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JP4550512B2 - Waste pyrolysis treatment system - Google Patents
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JP4550512B2 - Waste pyrolysis treatment system - Google Patents

Waste pyrolysis treatment system Download PDF

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JP4550512B2
JP4550512B2 JP2004219662A JP2004219662A JP4550512B2 JP 4550512 B2 JP4550512 B2 JP 4550512B2 JP 2004219662 A JP2004219662 A JP 2004219662A JP 2004219662 A JP2004219662 A JP 2004219662A JP 4550512 B2 JP4550512 B2 JP 4550512B2
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gas
waste
pyrolysis
cooler
reaction tower
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JP2006035115A (en
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勝記 井手
毅 野間
隆 雨宮
潔 今井
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Toshiba Corp
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    • 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
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    • Y02E50/30Fuel from waste, e.g. synthetic alcohol or diesel

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Description

本発明は、廃棄物等の被処理物を熱分解により処理する廃棄物熱分解処理システムに関する。   The present invention relates to a waste pyrolysis processing system for processing a workpiece such as waste by pyrolysis.

従来から、様々な汚染物質を含む未分別でかつ未処理の廃棄物を処理して使用可能な物質に変質させる廃棄物処理システムとして、例えば特開2000−202419号公報(特許文献1)に記載のような廃棄物を熱分解により処理する熱分解システムが知られている。   Conventionally, as a waste treatment system that converts unsorted and untreated waste containing various pollutants into usable materials, for example, described in JP 2000-202419 A (Patent Document 1) There is known a pyrolysis system for treating a waste such as the above by pyrolysis.

このような廃棄物処理システムでは、廃棄物等の被処理物は前処理装置を介して廃棄物供給装置により熱分解炉内へ供給され、熱分解炉において約550℃程度の温度で熱分解により処理される。一般的な熱分解炉としては、例えば回転ドラムを外部から加熱する外熱式回転キルンが用いられている。   In such a waste treatment system, an object to be treated such as waste is supplied into a thermal decomposition furnace by a waste supply device via a pretreatment device, and is thermally decomposed at a temperature of about 550 ° C. in the thermal decomposition furnace. It is processed. As a general pyrolysis furnace, for example, an externally heated rotary kiln that heats a rotary drum from the outside is used.

熱分解炉で熱分解により発生した有機性の高分子ガスはガス改質器により約1100℃の温度で改質されて低分子の可燃性ガスとなり、次いで、ガス冷却器により約900℃から200℃程度まで急冷却され、さらにガス浄化装置で浄化される。ガス浄化装置が実行するガス洗浄工程ではバグフィルターによるカーボンダストの除去、水によるガス水洗が行われる。ガス浄化装置で浄化された可燃性ガスは誘引ブロワ、水封装置、供給ブロワを経てガス利用先に供給される。これら熱分解炉、ガス改質器、ガス冷却器、ガス浄化装置は若干負圧の状態に誘引ブロワにより制御されているために外部より空気が入り込みやすい状態になっているが、その外部より空気が過剰に入らないように要部にシール構成が施されている。   The organic polymer gas generated by pyrolysis in the pyrolysis furnace is reformed at a temperature of about 1100 ° C. by a gas reformer to become a low molecular combustible gas, and then from about 900 ° C. to 200 ° C. by a gas cooler. It is rapidly cooled to about 0 ° C. and further purified by a gas purification device. In the gas cleaning process performed by the gas purification device, removal of carbon dust by a bag filter and gas water cleaning by water are performed. The combustible gas purified by the gas purification device is supplied to the gas usage destination through the induction blower, the water seal device, and the supply blower. These pyrolysis furnaces, gas reformers, gas coolers, and gas purification devices are controlled by the induction blower to a slightly negative pressure state, so that air easily enters from the outside. The main part is provided with a sealing structure so that the excessive amount does not enter.

ところが、従来の廃棄物熱分解処理システムでは、廃棄物を約550℃で熱分解して生成された熱分解ガスと改質用酸化剤(空気)をガス改質器内で反応させるため、カーボンが主成分の粉塵(以下、煤と称する。)が多量に発生する。この煤を効率良く後段に搬送し、要所を閉塞させないことが処理施設の稼動率を向上させるために重要である。また、改質ガスには多少の化学物質が含まれ、部分的に細い箇所や温度的に固体化する箇所に付着して閉塞に至る場合があるので、これを予防する対策が必要である。なお、廃棄物処理技術として、特願2003−068182号、特願2003−203553号、特願2003−391159号の特許出願に係る発明が本願発明者らの発明として知られている。
特開2000−202419号公報
However, in the conventional waste pyrolysis treatment system, the pyrolysis gas generated by pyrolyzing the waste at about 550 ° C. and the reforming oxidant (air) are reacted in the gas reformer. A large amount of dust (hereinafter referred to as soot) is generated. It is important to improve the operating rate of the processing facility by efficiently transporting the soot to the subsequent stage and not blocking the important points. Further, the reformed gas contains a certain amount of chemical substance, and may adhere to a partially thin part or a part that solidifies in temperature, resulting in clogging. Therefore, measures to prevent this are necessary. In addition, as waste treatment technology, inventions related to patent applications of Japanese Patent Application Nos. 2003-068182, 2003-203553, and 2003-391159 are known as the inventions of the present inventors.
JP 2000-202419 A

本発明は、このような従来の問題点に鑑みてなされたものであり、機器の最適な配置と構造と煤払いと煤排出と付着物の除去を円滑に行うことにより、廃棄物処理を安定かつ長期に渡って可能にした廃棄物熱分解処理システムを提供することを目的とする。   The present invention has been made in view of the above-described conventional problems, and by smoothly performing the optimal arrangement and structure of the device, the wiping, the slag discharge, and the removal of deposits, the waste treatment can be performed stably and. An object of the present invention is to provide a waste pyrolysis treatment system that has been made possible over a long period of time.

