JP4197289B2 - Ash processing equipment - Google Patents

Ash processing equipment Download PDF

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JP4197289B2
JP4197289B2 JP2003376477A JP2003376477A JP4197289B2 JP 4197289 B2 JP4197289 B2 JP 4197289B2 JP 2003376477 A JP2003376477 A JP 2003376477A JP 2003376477 A JP2003376477 A JP 2003376477A JP 4197289 B2 JP4197289 B2 JP 4197289B2
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ash
exhaust gas
secondary combustion
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unit
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JP2005140382A (en
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大輝 宮川
敬太 井上
鉄雄 佐藤
明弘 山田
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三菱重工環境エンジニアリング株式会社
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Description

本発明は、灰溶融炉排出ガスの処理装置に関する。   The present invention relates to a treatment apparatus for ash melting furnace exhaust gas.

従来から、下水汚泥、都市ゴミ及び産業廃棄物等の煤塵や焼却灰は、資源化、減量化及び無害化するためガス、油、電気エネルギー等により灰溶融炉内において溶融され、スラグやメタルとして取り出されている。スラグは冷却され固形化されると、大きく容積が減少し且つガラス化した状態となるので、重金属類は封入され安定化する。このため有害物質が雨水、地下水に溶出しないので、埋め立てによる二次公害の心配がない。また、コンクリートの骨材やブロック化して道路のタイルに再利用できる。   Conventionally, dust and incineration ash such as sewage sludge, municipal waste, and industrial waste are melted in an ash melting furnace by gas, oil, electric energy, etc. in order to recycle, reduce and detoxify them as slag and metal It has been taken out. When the slag is cooled and solidified, the volume is greatly reduced and the glass is vitrified, so that the heavy metals are enclosed and stabilized. For this reason, harmful substances do not elute into rainwater and groundwater, so there is no concern about secondary pollution caused by landfill. It can also be recycled into concrete aggregates and blocks for road tiles.

一方、灰溶融炉内で溶融処理中に発生した排ガスには、飛灰(主としてNaCl、KCl)、ダイオキシン、重金属等が含まれるため、排ガス処理装置で無害化する必要がある。図4を用い説明する。溶融炉3で発生したガスは排ガス処理装置に導かれ、二次燃焼室29で排ガス中の未燃分一酸化炭素ガス、水素ガスの燃焼及びダイオキシンの分解が行われる。二次燃焼室29を通過した排ガスは減温塔30に導かれ、ダイオキシンの再合成を防止するため水や空気を減温塔30に導入して、排ガス温度を摂氏200℃程度まで冷却する。冷却された排ガスは除塵装置15に送られ塵を取り除いた後、脱硝装置、脱硫装置に送られる。   On the other hand, since the exhaust gas generated during the melting process in the ash melting furnace contains fly ash (mainly NaCl, KCl), dioxin, heavy metals, etc., it must be rendered harmless by the exhaust gas processing apparatus. This will be described with reference to FIG. The gas generated in the melting furnace 3 is guided to an exhaust gas treatment device, and combustion of unburned carbon monoxide gas and hydrogen gas in the exhaust gas and decomposition of dioxin are performed in the secondary combustion chamber 29. The exhaust gas that has passed through the secondary combustion chamber 29 is guided to the temperature reducing tower 30, and water or air is introduced into the temperature reducing tower 30 to prevent dioxin resynthesis, and the exhaust gas temperature is cooled to about 200 ° C. The cooled exhaust gas is sent to a dust removing device 15 to remove dust, and then sent to a denitration device and a desulfurization device.

