JP2008082660A - Incinerator and clinker preventing/eliminating method by the incinerator - Google Patents

Incinerator and clinker preventing/eliminating method by the incinerator Download PDF

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JP2008082660A
JP2008082660A JP2006265730A JP2006265730A JP2008082660A JP 2008082660 A JP2008082660 A JP 2008082660A JP 2006265730 A JP2006265730 A JP 2006265730A JP 2006265730 A JP2006265730 A JP 2006265730A JP 2008082660 A JP2008082660 A JP 2008082660A
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incinerator
clinker
water
side wall
waste
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JP4992082B2 (en
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Masatomi Yanagisawa
正富 柳澤
Tatsuya Nakamura
達也 中村
Atsushi Mito
篤史 三戸
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Dowa Holdings Co Ltd
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Abstract

<P>PROBLEM TO BE SOLVED: To provide an incinerator and a clinker preventing/eliminating method by the incinerator having an effect of continuously preventing clinker from sticking to the inside of the incinerator and eliminating clinker which has already stuck and grown while causing no damage of a refractory material, with a simple facility at low cost. <P>SOLUTION: A water flow pipe 7 producing curtain-like flowing water 8 in the incinerator 3 is piped in the incinerator 3 for incinerating industrial waste and general waste. Dust in contact with the curtain-like flowing water 8 is thereby solidified and hardly sticks to a wall surface 32 of the incinerator 3 to continuously prevent clinker. <P>COPYRIGHT: (C)2008,JPO&INPIT

Description

本発明は、産業廃棄物や一般廃棄物等の廃棄物を焼却する際に生じるダストが、焼却炉の炉壁や煙道に付着、堆積して形成されるクリンカー(炉内生成物、炉内付着物)を防止・除去する手段を有する焼却炉、及びその焼却炉によるクリンカーの防止・除去方法に関するものである。   The present invention relates to a clinker (product in the furnace, in-furnace) formed by dust generated when incinerating waste such as industrial waste and general waste adhering to and depositing on the furnace wall and flue of the incinerator. The present invention relates to an incinerator having a means for preventing and removing deposits) and a method for preventing and removing clinker by the incinerator.

産業廃棄物や一般廃棄物の焼却炉においては、焼却に伴い、種種雑多な廃棄物が、溶融・固化等の物理変化や、酸化或いは酸・アルカリ反応等の化学反応を複合的に起こし、生成物が発生する。この生成物は、焼却炉の側壁等に付着した後、更に複雑な物理変化や化学反応を繰り返して成長し、硬質なクリンカーとなる。   In incinerators for industrial waste and general waste, various types of waste are generated by incineration in combination with physical changes such as melting and solidification and chemical reactions such as oxidation or acid / alkali reactions. Things are generated. After this product adheres to the side wall of the incinerator, etc., it grows by repeating more complicated physical changes and chemical reactions, and becomes a hard clinker.

クリンカーが成長すると、焼却炉の内部や煙道の容積が減少し、廃棄物そのものや燃焼排ガスの燃焼時間が減少する。それにより、有害物質を除去するための燃焼が不十分となる。また、炉内や煙道が狭くなると、排気の効率が悪くなることがある。更に、巨大化したクリンカーが落下して炉内の壁面や各種設備等が損傷することがあり、修繕のために多大な時間やコストを費やす必要が生じる。   As the clinker grows, the interior of the incinerator and the volume of the flue are reduced, and the combustion time of the waste itself and the combustion exhaust gas is reduced. Thereby, the combustion for removing harmful substances becomes insufficient. Further, when the furnace and the flue are narrowed, exhaust efficiency may be deteriorated. Furthermore, the clinker that has become enormous may fall and damage the wall surface and various facilities in the furnace, and it will be necessary to spend a great deal of time and cost for repairs.

このように、炉壁や煙道に発生したクリンカーが燃焼効率や設備の寿命に影響を及ぼさないために、クリンカーを除去する必要がある。従来、1年に数回、定期的に焼却炉の運転を停止し、人力によってクリンカーを除去していた。ところが、焼却炉の運転を停止した後、人による炉内の作業が可能な温度になるまでには、冷却のために数時間から数日を必要とする。更に、クリンカーの除去後、再び焼却を行うための焼却炉の立ち上げにも同様の昇温時間が必要であり、多大な時間を要する。そのため、焼却炉の年間の稼働時間が短くなる。   Thus, it is necessary to remove the clinker so that the clinker generated in the furnace wall and the flue does not affect the combustion efficiency and the life of the equipment. Conventionally, the operation of the incinerator was stopped periodically several times a year, and the clinker was removed manually. However, after the operation of the incinerator is stopped, it takes several hours to several days for cooling until it reaches a temperature at which a person can work in the furnace. Furthermore, after the clinker is removed, a similar temperature raising time is required for starting up the incinerator for incineration again, which requires a lot of time. This shortens the annual operating time of the incinerator.