請求項1の発明は、廃棄物等の被処理物を熱分解する熱分解炉と、前記熱分解炉における前記被処理物の熱分解により発生する有機性の高分子ガスを受け入れ、高温度のガス改質処理にて低分子の可燃性ガスに改質して排出するガス改質器と、前記ガス改質器から排出される可燃性ガスを受け入れて冷却し、排出するガス冷却器と、前記ガス冷却器から排出される可燃性ガスを受け入れ、浄化して不純物を除去し、浄化済みの可燃性ガスを排出するガス浄化装置とを備えた廃棄物熱分解処理システムにおいて、前記ガス改質器は前反応塔と後反応塔とで構成し、前記前反応塔と後反応塔との下部同士を接続することで凹形状とし、前記前反応塔の上部を前記熱分解炉に接続して前記有機性の高分子ガスを受け入れるようにすると共に当該前反応塔の上部付近に熱分解バーナを取り付け、前記後反応塔の上部の排出部を前記ガス冷却器に接続して当該ガス改質器内での高温度のガス改質処理にて改質された低分子の可燃性ガスを前記ガス冷却器に排出するようにし、前記ガス冷却器は、ガス冷却のための伝熱管が装填され、当該伝熱管の内部を上から下に前記可燃性ガスに通過させることによってガス冷却する前段部とクエンチャー装置で成る後段部とをそれらの下部同士を連通するように接続することによって凹形状にし、前記前段部の上部を前記ガス改質器の前記低分子の可燃性ガスの排出部に接続し、前記クエンチャー装置の上部を前記ガス浄化装置に接続したことを特徴とするものである。 The invention of claim 1 accepts a pyrolysis furnace for thermally decomposing an object to be treated such as waste and an organic polymer gas generated by the thermal decomposition of the object to be treated in the pyrolysis furnace, A gas reformer that reforms and discharges into a low-molecular combustible gas in a gas reforming process, a gas cooler that receives and cools the combustible gas discharged from the gas reformer, and discharges the combustible gas; In the waste pyrolysis system comprising a gas purification device that receives and purifies the combustible gas discharged from the gas cooler, removes impurities, and discharges the purified combustible gas, the gas reforming The vessel is composed of a pre-reaction tower and a post-reaction tower, and has a concave shape by connecting the lower parts of the pre-reaction tower and the post-reaction tower, and the upper part of the pre-reaction tower is connected to the pyrolysis furnace. The organic polymer gas is accepted and the front A pyrolysis burner was attached in the vicinity of the upper part of the tower, and the discharge part at the upper part of the post-reaction tower was connected to the gas cooler to be reformed by high-temperature gas reforming treatment in the gas reformer. A low-molecular combustible gas is discharged to the gas cooler, and the gas cooler is loaded with a heat transfer tube for gas cooling, and passes through the heat transfer tube from above to the combustible gas. By connecting the lower part of the front part and the rear part of the quencher device so as to communicate with each other, the upper part of the front part is the low molecule of the gas reformer. It connected to the discharge part of flammable gas, and the upper part of the said quencher apparatus was connected to the said gas purification apparatus.

請求項2の発明は、請求項1に記載の廃棄物熱分解処理システムにおいて、前記ガス冷却器の前段部と後段部との相連通する底部に、移送スクリュー、冷却スクリュー及び排出機構で構成したカーボン灰出し機構を設けたことを特徴とするものである。
According to a second aspect of the present invention, in the waste pyrolysis treatment system according to the first aspect, the bottom part of the gas cooler that communicates with the front part and the rear part comprises a transfer screw, a cooling screw, and a discharge mechanism. A carbon ash removal mechanism is provided.

請求項3の発明は、請求項1又は2に記載の廃棄物熱分解処理システムにおいて、前記クエンチャー装置の上部付近を縦型に設置したバグフィルターの中間部を接続し、このバグフィルター内の中間部より上方に設けられている縦型のろ布の外表面から内側に前記クエンチャー装置からのガスを流し、上部に向かって当該ガスが流れる構造にしたことを特徴とするものである。   The invention of claim 3 is the waste thermal decomposition treatment system according to claim 1 or 2, wherein an intermediate portion of a bug filter in which the vicinity of the upper part of the quencher device is vertically installed is connected, It is characterized in that the gas from the quencher device flows from the outer surface of the vertical filter cloth provided above the intermediate portion to the inside, and the gas flows upward.

請求項4の発明は、請求項1〜3のいずれかに記載の廃棄物熱分解処理システムにおいて、前記ガス冷却器の前段部に煙管ボイラを設置し、当該煙管ボイラの上部缶板に吸い込みコーンを設け、当該吸い込みコーンに蒸気を吹き付けるための煤払いノズルを前記吸い込みコーンに若干挿入した状態で配設したことを特徴とするものである。   According to a fourth aspect of the present invention, in the waste thermal decomposition treatment system according to any one of the first to third aspects, a smoke tube boiler is installed at a front stage of the gas cooler, and a suction cone is placed in an upper can plate of the smoke tube boiler. And a wiping nozzle for spraying steam on the suction cone is disposed in a state of being slightly inserted into the suction cone.

請求項5の発明は、請求項4に記載の廃棄物熱分解処理システムにおいて、前記ガス冷却器の煤払いノズルには常に微量の蒸気を流し、煤払い時は間欠的に蒸気を多めに流すことを特徴とするものである。   According to a fifth aspect of the present invention, in the waste pyrolysis processing system according to the fourth aspect, a small amount of steam is always allowed to flow through the nozzle of the gas cooler. It is a feature.

