された加熱ガ
スで加熱され、その加熱ガスはプロセスガスを案内する
通路とスクリューハウジングとの間に配置されている加
熱ジャケットを通して導かれる。この処置によってプロ
セスガス内に存在する水蒸気がスクリューハウジングの
比較的冷たい表面で凝縮することが避けられる。[0011] Preferably, the screw housing is heated, at least for part of its length, with a heating gas generated outside the pyrolysis furnace, the heating gas being provided between the passage for guiding the process gas and the screw housing. It is guided through a heating jacket arranged. This measure prevents the water vapor present in the process gas from condensing on the relatively cold surface of the screw housing.
【0012】本発明の第2の課題は請求項8に記載の方
法によって解決される。本発明に基づく廃棄物の熱処理
方法においては、廃棄物が搬入部で長手方向において搬
入部から搬出部に向って延びる熱分解炉に入れられ、熱
分解炉の長手方向に搬送され、その際に乾留され、その
乾留の際に生ずるプロセスガスの少なくとも一部が熱分
解炉から搬出部において取り出される。A second object of the invention is achieved by a method according to claim 8. In the waste heat treatment method according to the present invention, the waste is put into the pyrolysis furnace extending from the loading section toward the unloading section in the longitudinal direction at the loading section, and is transported in the longitudinal direction of the pyrolysis furnace. The carbonization is performed, and at least a part of the process gas generated during the carbonization is removed from the pyrolysis furnace at the carry-out section.
【0013】本発明の他の有利な実施態様は各従属請求
項に記載されている。[0013] Further advantageous embodiments of the invention are described in the respective dependent claims.
【0014】[0014]
【実施例】以下図面に示した実施例を参照して本発明を
詳細に説明する。DETAILED DESCRIPTION OF THE PREFERRED EMBODIMENTS The present invention will be described below in detail with reference to the embodiments shown in the drawings.
【0015】図1において廃棄物Aの熱処理設備は、廃
棄物Aを長手方向6に延びる熱分解炉4に搬送するスク
リューコンベヤ2例えば詰込み形スクリューコンベヤを
有している。熱分解炉4の中で廃棄物Aの熱分解あるい
は乾留が行われる。熱分解炉4はこのためにその中に配
置された加熱管8を通して導かれる加熱ガスHGで加熱
される。加熱ガスHGは熱分解炉4の外側における燃焼
過程(図示せず)で発生される。In FIG. 1, the heat treatment equipment for the waste A has a screw conveyor 2 for transporting the waste A to a pyrolysis furnace 4 extending in the longitudinal direction 6, for example, a packed screw conveyor. In the pyrolysis furnace 4, the pyrolysis or dry distillation of the waste A is performed. The pyrolysis furnace 4 is heated for this purpose by a heating gas HG which is guided through a heating tube 8 arranged therein. The heating gas HG is generated in a combustion process (not shown) outside the pyrolysis furnace 4.
【0016】円筒状の熱分解炉4は水平線に対して傾斜
しており、その長手軸線6を中心として回転可能に支持
され、気密回転ブッシング9を介して固定設備部分に結
合されている。熱分解炉4の傾斜および回転運動によっ
て廃棄物Aはゆっくりと熱分解炉4の搬入部10から矢
印12の方向に搬出部14に向けて搬送される。その搬
入部10においてスクリューコンベヤ2が熱分解炉4に
開口し、搬出部14には熱分解残留物Rを受けるための
室16が接続されている。熱分解残留物Rは後置接続さ
れた選別装置18に導入され、そこで微細成分Fと粗大
成分Gとに分けられる。微細成分Fおよび熱分解炉4の
内部における乾留の際に生ずるプロセスガスSGは高温
燃焼室(図示せず)に導かれ、そこで一緒に燃焼され
る。The cylindrical pyrolysis furnace 4 is inclined with respect to a horizontal line, is supported rotatably about its longitudinal axis 6, and is connected to a fixed equipment part via an airtight rotary bushing 9. The waste A is slowly conveyed from the loading section 10 of the pyrolysis furnace 4 to the discharge section 14 in the direction of the arrow 12 by the tilting and rotating motion of the pyrolysis furnace 4. The screw conveyor 2 opens into the pyrolysis furnace 4 at the loading section 10, and a chamber 16 for receiving the pyrolysis residue R is connected to the unloading section 14. The pyrolysis residue R is introduced into a downstream sorting device 18 where it is divided into a fine component F and a coarse component G. The fine component F and the process gas SG generated during the dry distillation inside the pyrolysis furnace 4 are led to a high-temperature combustion chamber (not shown), where they are burned together.