しかも、炉内に付着したクリンカーは極めて除去困難であり、除去作業は肉体的負担が大きい。また、専用機械や場合によっては大がかりな重機等が用いられるため、多大なコストを要する。   In addition, the clinker adhering to the furnace is extremely difficult to remove, and the removal work has a large physical burden. In addition, a dedicated machine or a heavy machine or the like that is large in some cases is used, which requires a great deal of cost.

そこで、特許文献1〜3に開示されている方法によりクリンカーの堆積を防ぐ方法が提案されている。   Therefore, a method for preventing clinker accumulation by the methods disclosed in Patent Documents 1 to 3 has been proposed.

特許文献1は、焼却炉の炉壁の内面に沿うように噴霧水を供給し、炉壁の内面近傍を流動する燃焼ガス中の灰分の温度を低下させて、溶融状態の灰分が炉壁に付着するのを防止するものである。特許文献2は、おき燃焼層及び灰層に、飽和水蒸気又は加熱水蒸気を挿入し、焼却炉底部の局部異常燃焼を防止して、クリンカーの発生を防止するものである。   In Patent Document 1, spray water is supplied along the inner surface of the furnace wall of the incinerator, the temperature of the ash in the combustion gas flowing near the inner surface of the furnace wall is lowered, and the molten ash is applied to the furnace wall. It prevents it from adhering. In Patent Document 2, saturated steam or heated steam is inserted into the vertical combustion layer and the ash layer to prevent local abnormal combustion at the bottom of the incinerator and prevent the generation of clinker.

特許文献3は、クリンカー生成部である炉の側壁に高融点粒子またはその分散液を噴射して、クリンカーの付着を防止するものである。   In Patent Document 3, high melting point particles or a dispersion liquid thereof are jetted onto a side wall of a furnace which is a clinker generating portion to prevent the clinker from adhering.

特開2004−205115号公報JP 2004-205115 A 特開2005−69542号公報JP-A-2005-69542 特開2006−29701号公報JP 2006-29701 A

ところが、上記特許文献1,2の発明は、いずれも霧状の水を噴霧するものであり、クリンカーの防止効果が十分ではないうえ、既に付着したクリンカーを除去する効果は期待できない。さらに、炉壁の内側を保護している耐火材は水濡れに弱く、亀裂・剥離等を生じやすい。また、上記特許文献3の発明は、高融点粒子や薬液タンクが必要であり、材料及び設備のためのコストが高くなる。   However, the inventions of Patent Documents 1 and 2 both spray mist-like water, and the effect of removing the already attached clinker cannot be expected in addition to the effect of preventing the clinker. Furthermore, the refractory material protecting the inside of the furnace wall is vulnerable to water wetting and is likely to crack and peel off. In addition, the invention of Patent Document 3 requires high melting point particles and a chemical solution tank, which increases the cost for materials and equipment.

本発明の目的は、簡単な設備で安価なコストにより、焼却炉の内部にクリンカーが付着するのを連続的に防止するとともに、既に付着して成長したクリンカーを除去する効果を有し、且つ耐火材へのダメージがない焼却炉と、その焼却炉によるクリンカーの防止・除去方法を提供することにある。   The object of the present invention is to continuously prevent the clinker from adhering to the inside of the incinerator at a low cost with simple equipment, and has the effect of removing the already attached and grown clinker, and has a fire resistance. An incinerator having no damage to the material, and a method for preventing and removing clinker by the incinerator.

上記問題を解決するため、本発明によれば、産業廃棄物や一般廃棄物を焼却する焼却炉において、焼却炉内にカーテン状の流水を発生させる流水管が配管されていることを特徴とする焼却炉が提供される。これにより、カーテン状の流水に接触した溶融状態のダスト等が固化し、焼却炉の壁面に付着しにくくなるため、連続的にクリンカーを防止することができる。   In order to solve the above problems, according to the present invention, in an incinerator for incinerating industrial waste and general waste, a water pipe for generating curtain-like running water is provided in the incinerator. An incinerator is provided. Thereby, since the molten dust etc. which contacted curtain-like flowing water solidify and it becomes difficult to adhere to the wall surface of an incinerator, a clinker can be prevented continuously.

前記流水管は、前記焼却炉の側壁に沿って配管されていることが好ましい。これにより、側壁全体にクリンカーが付着するのを防止することができる。   It is preferable that the flowing water pipe is piped along a side wall of the incinerator. Thereby, it can prevent that a clinker adheres to the whole side wall.

また、前記流水管は、前記側壁から所定の間隔を有して配管されていることが好ましい。これにより、焼却炉の側壁を保護する耐火材に流水が直接かかることがなく、耐火材がヒートショックで損傷するのを防ぐことができる。   Moreover, it is preferable that the said water flow pipe is piped with the predetermined space | interval from the said side wall. Thereby, running water is not directly applied to the refractory material protecting the side wall of the incinerator, and the refractory material can be prevented from being damaged by the heat shock.