本発明によれば、機器の最適な配置と煤払いと煤排出と付着物の除去を円滑に行うことができ、廃棄物処理の効率的な処理運用が長期に渡って可能な廃棄物熱分解処理システムを提供することができる。   According to the present invention, it is possible to smoothly perform the optimal arrangement of the device, the wiping, the slag discharge, and the removal of the deposits, and the waste pyrolysis process that enables efficient treatment operation of the waste treatment over a long period of time. A system can be provided.

以下本発明の実施の形態を図に基づいて詳説する。   Hereinafter, embodiments of the present invention will be described in detail with reference to the drawings.

(第1の実施の形態)図1は、本発明の1つの実施の形態の廃棄物熱分解処理システムのブロック図である。図1において、廃棄物等の被処理物は破砕、鉄回収を行う前処理装置101を介して廃棄物供給装置102により熱分解炉103内へ供給される。廃棄物は熱分解炉103において約550℃程度の温度で熱分解により処理される。この熱分解炉103としては、例えば回転ドラムを外部から加熱する外熱式回転キルンが一般的に用いられ、熱分解炉103で熱分解により発生した有機性の高分子ガスはガス改質器104に移され、ここで約1100℃の温度で改質されて低分子の可燃性ガスとなる。この可燃性ガスは、ガス冷却器105に移され、ここで約900℃から200℃程度まで急冷却された後、ガス浄化装置106に供給される。ガス浄化装置106では、冷却されたガスを浄化し不純物の除去された可燃性のガスが得られる。このガス浄化装置106はバグフィルターとガス洗浄装置を備え、バグフィルターによってカーボンダストを除去し、ガス洗浄装置106によって水によるガス水洗が行われる。ガス浄化装置106で浄化された可燃性ガスは誘引ブロワ107、水封装置108、供給ブロワ109を経てガス利用先に供給される。   (First Embodiment) FIG. 1 is a block diagram of a waste pyrolysis treatment system according to one embodiment of the present invention. In FIG. 1, an object to be processed such as waste is supplied into a thermal decomposition furnace 103 by a waste supply device 102 via a pretreatment device 101 that performs crushing and iron recovery. The waste is processed by pyrolysis at a temperature of about 550 ° C. in the pyrolysis furnace 103. As the pyrolysis furnace 103, for example, an externally heated rotary kiln for heating a rotary drum from the outside is generally used, and an organic polymer gas generated by pyrolysis in the pyrolysis furnace 103 is used as a gas reformer 104. Here, it is reformed at a temperature of about 1100 ° C. to become a low-molecular combustible gas. The combustible gas is transferred to the gas cooler 105 where it is rapidly cooled from about 900 ° C. to about 200 ° C. and then supplied to the gas purification device 106. In the gas purification device 106, the cooled gas is purified to obtain a combustible gas from which impurities are removed. The gas purification device 106 includes a bag filter and a gas cleaning device, removes carbon dust with the bag filter, and gas cleaning with water is performed by the gas cleaning device 106. The combustible gas purified by the gas purification device 106 is supplied to the gas use destination through the induction blower 107, the water seal device 108, and the supply blower 109.

一方、熱分解炉103で発生する残さは残さ排出装置111を介して熱分解炉103外へ排出され、残さ冷却、粉砕、分別装置112で有価金属を回収し、カーボン残さは造粒装置113に送られ、造粒物として再資源化される。また、ガス浄化装置106でガス洗浄に用いられた洗浄水は水処理装置114に送られ、中和処理と吸収、吸着処理が行われて浄化水とされ、ガス浄化装置106に返送される。   On the other hand, the residue generated in the pyrolysis furnace 103 is discharged to the outside of the pyrolysis furnace 103 through the residue discharge device 111, valuable metal is recovered by the residue cooling, pulverization, and separation device 112, and the carbon residue is transferred to the granulator 113. It is sent and recycled as a granulated product. The cleaning water used for gas cleaning in the gas purification device 106 is sent to the water treatment device 114, neutralized, absorbed and adsorbed, subjected to purification water, and returned to the gas purification device 106.

尚、熱分解炉103、ガス改質器104、ガス冷却器105、ガス浄化装置106は若干負圧の状態に誘引ブロワ107により制御されており、外部より空気が過剰に入らないように要部にシール構成が施されている。この図1に示す熱分解処理システムで、当該熱分解処理システムで生成される二次物質の可燃性ガスである改質ガスが、当該熱分解炉103のエネルギー源として再利用される。また、主要構成機器の温度調整用として還流される。また、システムで生成された余剰ガスは例えば燃焼炉等で排気ガス規準に従って燃焼させ、大気放出される。   Note that the pyrolysis furnace 103, the gas reformer 104, the gas cooler 105, and the gas purification device 106 are controlled by the induction blower 107 in a slightly negative pressure state, so that the main part does not enter excessive air from the outside. Is provided with a sealing structure. In the pyrolysis processing system shown in FIG. 1, a reformed gas that is a combustible gas of a secondary material generated in the pyrolysis processing system is reused as an energy source of the pyrolysis furnace 103. In addition, it is recirculated for temperature adjustment of main components. Further, surplus gas generated by the system is burned according to the exhaust gas standard in a combustion furnace or the like, and released into the atmosphere.