しかしながら、上述した従来の排ガス処理装置では、排ガス中に含まれる飛灰が排ガス処理装置内に付着して堆積し、内部の閉塞の原因となる。特に出滓口付近や第二ダクト31等の屈曲部には付着堆積しやすい。この堆積物を取り除くため清掃装置32が排ガス処理装置に設置される。清掃装置32には、ダクト外部から内部にエアを吹き込んで堆積物を除去する装置、電磁コイルまたはエアの力で質量のある物体をダクト表面に叩きつけることで内部の堆積物に衝撃を与えて除去するダクト外部の表面に設置された装置、偏心したおもりをつけたモータをまわして振動を与えることで内部の堆積物を除去するダクト表面に設置された装置などがある。これらの装置は内部に堆積した飛灰を剥離除去し、除去された堆積物は塔内を落下する。減温塔30の下部にはホッパ28と堆積物排出装置14が設置され堆積物を集め、排ガス処理装置外に排出する。いっぽう二次燃焼室29側では、堆積物が冷却水槽7に直接落ち冷却水を汚染する。冷却水槽の冷却水の汚染はスラグ、メタルの汚染の原因となる。冷却水槽の冷却水の汚染を防止している従来技術を図5に示す。除去された堆積物が冷却水槽7に直接落下しないよう、二次燃焼室29の下部にも、ホッパ28、堆積物排出装置14を配置している。   However, in the above-described conventional exhaust gas treatment device, fly ash contained in the exhaust gas adheres and accumulates in the exhaust gas treatment device, causing internal clogging. In particular, it tends to adhere and accumulate in the vicinity of the tap and the bent part such as the second duct 31. In order to remove this deposit, a cleaning device 32 is installed in the exhaust gas treatment device. The cleaning device 32 is a device that blows air from the outside of the duct to remove deposits, and strikes a mass object against the duct surface with an electromagnetic coil or air force to remove the deposits by impacting them. There is a device installed on the surface of the duct outside, and a device installed on the surface of the duct that removes internal deposits by turning a motor with an eccentric weight to give vibration. These devices exfoliate and remove the fly ash accumulated inside, and the removed deposit falls in the tower. A hopper 28 and a deposit discharge device 14 are installed at the lower part of the temperature reducing tower 30 to collect the deposit and discharge it outside the exhaust gas treatment device. On the other hand, on the secondary combustion chamber 29 side, deposits fall directly into the cooling water tank 7 and contaminate the cooling water. Contamination of the cooling water in the cooling water tank causes slag and metal contamination. FIG. 5 shows a conventional technique for preventing contamination of the cooling water in the cooling water tank. A hopper 28 and a deposit discharge device 14 are also arranged below the secondary combustion chamber 29 so that the removed deposit does not fall directly into the cooling water tank 7.

特許文献1に再燃焼の機能と冷却の機能とを一体に備えた再燃焼・冷却塔が開示される。該文献の図1に示されるように、再燃焼・冷却塔は上部に第二冷却ゾーンを有し、その下方に再燃焼・第一冷却ゾーンが配置される。このような排ガス処理装置は、再燃焼ゾーンの上方で水を噴霧するため再燃焼ゾーンに水が落ちたり、冷やされた排ガスが再び再燃焼ゾーンに落ち込んだり、再燃焼中の排ガス温度の低下の原因となる。すなわち、水噴霧ノズルに飛灰が付着すると正常な水の噴霧ができなくなり、水の粒が再燃焼ゾーンに落下する。また、再燃焼ゾーンで温められ上昇しようとする排ガスと、冷却ゾーンにより冷やされ下降しようとする排ガスが互いに衝突する向きに流れ、排ガスの滞留を招く。このような再燃焼ゾーンと冷却ゾーンの排ガスの干渉や冷却水の落ち込みは、ダイオキシンの再合成に適する温度領域が再燃焼・冷却塔内部に広がる問題が生じる。   Patent Document 1 discloses a recombustion / cooling tower that integrally has a reburning function and a cooling function. As shown in FIG. 1 of this document, the recombustion / cooling tower has a second cooling zone in the upper part, and a recombustion / first cooling zone is arranged below it. Such an exhaust gas treatment device sprays water above the recombustion zone, so that water falls into the recombustion zone, cooled exhaust gas falls into the recombustion zone again, or the exhaust gas temperature during recombustion decreases. Cause. That is, when fly ash adheres to the water spray nozzle, normal water spray cannot be performed, and water particles fall into the recombustion zone. In addition, the exhaust gas that is warmed up in the recombustion zone and that is going to rise and the exhaust gas that is cooled in the cooling zone and that is going down are flowing in the direction of colliding with each other, causing the exhaust gas to stay. Such interference between the exhaust gas in the recombustion zone and the cooling zone and a drop in the cooling water cause a problem that a temperature range suitable for resynthesis of dioxin spreads inside the recombustion / cooling tower.