また、前記流水管は、散水口が設けられていることが好ましく、これによりカーテン状の流水を発生させる。さらに、流水管の上方へ向けて開口する散水口が設けられていることが好ましく、これにより、流水管の上側にクリンカーが付着するのを防ぐことができる。   Moreover, it is preferable that the said water flow pipe is provided with the water spout, and this generates curtain-shaped water flow. Furthermore, it is preferable that a water spout opening that opens upward from the water pipe is provided, so that the clinker can be prevented from adhering to the upper side of the water pipe.

更に、焼却炉の底面が水封構造であることが好ましい。これにより、流水管からの流水を回収し、水封構造に用いることができる。   Furthermore, it is preferable that the bottom surface of the incinerator has a water seal structure. Thereby, the flowing water from a flowing water pipe can be collect | recovered and it can use for a water seal structure.

また、本発明は、産業廃棄物や一般廃棄物を焼却する際に発生するダストが焼却炉の側壁に付着、堆積して形成されるクリンカーの防止方法であって、前記焼却炉内にカーテン状の流水を発生させることにより、前記ダストが前記流水に接触して固化し、前記側壁に付着するのを防止する前記焼却炉によるクリンカーの防止方法を提供する。   The present invention also relates to a method for preventing clinker formed by dust generated when incinerating industrial waste and general waste adhering to and depositing on a side wall of an incinerator, and the curtain is formed in the incinerator. Thus, the present invention provides a method for preventing clinker by the incinerator, which prevents the dust from solidifying in contact with the flowing water and preventing the dust from adhering to the side wall.

更に、本発明は、産業廃棄物や一般廃棄物を焼却する際に発生するダストが焼却炉の側壁に付着、堆積して形成されるクリンカーの除去方法であって、前記焼却炉内にカーテン状の流水を発生させることにより、前記流水が堆積した前記クリンカーに接触し、ヒートショックで前記クリンカーが破壊されて剥がれ落ちる前記焼却炉によるクリンカーの除去方法を提供する。   Furthermore, the present invention is a method for removing a clinker formed by depositing and depositing dust generated when incinerating industrial waste and general waste on the side wall of an incinerator, wherein the incinerator has a curtain shape. A method of removing clinker by the incinerator that contacts the clinker on which the flowing water is accumulated by generating the flowing water and the clinker is destroyed by heat shock and peels off is provided.

また、本発明は、産業廃棄物や一般廃棄物を焼却する際に発生するダストが焼却炉の側壁に付着、堆積して形成されるクリンカーの除去方法であって、前記焼却炉内にカーテン状の流水を発生させることにより、前記流水が堆積した前記クリンカーに接触し、クリンカー成分の一部が前記流水に溶解して剥がれ落ちることを特徴とするクリンカーの除去方法を提供する。   The present invention also relates to a method for removing clinker formed by depositing and depositing dust generated when incinerating industrial waste and general waste on the side wall of an incinerator, wherein the incinerator has a curtain shape. The clinker removal method is characterized in that by generating the flowing water, the flowing water contacts the clinker on which the flowing water is deposited, and a part of the clinker component is dissolved in the flowing water and peeled off.

本発明によれば、カーテン状の流水を発生させることにより、廃棄物の焼却時に発生するダストが、低温の流水に接触して固化し、焼却炉の側壁等に付着しにくくなる。従って、連続的に、クリンカーの付着を防止する効果がある。また、高熱の焼却炉内では、流水の一部が蒸発して水蒸気が発生する。このとき、急激な体積の膨張によって、ダストが弾き返されて側壁に付着せずに落下する。更に、流水よりも広範囲なカーテン状の水蒸気が形成され、ダストが低温の水蒸気に接触して固化し、側壁に付着しにくくなる。このように、流水と水蒸気の両方を利用して、クリンカーの発生を阻止することができる。   According to the present invention, by generating curtain-shaped running water, dust generated during incineration of waste is solidified by contact with low-temperature running water and hardly adheres to the side walls of the incinerator. Therefore, there is an effect of continuously preventing clinker adhesion. Moreover, in a high-temperature incinerator, a part of running water evaporates and water vapor | steam is generated. At this time, the dust is repelled by the rapid expansion of the volume and falls without adhering to the side wall. Furthermore, a wider range of curtain-like water vapor is formed than flowing water, and the dust is solidified by contact with the low-temperature water vapor and hardly adheres to the side wall. Thus, the generation of clinker can be prevented by using both running water and water vapor.

また、側壁にクリンカーが付着し、それが成長した場合でも、流水がクリンカーに接触することにより、ヒートショックで破壊される。さらに、堆積したクリンカーに流水が接触し、クリンカー成分の一部が流水に溶解して剥がれ落ちる。従って、一定以上の大きさに成長したクリンカーを除去する効果が得られる。   Moreover, even when a clinker adheres to the side wall and grows, it is destroyed by a heat shock when the running water comes into contact with the clinker. Furthermore, the flowing water comes into contact with the deposited clinker, and a part of the clinker component is dissolved in the flowing water and peeled off. Therefore, an effect of removing clinker grown to a certain size or more can be obtained.