図2は、本発明の第1の実施の形態の廃棄物熱分解処理システムの機器配置の平面図である。図2において、廃棄物等の被処理物は前処理装置1を介して廃棄物供給装置2により熱分解炉3内へ供給され、熱分解炉3において約550℃程度の温度で熱分解により処理される。ここで、熱分解炉3で熱分解により発生した有機性の高分子ガスは熱分解炉出口フード4、ガス連結管5を介してガス改質器6に送られ、約1100℃の温度で改質されて低分子の可燃性ガスとなり、次いで、ガス冷却器7により約900℃から200℃程度まで急冷却され、バグフィルター8で煤を除去し、ガス洗浄装置9で水によるガス水洗が行われる。ガス浄化装置9で浄化された可燃性ガスは誘引ブロワ10、図示しない水封、供給ブロワを経てガス利用先に供給される。   FIG. 2 is a plan view of the equipment arrangement of the waste pyrolysis processing system according to the first embodiment of this invention. In FIG. 2, an object to be treated such as waste is supplied into the pyrolysis furnace 3 by the waste supply apparatus 2 through the pretreatment apparatus 1, and is processed by pyrolysis at a temperature of about 550 ° C. in the pyrolysis furnace 3. Is done. Here, the organic polymer gas generated by pyrolysis in the pyrolysis furnace 3 is sent to the gas reformer 6 through the pyrolysis furnace outlet hood 4 and the gas connection pipe 5 and modified at a temperature of about 1100 ° C. The gas is cooled to about 900 ° C. to about 200 ° C. by the gas cooler 7, the soot is removed by the bag filter 8, and the gas is washed with water by the gas washing device 9. Is called. The combustible gas purified by the gas purification device 9 is supplied to the gas use destination through the induction blower 10, a water seal (not shown), and a supply blower.

図3、図4、図5は、本発明の実施の形態に係る廃棄物熱分解処理システムの機器配置の縦断面図である。ガス改質器6は凹形状を呈し、前反応塔13の上部より熱分解ガスと空気(酸化材)が入り、後反応塔14の上部からガスが出る。後反応塔14の上部から出た煤を含んだ改質ガスは、縦型に設置したガス冷却器(煙管ボイラ)7の上部より入り、伝熱管15の内部を下方に流れてガス冷却され、ガス冷却器底部16で折り返して、クエンチャー装置17内を上向きに流れ、クエンチャー出口温度を制御して、縦型のバグフィルター8の中間部に導かれる。このような構成にすることにより、ガス冷却器7の伝熱管15内部で煤を同伴したガスを容易に搬送することができる。   3, FIG. 4, and FIG. 5 are longitudinal sectional views of the equipment layout of the waste pyrolysis processing system according to the embodiment of the present invention. The gas reformer 6 has a concave shape, and pyrolysis gas and air (oxidant) enter from the upper part of the pre-reaction tower 13, and gas exits from the upper part of the post-reaction tower 14. The reformed gas containing soot coming out from the upper part of the post-reaction tower 14 enters from the upper part of the gas cooler (smoke tube boiler) 7 installed in the vertical form, and flows downward in the heat transfer pipe 15 to be gas cooled, It is folded at the bottom 16 of the gas cooler, flows upward in the quencher device 17, and is led to the middle part of the vertical bag filter 8 by controlling the quencher outlet temperature. By adopting such a configuration, the gas accompanied with soot can be easily transported inside the heat transfer tube 15 of the gas cooler 7.

図3に示すクエンチャー装置17内には生成ガスノズル18、水噴霧ノズル19が組み込まれ、バグフィルター8に送るガス温度をすばやく制御できるようになっている。   A product gas nozzle 18 and a water spray nozzle 19 are incorporated in the quencher device 17 shown in FIG. 3 so that the gas temperature sent to the bag filter 8 can be quickly controlled.

図4に示すバグフィルター8内の中間部より上方にはろ布20が取り付けられ、ろ布20を通過したガスはガス洗浄装置9に送られ、ろ布20で集塵した煤は下部に落下して外部に排出される。   A filter cloth 20 is attached above the middle part in the bag filter 8 shown in FIG. 4, the gas that has passed through the filter cloth 20 is sent to the gas cleaning device 9, and the soot collected by the filter cloth 20 falls to the lower part. Discharged outside.

図5に示すガス洗浄装置9は冷却器21とガス洗浄塔22で構成され、入り口配管23を含め凹形状をしている。冷却器21には水噴霧ノズル24、ガス洗浄塔22には充填材25、水噴霧ノズル26、入り口配管23には内部掻き取り機構のスクレーパ27が組み込まれている。スクレーパ27は上部に取り付けたモータ27aで回転させ、内部の付着物を掻き取りながらガスに同伴して冷却器21内部に落下するようになっている。このため、付着物による配管閉塞を防止できる。   A gas cleaning device 9 shown in FIG. 5 includes a cooler 21 and a gas cleaning tower 22 and has a concave shape including an inlet pipe 23. The cooler 21 includes a water spray nozzle 24, the gas cleaning tower 22 includes a filler 25, a water spray nozzle 26, and an inlet pipe 23 incorporates a scraper 27 of an internal scraping mechanism. The scraper 27 is rotated by a motor 27a attached to the upper portion, and is dropped into the cooler 21 along with the gas while scraping off internal deposits. For this reason, it is possible to prevent the piping from being blocked by the adhering matter.

ガス洗浄装置9を出たガスは、誘引ブロワ10に吸い込まれ、水封装置11で逆流できないように水封される。水封装置11で水封されたガスは、後段の供給ブロワ(図1における109)に送られる構成になっている。   The gas exiting the gas cleaning device 9 is sucked into the attracting blower 10 and sealed with water so that the water sealing device 11 cannot back flow. The gas sealed with the water sealing device 11 is configured to be sent to a subsequent supply blower (109 in FIG. 1).

図3に詳しく示されているように、ガス改質器6の底部には移送スクリュー28が設置されている。移送スクリュー28は、底部に溜まった煤29を冷却スクリュー30に移送する。冷却スクリュー30は煤を冷却し、排出機構31(例えば図6、図7に示すようなダブルダンパ構成)に煤を送る。排出機構31は空気を外部と遮断しながら煤を外部に排出するようになっている。   As shown in detail in FIG. 3, a transfer screw 28 is installed at the bottom of the gas reformer 6. The transfer screw 28 transfers the gutter 29 collected at the bottom to the cooling screw 30. The cooling screw 30 cools the soot and sends the soot to a discharge mechanism 31 (for example, a double damper configuration as shown in FIGS. 6 and 7). The discharge mechanism 31 discharges soot outside while blocking air from the outside.