【0017】熱分解炉4はその搬入部10において円筒
状通路20に接続されている。この通路20はスクリュ
ーコンベヤ2のスクリューハウジング22を少なくとも
その長さの一部にわたって包囲している。この通路20
は排気室24に開口し、この排気室24からプロセスガ
スSGが例えば誘引送風機(図示せず)によって排出さ
れる。円筒状通路20および排気室24は搬入部10に
おいて熱分解炉4内で生ずるプロセスガスSGの少なく
とも一部に対する出口を形成している。プロセスガス案
内通路20とスクリューコンベヤ2のハウジング22と
の間に同様に円筒状の加熱ジャケット25が設けられて
いる。これは例えば管系26、27を有し(図2参
照)、熱分解炉4の外側で発生した加熱ガスHGの部分
流によってまず右に向けて、それから左に向けて貫流さ
れる。この加熱ジャケット25によって、比較的冷たい
スクリューハウジング22においてプロセスガスSG内
の水蒸気が凝縮することが確実に防止される。The pyrolysis furnace 4 is connected to a cylindrical passage 20 at a carry-in portion 10 thereof. This passage 20 surrounds the screw housing 22 of the screw conveyor 2 at least over part of its length. This passage 20
Opens into an exhaust chamber 24 from which the process gas SG is exhausted by, for example, an induced blower (not shown). The cylindrical passage 20 and the exhaust chamber 24 form an outlet for at least a part of the process gas SG generated in the pyrolysis furnace 4 at the loading section 10. Similarly, a cylindrical heating jacket 25 is provided between the process gas guide passage 20 and the housing 22 of the screw conveyor 2. It has, for example, tubing 26, 27 (see FIG. 2) and is first passed to the right and then to the left by a partial flow of the heating gas HG generated outside the pyrolysis furnace 4. The heating jacket 25 reliably prevents water vapor in the process gas SG from condensing in the relatively cold screw housing 22.
【0018】搬出部14に配置された室16にプロセス
ガスSGに対する搬出側出口28が設けられ、この出口
28を通してもプロセスガスSGが熱分解炉4および室
16から排出される。A discharge port 28 for the process gas SG is provided in the chamber 16 disposed in the discharge section 14, and the process gas SG is discharged from the pyrolysis furnace 4 and the chamber 16 through this outlet 28.
【0019】搬入側出口24および搬出側出口28から
それぞれ取り出されたプロセスガスSGは例えば共通の
誘引送風機によって排出される。この場合搬出部から取
り出されるプロセスガスSGと搬入部から取り出される
プロセスガスSGとの量の比率は適当な調整弁あるいは
調整フラッパによって制御される。しかし互いに独立し
て駆動される二つの誘引送風機を設けることもでき、そ
の場合、搬入側出口24および搬出側出口28にそれぞ
れ接続された誘引送風機の制御に応じて、廃棄物Aの搬
送方向12と逆向きに破線矢印29の方向に流れるプロ
セスガス流の分量が調整される。The process gas SG respectively taken out from the carry-in side outlet 24 and the carry-out side outlet 28 is exhausted by, for example, a common induction blower. In this case, the ratio of the amount of the process gas SG taken out from the carry-out portion to the amount of the process gas SG taken out from the carry-in portion is controlled by an appropriate regulating valve or regulating flapper. However, it is also possible to provide two induction blowers that are driven independently of each other, in which case the transfer direction 12 of the waste A is controlled according to the control of the induction blowers connected to the carry-in outlet 24 and the carry-out outlet 28, respectively. In the opposite direction, the amount of the process gas flow flowing in the direction of the dashed arrow 29 is adjusted.
【0020】熱分解炉4の内部に、酸素を含有するガス
BG例えば酸素で豊富化された空気あるいは純粋な酸素
を供給する供給配管30が開口している。この供給配管
30の自由端32で熱分解炉4の中に流出するガスBG
はプロセスガスおよび熱分解残留物の酸化によって熱分
解炉4の中に追加的に熱を導入させる。プロセスガスS
Gの対向流によって搬入部の温度が補助的に熱エネルギ
ーを導入しなくても、ドイツ特許出願公開第43279
53A1号明細書で知られている実施形態に比べて高め
られるので、酸化の開始に必要な反応条件(反応パート
ナー:プロセスガスSGと熱分解残留物Rの存在並びに
酸化の発生にとって必要な反応温度)は、補助的な熱エ
ネルギーの導入がなくても熱分解炉4内において搬入部
10に移動されている場所に既に存在している。A supply pipe 30 for supplying a gas BG containing oxygen, for example, air enriched with oxygen or pure oxygen is opened inside the pyrolysis furnace 4. The gas BG flowing into the pyrolysis furnace 4 at the free end 32 of the supply pipe 30
Causes additional heat to be introduced into the pyrolysis furnace 4 by oxidation of the process gases and pyrolysis residues. Process gas S
Due to the counterflow of the G, the temperature of the inlet is not supplementary with the introduction of thermal energy, without having to introduce thermal energy.