以下、本発明の実施の形態を、図を参照して説明する。   Hereinafter, embodiments of the present invention will be described with reference to the drawings.

図1は、本発明に係る焼却炉3を備えた廃棄物燃焼装置1の概要を示す。廃棄物燃焼装置1は、例えばロータリーキルン装置等による一次燃焼装置2、一次燃焼装置2から排出される廃棄物や一次燃焼装置2において発生した排ガスを燃焼させる焼却炉3、焼却炉3において燃焼させた排ガスを冷却する冷却装置4、冷却した排ガスから灰分を分離する煤塵除去装置5、灰分を除去した排ガスを大気中に排出する煙突6を備えている。焼却炉3の下部には、燃焼後の残渣物を搬送する水封式コンベア装置10が設けられている。   FIG. 1 shows an outline of a waste combustion apparatus 1 provided with an incinerator 3 according to the present invention. The waste combustion apparatus 1 is combusted in an incinerator 3 and an incinerator 3 for combusting, for example, a primary combustion apparatus 2 such as a rotary kiln apparatus, waste discharged from the primary combustion apparatus 2 and exhaust gas generated in the primary combustion apparatus 2 A cooling device 4 for cooling the exhaust gas, a soot removal device 5 for separating ash from the cooled exhaust gas, and a chimney 6 for discharging the exhaust gas from which the ash has been removed to the atmosphere are provided. A water-sealed conveyor device 10 that conveys the residue after combustion is provided at the lower portion of the incinerator 3.

焼却炉3は、例えば縦長の略直方体状もしくは円柱状に形成されている。焼却炉3は、長手方向を縦に向け、側壁32を略鉛直にした状態で備えられる。焼却炉3の内壁は、例えば煉瓦等の耐火材によって形成されており、焼却炉3内は、耐酸性・耐熱性を有する。この焼却炉3の内側が燃焼室31となっている。焼却炉3の一側壁には、一次燃焼装置2の端部に連通する開口33が形成されている。焼却炉3の下端部には、水封式コンベア装置10に接続された残渣物排出口34が設けられている。   The incinerator 3 is formed in, for example, a vertically long substantially rectangular parallelepiped shape or a cylindrical shape. The incinerator 3 is provided in a state where the longitudinal direction is directed vertically and the side wall 32 is substantially vertical. The inner wall of the incinerator 3 is formed of a refractory material such as brick, for example, and the inside of the incinerator 3 has acid resistance and heat resistance. Inside the incinerator 3 is a combustion chamber 31. An opening 33 communicating with the end of the primary combustion device 2 is formed on one side wall of the incinerator 3. At the lower end portion of the incinerator 3, a residue discharge port 34 connected to the water-sealed conveyor device 10 is provided.

被燃焼物である各種廃棄物は、適当な大きさに粉砕混合され、供給部11から一次燃焼装置2内へ供給される。一次燃焼装置2内において、廃棄物を加熱し、乾燥及び燃焼させる。乾燥及び一次燃焼後の廃棄物や一次燃焼時に発生した排ガスは、開口33から焼却炉3の燃焼室31へ送り込まれ、焼却炉3による二次燃焼が行われる。二次燃焼時の燃焼温度は、少なくとも800℃以上、望ましくは900℃以上であり、これにより、排ガスを完全燃焼させ、ダイオキシン類を確実に分解することができる。廃棄物が燃焼室31内で焼却された後に残った残渣物は、残渣物排出口34を介して水封式コンベア装置10内に排出される。   Various types of waste as combustible materials are pulverized and mixed to an appropriate size and supplied from the supply unit 11 into the primary combustion apparatus 2. In the primary combustion apparatus 2, the waste is heated, dried and burned. Waste after drying and primary combustion and exhaust gas generated during primary combustion are sent from the opening 33 to the combustion chamber 31 of the incinerator 3, and secondary combustion is performed by the incinerator 3. The combustion temperature at the time of secondary combustion is at least 800 ° C. or higher, desirably 900 ° C. or higher, so that exhaust gas can be completely burned and dioxins can be reliably decomposed. The residue remaining after the waste is incinerated in the combustion chamber 31 is discharged into the water-sealed conveyor device 10 through the residue discharge port 34.

焼却炉3の上端部には、排ガスを導出する導出口35が開口され、冷却装置4に接続される。導出口35から排出された排ガスは、冷却装置4に導入されて所定の冷却工程が行われる。その後、排ガスは煤塵除去装置5に送られ、残留していた灰分等が除去されて、煙突6から大気中に放出される。   At the upper end of the incinerator 3, a lead-out port 35 for leading exhaust gas is opened and connected to the cooling device 4. The exhaust gas discharged from the outlet 35 is introduced into the cooling device 4 and a predetermined cooling process is performed. Thereafter, the exhaust gas is sent to the dust removing device 5 where the remaining ash and the like are removed and discharged from the chimney 6 into the atmosphere.