この配出機構31におけるダブルダンパ構成を、図6、図7を用いて説明する。図6は、改質器6の床に溜まったカーボン及び溶融物の排出を行う排出機構80の断面図であり、図7は、排出機構80の動作を説明する断面図である。排出機構80は、側壁81に支柱82を介して設置された回転可動部83に、上、下開閉フタ84,85が取り付けられており、上下2層構造となっている。そして図7(1)に示すように上開閉フタ84上に煤86が溜まると、図7(2)に示すように上開閉フタ84を開いて下開閉フタ85上に煤86を落とす。次に図7(3)に示すように上開閉フタ84を閉じて大気の侵入を塞いでから、図7(4)に示すように下開閉フタ85が開いて煤86を外部に捨てる。煤86が外部に捨てられると、図7(5)に示すように下開閉フタ85を閉じる。このように2層構造とすることで、廃棄物熱分解処理システム内には可燃性の気体等があることから、大気(酸素)が急激に流れ込むのを防ぐことができる。   A double damper configuration in the distribution mechanism 31 will be described with reference to FIGS. FIG. 6 is a cross-sectional view of a discharge mechanism 80 that discharges carbon and melt accumulated in the floor of the reformer 6, and FIG. 7 is a cross-sectional view illustrating the operation of the discharge mechanism 80. In the discharge mechanism 80, upper and lower open / close lids 84 and 85 are attached to a rotationally movable portion 83 installed on a side wall 81 through a column 82, and has a two-layer structure. 7 (1), when the collar 86 accumulates on the upper opening / closing lid 84, the upper opening / closing lid 84 is opened and the collar 86 is dropped on the lower opening / closing lid 85 as shown in FIG. 7 (2). Next, as shown in FIG. 7 (3), the upper opening / closing lid 84 is closed to block the intrusion of the atmosphere, and then the lower opening / closing lid 85 is opened as shown in FIG. When the bag 86 is thrown away, the lower opening / closing lid 85 is closed as shown in FIG. By adopting a two-layer structure in this way, since there is a combustible gas or the like in the waste pyrolysis processing system, it is possible to prevent the atmosphere (oxygen) from flowing in rapidly.

図3に示すように、ガス冷却器7の底部16には移送スクリュー32が設置されている。移送スクリュー32は、底部16に溜まった煤33を冷却スクリュー34に移送する。冷却スクリュー34は煤33を冷却し、図6、図7に示したのと同様のダブルダンパ構成の排出機構35に煤33を送る。排出機構35は空気を外部と遮断しながら煤33を外部に排出する。移送スクリュー32は機外に設置したモータ32aで回転駆動される。この構造により、ガス冷却器7の底部16に溜まる煤33を容易に排出し、ガス閉塞なく運転継続ができる。   As shown in FIG. 3, a transfer screw 32 is installed at the bottom 16 of the gas cooler 7. The transfer screw 32 transfers the gutter 33 collected at the bottom 16 to the cooling screw 34. The cooling screw 34 cools the gutter 33 and sends the gutter 33 to a discharge mechanism 35 having a double damper configuration similar to that shown in FIGS. The discharge mechanism 35 discharges the gutter 33 to the outside while blocking air from the outside. The transfer screw 32 is rotationally driven by a motor 32a installed outside the apparatus. With this structure, the gutter 33 accumulated at the bottom 16 of the gas cooler 7 can be easily discharged, and the operation can be continued without gas blockage.

図4に示すように、バグフィルター8で集塵した煤36は下部に落下して冷却スクリュー37で冷却し、図6、図7に示したのと同様のダブルダンパ構成の排出機構38に煤36を送る。排出機構38は空気を外部と遮断しながら煤を外部に排出する。   As shown in FIG. 4, the soot 36 collected by the bag filter 8 falls to the lower part and is cooled by the cooling screw 37, and the soot 36 is discharged into the discharge mechanism 38 having the same double damper configuration as shown in FIGS. 6 and 7. Send 36. The discharge mechanism 38 discharges the soot outside while blocking air from the outside.

図3に示すように、ガス冷却器(煙管ボイラ)7の上部ガス入口部には煤払いノズル39、制御弁40が取り付けて、ボイラ自身で発生した蒸気を使って定期的に煤払いを行う構造にしてある。これによってガス冷却器7の入口部の煤閉塞を未然に防止している。   As shown in FIG. 3, a gas discharge nozzle 39 and a control valve 40 are attached to the upper gas inlet of the gas cooler (smoke tube boiler) 7 so that the gas can be periodically discharged using steam generated by the boiler itself. It is. This prevents the clogging of the inlet portion of the gas cooler 7 in advance.

図4に示すように、バグフィルター8のろ布20の上方出口部には、窒素を噴き出してろ布20についた煤36を払い落とす逆洗ノズル41とその制御弁42が設けられている。さらに、バグフィルター8には本体を仕切るための入口弁43および出口弁44が取り付けてあり、また図示しないバグバイパスラインが設けられてあって、プラント昇温や非常時には入口弁43、出口弁44を閉じてバグバイパスラインにガスをバイパスさせることで、バグフィルター8本体を系から隔離できるようになっている。   As shown in FIG. 4, a backwash nozzle 41 and its control valve 42 are provided at the upper outlet portion of the filter cloth 20 of the bag filter 8 to blow out nitrogen from the filter cloth 20 by blowing out nitrogen. Further, the bag filter 8 is provided with an inlet valve 43 and an outlet valve 44 for partitioning the main body, and is provided with a bag bypass line (not shown). The bag filter 8 main body can be isolated from the system by closing and closing the gas to the bag bypass line.