The reaction conditions required for the initiation of the oxidation (reaction partners: the presence of the process gas SG and the pyrolysis residue R as well as the reaction temperature required for the oxidation to occur, are increased as compared to the embodiment known from US Pat. ) Is already present in the pyrolysis furnace 4 at a location that has been moved to the carry-in section 10 without the introduction of auxiliary thermal energy.
【0021】この実施例において、供給配管30は熱分
解炉4に開口する前において部分的にプロセスガスSG
を案内する通路20の中を延びている。これによりその
中を導かれるガスBGは熱分解炉4の中に流出する前に
予め加熱される。追加的に供給配管30に熱交換器34
を接続することもでき、この熱交換器34には例えば設
備内で生ずる廃熱あるいは外部プロセスからの熱Wが導
入される。In this embodiment, the supply pipe 30 is partially filled with the process gas SG before opening to the pyrolysis furnace 4.
In a passage 20 for guiding the Thereby, the gas BG guided therein is heated in advance before flowing out into the pyrolysis furnace 4. In addition, a heat exchanger 34 is connected to the supply pipe 30.
The heat exchanger 34 receives, for example, waste heat generated in the facility or heat W from an external process.
【図1】本発明に基づく廃棄物の熱処理設備の縦断面
図。FIG. 1 is a longitudinal sectional view of a waste heat treatment facility according to the present invention.
【図2】図1におけるII−II線に沿った断面図。FIG. 2 is a sectional view taken along the line II-II in FIG.
2 スクリューコンベヤ 4 熱分解炉 6 熱分解炉の長手方向 8 加熱管 9 回転ブッシング 10 搬入部 12 廃棄物の搬送方向 14 搬出部 16 室 18 選別装置 20 通路 22 スクリューハウジング 24 排気室 25 加熱ジャケット 26 管系 27 管系 28 搬出側出口 29 プロセスガスの部分流の流れ方向 30 空気(酸素)供給配管 32 供給配管30の自由端 34 熱交換器 A 廃棄物 F 微細成分 G 粗大成分 HG 高温ガス R 熱分解残留物 SG 乾留ガス BG 空気又は酸素 2 Screw Conveyor 4 Pyrolysis Furnace 6 Longitudinal direction of Pyrolysis Furnace 8 Heating Tube 9 Rotary Bushing 10 Carry-In Port 12 Waste Transporting Direction 14 Carry-Out Portion 16 Room 18 Sorting Device 20 Passage 22 Screw Housing 24 Exhaust Chamber System 27 Pipe system 28 Outlet outlet 29 Flow direction of partial flow of process gas 30 Air (oxygen) supply pipe 32 Free end of supply pipe 30 34 Heat exchanger A Waste F Fine component G Coarse component HG Hot gas R Thermal decomposition Residue SG Carbonization gas BG Air or oxygen
───────────────────────────────────────────────────── フロントページの続き (72)発明者 カールハインツ ウンフエルツアークト ドイツ連邦共和国 63500 ゼリゲンシユ タツト タウヌスシユトラーセ 21 (72)発明者 ハルトムート ヘルム ドイツ連邦共和国 63303 ドライアイヒ グラーフエンブルツフシユトラーセ 18 (72)発明者 カール マイ ドイツ連邦共和国 61118 バート‐フイ ルベル クルト‐モースドルフ‐シユトラ ーセ 6 (72)発明者 ルードルフ アーレンス‐ボートツオング ドイツ連邦共和国 67071 ルートヴイツ ヒスハーフエン フイル‐シヤイデマン- シユトラーセ 47 ──────────────────────────────────────────────────の Continued on the front page (72) Inventor Karl Heinz Unfelzerkut Germany 63500 Zeligenscheut Tadt Taunusshuitlase 21 (72) Inventor Hartmut Helm Germany 63303 Dreieich Grafemblüftsjlase 18 (72) ) Inventor Karl-May Germany 61118 Bad-Fuilbel Kurt-Mosdorf-Schüitlasse 6 (72) Inventor Rudolf Aarens-Boatzong, Germany 67071 Ludweiss-Hishalfen Fil-Scheidemann-Schutlase 47
Claims (15)
手方向(6)に延びる熱分解炉(4)を有し、この熱分
解炉(4)がその一端に廃棄物(A)の搬入部(10)
を、その他端に乾留の際に生ずる熱分解残留物(R)の
搬出部(14)を有し、前記搬入部(10)に熱分解炉
(4)の中で生じたプロセスガス(SG)の出口(2
4)が配置されていることを特徴とする廃棄物の熱処理
設備。1. A pyrolysis furnace (4) extending in a longitudinal direction (6) for transporting and carbonizing waste (A), the pyrolysis furnace (4) being provided at one end with the waste (A). Loading section (10)
At the other end, a discharge portion (14) for pyrolysis residue (R) generated during dry distillation, and a process gas (SG) generated in the pyrolysis furnace (4) at the input portion (10). Exit (2
(4) A waste heat treatment facility, wherein:
(BG)の供給配管(30)を備えていることを特徴と
する請求項1記載の設備。2. The installation according to claim 1, further comprising a supply pipe (30) for the oxygen-containing gas (BG) which opens into the pyrolysis furnace (4).