焼却炉3には、燃焼室31に廃液を噴霧する噴霧ノズル38が複数個備えられている。これらの噴霧ノズル38の数や配置、向き、噴霧量、噴霧状態等を適宜設定することにより、噴霧ノズル38から燃焼室31に噴霧される廃液は、高温で蒸発し、蒸発残渣分は焼却される。尚、この噴霧ノズル38は、産業廃棄物を焼却する場合に設けられ、通常一般廃棄物用の焼却炉では設けられない。   The incinerator 3 is provided with a plurality of spray nozzles 38 that spray the waste liquid into the combustion chamber 31. By appropriately setting the number, arrangement, orientation, spray amount, spray state, etc. of these spray nozzles 38, the waste liquid sprayed from the spray nozzles 38 to the combustion chamber 31 evaporates at a high temperature, and the evaporation residue is incinerated. The The spray nozzle 38 is provided when incinerating industrial waste, and is not usually provided in an incinerator for general waste.

焼却炉3には、燃焼室31に空気を供給する空気供給口36が複数個備えられている。これらの空気供給口36の数や配置、向き等を適宜設定することにより、空気供給口36から燃焼室31に空気が供給される際に燃焼室31内の雰囲気が撹拌され、燃焼室31の容積を有効に利用して燃焼させることができる。また、焼却炉3には、燃焼室31に燃焼ガスを供給するバーナ37が設けられている。空気供給口36から供給される空気の流量や、バーナ37に供給される空気の流量は、いずれも可変である。   The incinerator 3 is provided with a plurality of air supply ports 36 for supplying air to the combustion chamber 31. By appropriately setting the number, arrangement, orientation, and the like of these air supply ports 36, the atmosphere in the combustion chamber 31 is agitated when air is supplied from the air supply port 36 to the combustion chamber 31. The volume can be used effectively for combustion. The incinerator 3 is provided with a burner 37 that supplies combustion gas to the combustion chamber 31. The flow rate of air supplied from the air supply port 36 and the flow rate of air supplied to the burner 37 are both variable.

燃焼室31内の、クリンカーが生成しやすい位置、もしくは生成が予測される位置の上部に、流水管7を配管し、流水8を発生させる。流水管7は、燃焼室31上部に、側壁32の内側に沿って、側壁32から適当な間隔を有して設置される。流水管7は、焼却炉3の側壁32に形成された貫通孔を通して焼却炉3の外部から燃焼室31内へ挿通され、固定具14により側壁32に固定される。流水管7は、焼却炉3の外部において、流水計13及びポンプ12を備え、これらにより散水量が制御される。   In the combustion chamber 31, a running water pipe 7 is piped at a position where a clinker is likely to be generated or a position where generation is predicted to generate flowing water 8. The flowing water pipe 7 is installed in the upper part of the combustion chamber 31 along the inner side of the side wall 32 with an appropriate interval from the side wall 32. The flowing water pipe 7 is inserted into the combustion chamber 31 from the outside of the incinerator 3 through a through hole formed in the side wall 32 of the incinerator 3, and is fixed to the side wall 32 by the fixture 14. The flowing water pipe 7 includes a flow meter 13 and a pump 12 outside the incinerator 3, and the amount of water spray is controlled by these.

尚、流水管7の配管位置は、図1の例に示す位置に限ることはなく、クリンカーが生成しやすい場所の必要な範囲に必要な本数だけ配管するのが好ましい。   In addition, the piping position of the flowing water pipe 7 is not restricted to the position shown in the example of FIG. 1, and it is preferable to connect as many pipes as necessary in a necessary range of a place where clinker is easily generated.

流水管7には、後述する散水口が複数個所設けられる。散水口から、例えば1時間当たり1.6立米の水が燃焼室31に散水される。高温の燃焼室31内でも未蒸発な状態の水が流れるように、十分な水量で、且つ大きな水滴となるように散水する。流れ落ちた水は、水封式コンベア装置10に回収される。   The water flow pipe 7 is provided with a plurality of water spouts to be described later. For example, 1.6 m2 of water per hour is sprinkled from the water spout into the combustion chamber 31. Water is sprayed with a sufficient amount of water and large water droplets so that unevaporated water flows even in the high temperature combustion chamber 31. The water that has flowed down is collected by the water-sealed conveyor device 10.