このようにして第1の実施の形態によれば、各構成機器を凹形状として前段上部からガス等を取り込み、底部に流下させて、煤等を集め、ガスは後段部を上昇させて次段の構成機器へ移流させる構造にすることにより、ガスから煤等を効率的に分離して処理できる。   As described above, according to the first embodiment, each component device is formed into a concave shape, gas and the like are taken in from the upper part of the front stage, flowed down to the bottom part, soot and the like are collected, and the gas is raised to the rear stage part. By making the structure advancing to the component equipment, it is possible to efficiently separate and process soot and the like from the gas.

(第2の実施の形態)本発明の第2の実施の形態の廃棄物熱分解処理システムはガス冷却器7の構造に特徴を有する。したがって他の機器の構成は、第1の実施の形態と共通する。図8は、本実施の形態で採用するガス冷却器7の構造を示している。この図8を用いてガス冷却器7の上部缶板の煤払い構造を詳細に説明する。約900℃の改質ガスがガス改質器6より流れ入る。   (Second Embodiment) The waste pyrolysis treatment system of the second embodiment of the present invention is characterized by the structure of the gas cooler 7. Therefore, the configuration of other devices is the same as that of the first embodiment. FIG. 8 shows the structure of the gas cooler 7 employed in the present embodiment. With reference to FIG. 8, the wiping structure of the upper can plate of the gas cooler 7 will be described in detail. About 900 ° C. reformed gas flows from the gas reformer 6.

ガス冷却器7は圧力容器、伝熱管46、上部缶板47、下部缶板48、天板49で構成され、上部煙室50内の上部缶板47の上部に蒸気整流器51が置かれている。蒸気整流器51には伝熱管46と同じ配列に対応して吸い込みコーン52が設けられている。吸い込みコーン52は下に絞った円錐台形状になっている。また、吸い込みコーン52毎に煤払いノズル53が天板49を貫通してシール54で外部との気密を確保して取り付けられている。煤払いノズル53は吸い込みコーン52に若干挿入して組み立てられている。吸い込みコーン52は耐熱金属や耐熱金属枠に耐火材を流し込んだ構成である。   The gas cooler 7 includes a pressure vessel, a heat transfer tube 46, an upper can plate 47, a lower can plate 48, and a top plate 49, and a steam rectifier 51 is placed above the upper can plate 47 in the upper smoke chamber 50. . The steam rectifier 51 is provided with a suction cone 52 corresponding to the same arrangement as the heat transfer tubes 46. The suction cone 52 has a truncated conical shape squeezed downward. Further, for each suction cone 52, a wiping nozzle 53 passes through the top plate 49 and is attached with a seal 54 while ensuring airtightness from the outside. The wiping nozzle 53 is assembled by being slightly inserted into the suction cone 52. The suction cone 52 has a structure in which a refractory material is poured into a refractory metal or a refractory metal frame.

煤払いには自身で発生した蒸気を用い、煤払いノズル53には常に微量の蒸気を流す弁55、煤払い時に間欠的に多めの蒸気を流す制御弁56が取り付けられている。弁55によって常時微量の蒸気を流しているため、断続的に多量に蒸気を流すのみの構成に比べて、この煤払いノズル53が詰まることがなく、熱衝撃も低くなることからノズルの破損も防止できる。   A steam generated by itself is used for the wiping, and a valve 55 for always flowing a small amount of steam is attached to the wiping nozzle 53, and a control valve 56 for flowing a large amount of steam intermittently during the wiping. Since a small amount of steam is constantly flown by the valve 55, the wiping nozzle 53 is not clogged and the thermal shock is reduced as compared with a configuration in which a large amount of steam is flowed intermittently, so that damage to the nozzle is prevented. it can.

加えて、吸い込みコーン52を取り付けることによって、煤払いノズル53から噴出した蒸気を確実に伝熱管46に入れ込める。また、煤払いノズル53を吸い込みコーン52に若干挿入した状態で組み立ててあるため、煤払いノズル53の熱膨張によって長さが伸びても伝熱管46もしくは上部缶板47に干渉することを未然に防ぐことができる。   In addition, by attaching the suction cone 52, the steam ejected from the wiping nozzle 53 can be reliably put into the heat transfer tube 46. In addition, since the wiping nozzle 53 is assembled with the suction cone 52 being slightly inserted, even if the length of the wiping nozzle 53 is increased due to thermal expansion, it is prevented from interfering with the heat transfer tube 46 or the upper can plate 47 in advance. Can do.

図9はガス冷却器7の底部16に設置した移送スクリュー32の説明図である。図9においてガス冷却器7の底部に溜まった煤33は移送スクリュー32で冷却スクリュー34側へ向かって送られる。移送スクリュー32はモータ32aで回転駆動される。駆動軸は隔壁57を貫通しシール58で外部と気密を確保してスクリュー32と結合している。移送スクリュー32は螺旋形状をしており、内部に掻き取り棒59が挿入されている。このような構成にすることにより、スクリュー32に付着するカーボンを掻き取り棒59が掻き取ってスクリュー32自体へのカーボンの付着を少なくし、長期的に煤33を移送できる。   FIG. 9 is an explanatory diagram of the transfer screw 32 installed at the bottom 16 of the gas cooler 7. In FIG. 9, the soot 33 accumulated at the bottom of the gas cooler 7 is sent by the transfer screw 32 toward the cooling screw 34. The transfer screw 32 is rotationally driven by a motor 32a. The drive shaft passes through the partition wall 57 and is connected to the screw 32 while ensuring airtightness with the seal 58. The transfer screw 32 has a spiral shape, and a scraping bar 59 is inserted therein. By adopting such a configuration, the carbon sticking to the screw 32 is scraped off by the scraping bar 59 so that the carbon sticking to the screw 32 itself is reduced, and the rod 33 can be transferred over a long period of time.