熱するための熱交換器(34)を備えていることを特徴
とする請求項2記載の設備。3. The installation according to claim 2, further comprising a heat exchanger for heating the gas (BG) connected to the supply line.
ューハウジング(22)付きのスクリューコンベヤ
(2)を備え、そのスクリューハウジング(22)が少
なくともその長さの一部にわたってプロセスガス(S
G)で加熱されることを特徴とする請求項1ないし3の
いずれか1つに記載の設備。4. A screw conveyor (2) with a screw housing (22) upstream of a pyrolysis furnace (4), said screw housing (22) comprising at least a part of its length a process gas (2). S
4. The installation according to claim 1, wherein the installation is heated in G).
ともその長さの一部にわたってプロセスガス(SG)を
案内する通路(20)の中に配置されていることを特徴
とする請求項4記載の設備。5. The installation according to claim 4, wherein the screw housing is arranged in a passage for guiding the process gas over at least a part of its length.
ともその長さの一部を熱分解炉(4)の外側で発生され
た加熱ガス(HG)で加熱されることを特徴とする請求
項4又は5記載の設備。6. The screw housing (22) is heated at least part of its length by a heating gas (HG) generated outside the pyrolysis furnace (4). Equipment as described.
(20)とスクリューハウジング(22)との間に、加
熱ガス(HG)を案内しスクリューハウジング(22)
を少なくともその長さの一部にわたって包囲する加熱ジ
ャケット(25)が配置されていることを特徴とする請
求項6記載の設備。7. A screw housing (22) for guiding a heating gas (HG) between a passage (20) for guiding a process gas (SG) and a screw housing (22).
7. The installation according to claim 6, wherein a heating jacket (25) is arranged surrounding at least part of its length.
向(6)において搬入部(10)から搬出部(14)に
向って延びる熱分解炉(4)に入れられ、熱分解炉
(4)の長手方向(6)に搬送され、その際に乾留さ
れ、その乾留の際に生ずるプロセスガス(SG)の少な
くとも一部が熱分解炉(4)から搬出部(10)におい
て取り出されることを特徴とする廃棄物の熱処理方法。8. The waste (A) is introduced into a pyrolysis furnace (4) which extends from a loading section (10) to a discharge section (14) in a longitudinal direction (6) at a loading section (10) and is pyrolyzed. It is conveyed in the longitudinal direction (6) of the furnace (4) and is carbonized at that time, and at least a part of the process gas (SG) generated during the carbonization is taken out from the pyrolysis furnace (4) at the discharge section (10). Waste heat treatment method.
が供給されることを特徴とする請求項8記載の方法。9. An oxygen-containing gas (BG) is supplied to a pyrolysis furnace (4).
9. The method according to claim 8, wherein is provided.
給前に加熱されることを特徴とする請求項9記載の方
法。10. The method according to claim 9, wherein the gas (BG) is heated before being supplied to the pyrolysis furnace (4).
ことを特徴とする請求項9又は10記載の方法。11. The method according to claim 9, wherein air is used as the gas (BG).
た空気あるいは純粋な酸素が利用されることを特徴とす
る請求項9又は10記載の方法。12. The method as claimed in claim 9, wherein the gas (BG) is air enriched with oxygen or pure oxygen.