図2に示すように、焼却炉3の側壁32は、構造鉄皮32aと、鉄皮32aを保護するための耐火煉瓦等からなる耐火層32bとの二重構造により構成される。尚、耐火層を複数備えた構造のものも存在する。また、焼却炉3の形状や温度域等によっては、耐火層32bを設けない場合もある。流水管7は、この側壁32から間隔Dだけ離れた位置に設けられる。間隔Dは、散水された水が直接耐火層32bに飛散して耐火層32bがヒートショックで破損しないように設定され、通常100mm〜500mm程度である。燃焼室31内の流水管7には、図2に示すように、上方に向かって開口する散水口71が一定間隔、例えば100mmおきに複数開けられている。散水口71の径は、例えば5mm程度である。流水管7の素材は、ステンレス鋼、好ましくはSUS316L等の耐熱性に優れたものが用いられる。   As shown in FIG. 2, the side wall 32 of the incinerator 3 is constituted by a double structure of a structural iron skin 32a and a refractory layer 32b made of a refractory brick or the like for protecting the iron skin 32a. There are also structures having a plurality of refractory layers. Further, depending on the shape and temperature range of the incinerator 3, the refractory layer 32b may not be provided. The water flow pipe 7 is provided at a position separated from the side wall 32 by a distance D. The interval D is set so that the sprinkled water is directly scattered on the refractory layer 32b and the refractory layer 32b is not damaged by heat shock, and is usually about 100 mm to 500 mm. As shown in FIG. 2, a plurality of water spray ports 71 opening upward are provided in the water flow pipe 7 in the combustion chamber 31 at regular intervals, for example, every 100 mm. The diameter of the water spout 71 is, for example, about 5 mm. The material of the water flow pipe 7 is stainless steel, preferably SUS316L or the like having excellent heat resistance.

流水管7の散水口71は、下方や側方あるいは上方など、いずれの方向に開口させてもよいが、上方に向かって開口することが好ましい。図3(A)に示すように、流水管7aの下方に散水口71aを設け、下方に向かって散水すると、流水管7の上部に、焼却時に発生するダストが付着し、クリンカー9が堆積しやすい。図3(B)に示すように上方に向かって散水すると、流水管7の外周が流水8bで覆われて、クリンカーが付着しにくくなる。更に、流水管7の内側を流れる流水8aと外周の流水8bとで流水管7を冷却するため、燃焼室31内の高温雰囲気における流水管7の強度低下を防ぎ、耐久性を高める。   The water spray port 71 of the water flow pipe 7 may be opened in any direction such as downward, sideward, or upward, but it is preferable to open upward. As shown in FIG. 3 (A), when a water spout 71a is provided below the water pipe 7a and water is sprayed downward, dust generated during incineration adheres to the upper part of the water pipe 7, and the clinker 9 is deposited. Cheap. When water is sprinkled upward as shown in FIG. 3B, the outer periphery of the water pipe 7 is covered with the water 8b, and the clinker is less likely to adhere. Furthermore, since the flowing water pipe 7 is cooled by the flowing water 8a flowing inside the flowing water pipe 7 and the flowing water 8b on the outer periphery, the strength of the flowing water pipe 7 in the high temperature atmosphere in the combustion chamber 31 is prevented from being reduced, and the durability is improved.

このように、流水管7の上側に散水口71を設けることにより、散水時、燃焼室31内に、図4に示すような流水及び水蒸気が発生する。則ち、流水管7上部から流水管7の外周に沿って流水8bが発生し、燃焼室31の下方に向かって流水8cがカーテン状に形成される。また、1000℃程度に達する高温の燃焼室31内では、散水された水の一部は蒸発し、カーテン状の水蒸気8dが形成される。流水が蒸発する際、気化により体積が急激に膨張するため、図4に示すように、燃焼時に生じたダスト9aを弾き返す効果が得られる。また、ダスト9aが低温のカーテン状の流水8cまたは水蒸気8dに接触することにより、溶融状態のダスト9aが固化して側壁32にクリンカーとして付着しにくい状態となり、燃焼室31下方の残渣物排出口34(図1)へ向けて落下する。   As described above, by providing the water spout 71 on the upper side of the water flow pipe 7, water and water vapor as shown in FIG. 4 are generated in the combustion chamber 31 during water sprinkling. That is, running water 8 b is generated from the upper part of the running water pipe 7 along the outer periphery of the running water pipe 7, and the running water 8 c is formed in a curtain shape toward the lower side of the combustion chamber 31. In the high-temperature combustion chamber 31 reaching about 1000 ° C., a part of the sprinkled water evaporates to form curtain-shaped water vapor 8d. When flowing water evaporates, the volume rapidly expands due to vaporization, so that an effect of repelling dust 9a generated during combustion can be obtained as shown in FIG. Further, when the dust 9a comes into contact with the low-temperature curtain-like running water 8c or water vapor 8d, the molten dust 9a is solidified and hardly adheres to the side wall 32 as a clinker, and a residue discharge port below the combustion chamber 31 Drop toward 34 (FIG. 1).