(第3の実施の形態)本発明の第3の実施の形態はまた、ガス冷却器7の構造に特徴を有している。図10は本発明の第3の実施の形態の廃棄物熱分解処理システムにおけるガス冷却器7の構造の説明図であり、図11は、そのスクレーパの正面図である。図10において、ガス冷却器7の煙管ボイラ伝熱管46内には付着物を掻き取るスクレーパ60が挿入してあり、またガス冷却器底部16には煤払いノズル61が設けてある。スクレーパ60は駆動モータ62で駆動され、シール63で外部と気密的に遮断して取り付けられている。下部煙室64の底部に溜まった煤65は煤払いノズル61で吹き飛ばされ、後段の冷却スクリュー34側に送られる。   (Third Embodiment) The third embodiment of the present invention is also characterized by the structure of the gas cooler 7. FIG. 10 is an explanatory view of the structure of the gas cooler 7 in the waste pyrolysis processing system of the third embodiment of the present invention, and FIG. 11 is a front view of the scraper. In FIG. 10, a scraper 60 for scraping off deposits is inserted into the smoke tube boiler heat transfer tube 46 of the gas cooler 7, and a wiping nozzle 61 is provided at the gas cooler bottom 16. The scraper 60 is driven by a drive motor 62, and is attached by being sealed off from the outside by a seal 63. The soot 65 collected at the bottom of the lower smoke chamber 64 is blown off by the soot removal nozzle 61 and sent to the cooling screw 34 side in the subsequent stage.

煤払いには自身で発生した蒸気を用い、煤払いノズル61には常に微量の蒸気を流す弁66、煤払い時に断続的に多めの蒸気を流す制御弁67が取り付けられている。この構成によって、常時微量の蒸気を流しているため、断続的に多量に蒸気を流すのみの場合に比べて、煤払いノズルが詰まることがなく、熱衝撃も低くなることからノズルの破損も防ぐことができる。   Steam generated by itself is used for steaming, and a valve 66 for flowing a small amount of steam at all times and a control valve 67 for flowing a large amount of steam intermittently when brushing are attached. With this configuration, a small amount of steam is constantly flowing, so that compared to the case where only a large amount of steam is flowed intermittently, the brushed nozzle will not be clogged and the thermal shock will be lower, thus preventing damage to the nozzle. Can do.

一般的な廃棄物熱分解処理システムのブロック図。The block diagram of a general waste pyrolysis processing system. 本発明の第1の実施の形態の廃棄物熱分解処理システムの機器配置を示すレイアウト図。The layout figure which shows the equipment arrangement | positioning of the waste pyrolysis processing system of the 1st Embodiment of this invention. 上記第1の実施の形態の廃棄物熱分解処理システムにおけるガス改質器及びガス冷却器の構造断面図。Sectional drawing of the structure of the gas reformer and gas cooler in the waste thermal decomposition treatment system of the said 1st Embodiment. 上記第1の実施の形態の廃棄物熱分解処理システムにおけるバグフィルターの構造断面図。Sectional drawing of the structure of the bag filter in the waste thermal decomposition treatment system of the said 1st Embodiment. 上記第1の実施の形態の廃棄物熱分解処理システムにおけるガス洗浄装置の構造断面図。Sectional drawing of the structure of the gas cleaning apparatus in the waste thermal decomposition treatment system of the said 1st Embodiment. 上記第1の実施の形態におけるダブルダンパ構成の煤排出機構の断面図。Sectional drawing of the soot discharge mechanism of the double damper structure in the said 1st Embodiment. 上記煤排出機構の動作の説明図。Explanatory drawing of operation | movement of the said soot discharging mechanism. 本発明の第2の実施の形態の廃棄物熱分解処理システムにおけるガス冷却器の前段部の構造断面図。Sectional drawing of the structure of the front | former part of the gas cooler in the waste pyrolysis processing system of the 2nd Embodiment of this invention. 上記第2の実施の形態の廃棄物熱分解処理システムにおけるガス冷却器の底部の移送スクリューの説明図。Explanatory drawing of the transfer screw of the bottom part of the gas cooler in the waste thermal decomposition treatment system of the said 2nd Embodiment. 本発明の第3の実施の形態の廃棄物熱分解処理システムにおけるガス冷却器の構造断面図。Sectional drawing of the structure of the gas cooler in the waste pyrolysis processing system of the 3rd Embodiment of this invention. 本発明の第3の実施の形態のスクレーパの証明図。The proof figure of the scraper of the 3rd Embodiment of this invention.

符号の説明Explanation of symbols

6 ガス改質器
7 ガス冷却器
8 バグフィルター
9 ガス洗浄装置
13 前反応塔
14 後反応塔
17 クエンチャー装置
20 ろ布
21 冷却器
22 ガス洗浄塔
23 入口配管
27 スクレーパ
32 移送スクリュー
34 冷却スクリュー
35 排出機構
37 冷却スクリュー
38 排出機構
47 上部缶板
52 吸い込みコーン
53 煤払いノズル
55,56 弁
59 掻き取り棒
60 スクレーパ
61 煤払いノズル
80 排出機構
81 側壁
82 支柱
83 回転可動部
84 上開閉フタ
85 下開閉フタ
6 Gas reformer 7 Gas cooler 8 Bag filter 9 Gas cleaning device 13 Pre-reaction tower 14 Post-reaction tower 17 Quencher device 20 Filter cloth 21 Cooler 22 Gas cleaning tower 23 Inlet piping 27 Scraper 32 Transfer screw 34 Cooling screw 35 Discharge mechanism 37 Cooling screw 38 Discharge mechanism 47 Upper can plate 52 Suction cone 53 Discharge nozzle 55, 56 Valve 59 Scraping rod 60 Scraper 61 Discharge nozzle 80 Discharge mechanism 81 Side wall 82 Support column 83 Rotating movable part 84 Upper opening / closing cover 85 Lower opening / closing cover