られる前に熱分解炉(4)で発生したプロセスガス(S
G)で加熱されることを特徴とする請求項8ないし12
のいずれか1つに記載の方法。13. The process gas (S) generated in the pyrolysis furnace (4) before the waste (A) is put into the pyrolysis furnace (4).
13. Heating in G).
The method according to any one of the preceding claims.
スクリューコンベヤ(2)のスクリューハウジング(2
2)が少なくともその長さの一部にわたって搬入部から
取り出されるプロセスガス(SG)で加熱されることを
特徴とする請求項13記載の方法。14. A screw housing (2) of a screw conveyor (2) which is connected upstream of a pyrolysis furnace (4).
14. The method according to claim 13, wherein 2) is heated with a process gas (SG) withdrawn from the inlet for at least part of its length.
ーハウジング(22)が少なくともその長さの一部にわ
たって熱分解炉(4)の外側の燃焼で発生された加熱ガ
ス(HG)で加熱されることを特徴とする請求項14記
載の方法。15. The screw housing (22) of the screw conveyor (2) is heated by heating gas (HG) generated by combustion outside the pyrolysis furnace (4) over at least a part of its length. The method according to claim 14, characterized in that:
Applications Claiming Priority (2)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
DE19706757A DE19706757A1 (en) | 1997-02-20 | 1997-02-20 | Thermic refuse processing plant |
DE19706757.3 | 1997-02-20 |
Publications (1)
Publication Number | Publication Date |
---|---|
JPH10238728A true JPH10238728A (en) | 1998-09-08 |
Family
ID=7820958
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP10050063A Withdrawn JPH10238728A (en) | 1997-02-20 | 1998-02-16 | Heat treatment facility for waste and method therefor |
Country Status (2)
Country | Link |
---|---|
JP (1) | JPH10238728A (en) |
DE (1) | DE19706757A1 (en) |
Cited By (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP2012098015A (en) * | 2010-11-05 | 2012-05-24 | Ihi Corp | Waste pyrolysis gasifying apparatus |
CN108954332A (en) * | 2018-05-28 | 2018-12-07 | 温州市骐邦环保科技有限公司 | A kind of environmental protection and energy saving garbage combustion device |
CN115405918A (en) * | 2022-08-11 | 2022-11-29 | 湖北鑫星节能炉具有限公司 | Biomass particle combustion furnace with bottom ventilation structure |
CN117139344A (en) * | 2023-09-12 | 2023-12-01 | 四川云华川科技有限公司 | Domestic waste serialization multilayer pyrolysis reation kettle |
Families Citing this family (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
LT6131B (en) * | 2013-07-11 | 2015-03-25 | Uab "Enasa" | Installation for sewage sludge recovery and recycling into ecological products |
CN104595903B (en) * | 2015-01-27 | 2017-09-01 | 陈艳 | A kind of biomass garbage pyrolysis incineration device |
Family Cites Families (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
DE2356294A1 (en) * | 1973-11-10 | 1975-05-15 | Air Preheater | Refuse incinerator with gasifier and burner - prevents oxidation of metallic refuse and uses afterburner heat for oxidation |
DE4327953A1 (en) * | 1993-08-19 | 1995-02-23 | Siemens Ag | Plant for thermal waste disposal and method for operating such a plant |
-
1997
- 1997-02-20 DE DE19706757A patent/DE19706757A1/en not_active Withdrawn
-
1998
- 1998-02-16 JP JP10050063A patent/JPH10238728A/en not_active Withdrawn
Cited By (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP2012098015A (en) * | 2010-11-05 | 2012-05-24 | Ihi Corp | Waste pyrolysis gasifying apparatus |
CN108954332A (en) * | 2018-05-28 | 2018-12-07 | 温州市骐邦环保科技有限公司 | A kind of environmental protection and energy saving garbage combustion device |
CN115405918A (en) * | 2022-08-11 | 2022-11-29 | 湖北鑫星节能炉具有限公司 | Biomass particle combustion furnace with bottom ventilation structure |
CN117139344A (en) * | 2023-09-12 | 2023-12-01 | 四川云华川科技有限公司 | Domestic waste serialization multilayer pyrolysis reation kettle |
CN117139344B (en) * | 2023-09-12 | 2024-04-09 | 四川云华川科技有限公司 | Domestic waste serialization multilayer pyrolysis reation kettle |
Also Published As
Publication number | Publication date |
---|---|
DE19706757A1 (en) | 1998-09-03 |
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