また、図5に示すように、側壁32にクリンカー9bが堆積した場合には、側壁32近傍の流水8cにより、堆積したクリンカー9bがヒートショックで破壊されて一部が剥がれ落ちる。従って、クリンカー9bは一定以上に成長することなく除去されるので、焼却炉3の運転に影響を及ぼすことがない。   As shown in FIG. 5, when the clinker 9b is accumulated on the side wall 32, the accumulated clinker 9b is destroyed by heat shock and a part is peeled off by the flowing water 8c near the side wall 32. Therefore, since the clinker 9b is removed without growing beyond a certain level, the operation of the incinerator 3 is not affected.

このように、未蒸発の水流と、蒸発して生成した水蒸気とを併用することにより、簡単且つ安価に、連続的に焼却炉3内のクリンカーの付着や成長を抑えることができる。そのため、焼却炉3の運転を停止してクリンカーを除去するという労力及びコストのかかる作業を行う必要がなく、焼却炉3の操業上の安定性、及びコスト優位性が大幅に向上する。実際に、上記のように流水管7を配管して散水を実施したところ、1年に3〜4回必要であったクリンカーの除去作業を行う必要がなくなった。   In this way, by using the un-evaporated water stream and the water vapor generated by evaporation in combination, the adhesion and growth of the clinker in the incinerator 3 can be suppressed easily and inexpensively. Therefore, it is not necessary to perform the labor and cost of removing the clinker by stopping the operation of the incinerator 3, and the operational stability and cost advantage of the incinerator 3 are greatly improved. Actually, when the water pipe 7 was piped and sprinkled as described above, it was no longer necessary to remove the clinker, which was required 3 to 4 times a year.

また、一般的に1000℃を超えることもある焼却炉3内では、鉄などの物質は軟化し、強度を維持できないが、流水管7内に水が流れることで、流水管7自体の温度が下がり、強度及び耐久性を維持できる。   In general, an incinerator 3 that may exceed 1000 ° C. softens a substance such as iron and cannot maintain its strength. However, when water flows in the flowing water pipe 7, the temperature of the flowing water pipe 7 itself increases. Decrease, strength and durability can be maintained.

図6は、流水管14の異なる配管例を示す。焼却炉3の側壁32の前面に縦方向に流水管14を配管し、流水管14の側方に設けた散水口141から放物線状に散水して、燃焼室31内にカーテン状の流水を発生させる。このように、例えば焼却炉の構造上の制約等から、上方から散水する位置に流水管を配管することが困難な場合には、側方や下方から散水するように配管してもよい。   FIG. 6 shows different piping examples of the flowing water pipe 14. A running water pipe 14 is vertically installed on the front surface of the side wall 32 of the incinerator 3 and sprinkled in a parabolic shape from a water spout 141 provided on the side of the running water pipe 14 to generate curtain-like running water in the combustion chamber 31. Let As described above, for example, when it is difficult to connect the water pipe to the position where water is sprayed from above due to structural restrictions of the incinerator, the water pipe may be sprayed from the side or from below.

本発明は、産業廃棄物や一般廃棄物の焼却炉に適用できる。   The present invention can be applied to an incinerator for industrial waste and general waste.

本発明に係る焼却炉を備えた廃棄物燃焼装置を示す概要図。The schematic diagram which shows the waste combustion apparatus provided with the incinerator which concerns on this invention. 図1の焼却炉の流水管設置部を示す部分切断斜視図。The partial cutting perspective view which shows the flowing water pipe installation part of the incinerator of FIG. 流水管の散水口の位置による散水状態を示す説明図。Explanatory drawing which shows the watering state by the position of the watering opening of a water pipe. 本発明による散水時の状態を示す説明図。Explanatory drawing which shows the state at the time of watering by this invention. 本発明による散水時の異なる状態を示す説明図。Explanatory drawing which shows the different state at the time of watering by this invention. 流水管の異なる配管例を示す縦断面図。The longitudinal cross-sectional view which shows the piping example from which a flowing water pipe differs.

符号の説明Explanation of symbols

1 廃棄物燃焼装置
2 一次燃焼装置
3 焼却炉
4 冷却装置
5 煤塵除去装置
6 煙突
7 流水管
8,8c 流水
9a ダスト
9b クリンカー
10 水封式コンベア装置
11 供給部
12 ポンプ
13 流量計
31 燃焼室
32 側壁
71 散水口
DESCRIPTION OF SYMBOLS 1 Waste combustion apparatus 2 Primary combustion apparatus 3 Incinerator 4 Cooling apparatus 5 Dust removal apparatus 6 Chimney 7 Flowing water pipes 8 and 8c Flowing water 9a Dust 9b Clinker 10 Water-sealed conveyor apparatus 11 Supply part 12 Pump 13 Flow meter 31 Combustion chamber 32 Side wall 71 Water spout

Claims (9)