Claims (5)

廃棄物等の被処理物を熱分解する熱分解炉と、
前記熱分解炉における前記被処理物の熱分解により発生する有機性の高分子ガスを受け入れ、高温度のガス改質処理にて低分子の可燃性ガスに改質して排出するガス改質器と、
前記ガス改質器から排出される可燃性ガスを受け入れて冷却し、排出するガス冷却器と、
前記ガス冷却器から排出される可燃性ガスを受け入れ、浄化して不純物を除去し、浄化済みの可燃性ガスを排出するガス浄化装置とを備えた廃棄物熱分解処理システムにおいて、
前記ガス改質器は前反応塔と後反応塔とで構成し、前記前反応塔と後反応塔との下部同士を接続することで凹形状とし、前記前反応塔の上部を前記熱分解炉に接続して前記有機性の高分子ガスを受け入れるようにすると共に当該前反応塔の上部付近に熱分解バーナを取り付け、前記後反応塔の上部の排出部を前記ガス冷却器に接続して当該ガス改質器内での高温度のガス改質処理にて改質された低分子の可燃性ガスを前記ガス冷却器に排出するようにし、
前記ガス冷却器は、ガス冷却のための伝熱管が装填され、当該伝熱管の内部を上から下に前記可燃性ガスに通過させることによってガス冷却する前段部とクエンチャー装置で成る後段部とをそれらの下部同士を連通するように接続することによって凹形状にし、前記前段部の上部を前記ガス改質器の前記低分子の可燃性ガスの排出部に接続し、前記クエンチャー装置の上部を前記ガス浄化装置に接続したことを特徴とする廃棄物熱分解処理システム。
A pyrolysis furnace for thermally decomposing processed materials such as waste;
A gas reformer that accepts an organic polymer gas generated by thermal decomposition of the object to be processed in the pyrolysis furnace, reforms it into a low-molecular combustible gas by high-temperature gas reforming treatment, and discharges it. When,
A gas cooler that receives and cools the combustible gas discharged from the gas reformer, and discharges the combustible gas;
In a waste pyrolysis system comprising a gas purification device that receives and purifies the combustible gas discharged from the gas cooler, removes impurities, and discharges the purified combustible gas,
The gas reformer includes a pre-reaction tower and a post-reaction tower, and has a concave shape by connecting lower portions of the pre-reaction tower and the post-reaction tower, and the upper part of the pre-reaction tower is the pyrolysis furnace. The organic polymer gas is received and a pyrolysis burner is attached in the vicinity of the upper part of the pre-reaction tower, and the discharge part at the upper part of the post-reaction tower is connected to the gas cooler. The low-molecular combustible gas modified by the high-temperature gas reforming process in the gas reformer is discharged to the gas cooler,
The gas cooler is equipped with a heat transfer tube for gas cooling, and a front stage part for cooling the gas by passing the inside of the heat transfer pipe from the top to the bottom through the combustible gas, and a rear stage part composed of a quencher device, Are connected in such a manner that the lower portions thereof communicate with each other, and the upper portion of the front stage portion is connected to the low molecular combustible gas discharge portion of the gas reformer, and the upper portion of the quencher device. Is connected to the gas purification apparatus.
前記ガス冷却器の前段部と後段部とが相連通する底部に、移送スクリュー、冷却スクリュー及び排出機構で構成したカーボン灰出し機構を設けたことを特徴とする請求項1に記載の廃棄物熱分解処理システム。   2. The waste heat according to claim 1, wherein a carbon ash removal mechanism including a transfer screw, a cooling screw, and a discharge mechanism is provided at a bottom portion where the front and rear stages of the gas cooler communicate with each other. Disassembly processing system. 前記クエンチャー装置の上部付近を縦型に設置したバグフィルターの中間部接続し、このバグフィルター内の中間部より上方に設けられている縦型のろ布の外表面から内側に前記クエンチャー装置からのガスを流し、上部に向かって当該ガスが流れる構造にしたことを特徴とする請求項1又は2に記載の廃棄物熱分解処理システム。 The upper part of the quencher device is connected to the middle part of a bag filter installed vertically, and the quencher is placed inward from the outer surface of the vertical filter cloth provided above the middle part in the bag filter. The waste pyrolysis treatment system according to claim 1 or 2, wherein gas from the apparatus is flowed and the gas flows toward an upper part. 前記ガス冷却器の前段部に煙管ボイラを設置し、当該煙管ボイラの上部缶板に吸い込みコーンを設け、当該吸い込みコーンに蒸気を吹き付けるための煤払いノズルを前記吸い込みコーンに若干挿入した状態で配設したことを特徴とする請求項1〜3のいずれかに記載の廃棄物熱分解処理システム。   A smoke tube boiler is installed at the front stage of the gas cooler, a suction cone is provided on the upper can plate of the smoke tube boiler, and a wiping nozzle for spraying steam on the suction cone is slightly inserted into the suction cone. The waste thermal decomposition treatment system according to any one of claims 1 to 3, wherein 前記ガス冷却器の煤払いノズルには常に微量の蒸気を流し、煤払い時は間欠的に蒸気を多めに流すことを特徴とする請求項4に記載の廃棄物熱分解処理システム。   The waste pyrolysis processing system according to claim 4, wherein a small amount of steam is always supplied to the soaking nozzle of the gas cooler, and a large amount of steam is intermittently supplied when sowing.
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