産業廃棄物や一般廃棄物を焼却する焼却炉において、前記焼却炉内にカーテン状の流水を発生させる流水管が配管されていることを特徴とする焼却炉。   An incinerator for incinerating industrial waste and general waste, wherein an inflow furnace for generating curtain-like running water is provided in the incinerator. 前記流水管は、前記焼却炉の側壁に沿って配管されていることを特徴とする請求項1に記載の焼却炉。   The incinerator according to claim 1, wherein the flowing water pipe is piped along a side wall of the incinerator. 前記流水管は、前記側壁から所定の間隔を有して配管されていることを特徴とする請求項1または2に記載の焼却炉。   3. The incinerator according to claim 1, wherein the water pipe is piped at a predetermined interval from the side wall. 前記流水管に散水口が設けられていることを特徴とする請求項1〜3のいずれかに記載の焼却炉。   The incinerator according to any one of claims 1 to 3, wherein a water spout is provided in the water pipe. 前記流水管は、前記流水管の上方へ向けて開口する散水口が設けられていることを特徴とする請求項1〜3のいずれかに記載の焼却炉。   The incinerator according to any one of claims 1 to 3, wherein the water pipe is provided with a water spout opening that opens upward of the water pipe. 前記焼却炉の底面が水封構造であることを特徴とする請求項1〜5のいずれかに記載の焼却炉。   The incinerator according to any one of claims 1 to 5, wherein a bottom surface of the incinerator has a water seal structure. 産業廃棄物や一般廃棄物を焼却する際に発生するダストが焼却炉の側壁に付着、堆積して形成されるクリンカーの防止方法であって、
前記焼却炉内にカーテン状の流水を発生させることにより、前記ダストが前記流水に接触して固化し、前記側壁に付着するのを防止することを特徴とする請求項1〜6のいずれかに記載の焼却炉によるクリンカーの防止方法。
A method for preventing a clinker formed by depositing and depositing dust generated when incinerating industrial waste and general waste on the side wall of an incinerator,
The curtain-like running water is generated in the incinerator to prevent the dust from contacting and solidifying and adhering to the side wall. The clinker prevention method by the incinerator described.
産業廃棄物や一般廃棄物を焼却する際に発生するダストが焼却炉の側壁に付着、堆積して形成されるクリンカーの除去方法であって、
前記焼却炉内にカーテン状の流水を発生させることにより、前記流水が堆積した前記クリンカーに接触し、ヒートショックで前記クリンカーが破壊されて剥がれ落ちることを特徴とする請求項1〜6のいずれかに記載の焼却炉によるクリンカーの除去方法。
A method for removing a clinker formed by depositing and depositing dust generated when incinerating industrial waste and general waste on the side wall of an incinerator,
7. The curtain-like running water is generated in the incinerator to come into contact with the clinker on which the running water is accumulated, and the clinker is destroyed and peeled off by heat shock. The removal method of the clinker by the incinerator described in 1.
産業廃棄物や一般廃棄物を焼却する際に発生するダストが焼却炉の側壁に付着、堆積して形成されるクリンカーの除去方法であって、
前記焼却炉内にカーテン状の流水を発生させることにより、前記流水が堆積した前記クリンカーに接触し、クリンカー成分の一部が前記流水に溶解して剥がれ落ちることを特徴とする請求項1〜6のいずれかに記載の焼却炉によるクリンカーの除去方法。
A method for removing a clinker formed by depositing and depositing dust generated when incinerating industrial waste and general waste on the side wall of an incinerator,
The curtain-like running water is generated in the incinerator to contact the clinker on which the running water is deposited, and a part of the clinker component is dissolved in the running water and peeled off. The removal method of the clinker by the incinerator in any one of.
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KR101601895B1 (en) 2014-08-29 2016-03-22 연세대학교 원주산학협력단 Apparatus and method for automatic evaluation of apnea-hypopnea, reflecting sleep states and severity
TWI738316B (en) * 2019-05-07 2021-09-01 日本三菱動力股份有限公司 Stove and boiler equipped with it
JP2023008366A (en) * 2021-07-06 2023-01-19 アクアテクノEsco事業株式会社 Incinerator cleaning method

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JPS53117265A (en) * 1977-03-22 1978-10-13 Chiaki Hayata Parallel standing wall zone
JPS558507A (en) * 1978-06-30 1980-01-22 Hitachi Zosen Corp Apparatus for prevention of adhesion of clinker at garbage incinerator
JPS5531212A (en) * 1978-08-25 1980-03-05 Mitsui Toatsu Chem Inc Apparatus for processing residue produced at incineration in incinerator
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Publication number Priority date Publication date Assignee Title
KR101601895B1 (en) 2014-08-29 2016-03-22 연세대학교 원주산학협력단 Apparatus and method for automatic evaluation of apnea-hypopnea, reflecting sleep states and severity
TWI738316B (en) * 2019-05-07 2021-09-01 日本三菱動力股份有限公司 Stove and boiler equipped with it
JP2023008366A (en) * 2021-07-06 2023-01-19 アクアテクノEsco事業株式会社 Incinerator cleaning method
JP7249685B2 (en) 2021-07-06 2023-03-31 アクアテクノEsco事業株式会社 Incinerator cleaning method

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