特開平10−253041号公報Japanese Patent Laid-Open No. 10-253041

本発明はこのような実情に鑑みてなされたものであり、その目的は、排ガス処理装置内での飛灰の堆積をできるだけ防ぎ、堆積飛灰の除去の容易化、スラグ、メタル及びその冷却水の汚染防止、ダイオキシンの分解と再合成の抑制、排ガス処理装置の簡便化を実現した排ガス処理装置を有する灰処理設備を提供することにある。   The present invention has been made in view of such circumstances, and its purpose is to prevent the accumulation of fly ash in the exhaust gas treatment apparatus as much as possible, facilitate the removal of the accumulated fly ash, slag, metal and cooling water thereof. It is to provide an ash treatment facility having an exhaust gas treatment device that realizes prevention of contamination, suppression of dioxin decomposition and resynthesis, and simplification of the exhaust gas treatment device.

上記目的を達成するため、請求項1記載の発明は、灰溶融炉と、前記灰溶融炉からの排ガスを処理する二次燃焼部と減温部とからなる排ガス処理装置とを備えた灰処理設備において、前記減温部は前記二次燃焼部の下方に配置されるとともに、前記灰溶融炉に設けられた出滓口に出滓口部ダクトを介して連通して、冷却水によってスラグを砕き冷却する水砕水ノズルが設置された水砕ノズルカバーが設けられ、同水砕ノズルカバーの上部と前記第二次燃焼部の上部とを水平面を有さないダクトによって連通してなることを特徴とする。 In order to achieve the above object, an invention according to claim 1 is an ash treatment comprising an ash melting furnace, and an exhaust gas treatment device comprising a secondary combustion part for treating the exhaust gas from the ash melting furnace and a temperature reducing part. in equipment, the reduced temperature portion is arranged below the secondary combustion unit Rutotomoni, communicated via the tapping opening duct tapping port provided in the ash melting furnace, the slag by the cooling water water砕水granulated nozzle cover in which the nozzles are installed is provided for crushing cooling, Rukoto such communicating by the duct having no horizontal plane and the upper portion of the upper of Domizu砕nozzle cover secondary combustion unit It is characterized by.

請求項2記載の発明は、請求項1に記載の灰処理設備において、前記出滓口より下方に前記二次燃焼部を設けることを特徴とする。   According to a second aspect of the present invention, in the ash treatment facility according to the first aspect, the secondary combustion section is provided below the tap outlet.

請求項3記載の発明は、請求項1又は請求項2に記載の灰処理設備において、前記二次燃焼部と前記減温部を一体に備えたことを特徴とする。   According to a third aspect of the present invention, in the ash treatment facility according to the first or second aspect, the secondary combustion section and the temperature reducing section are integrally provided.

請求項4記載の発明は、請求項1又は請求項2に記載の灰処理設備において、前記排ガス処理装置には前記減温部の下方にのみ堆積物排出装置が配置されていることを特徴とする。   According to a fourth aspect of the present invention, in the ash treatment facility according to the first or second aspect, the exhaust gas treatment device is provided with a deposit discharge device only below the temperature reducing portion. To do.

請求項5記載の発明は、請求項3に記載の灰処理設備において、前記二次燃焼部と前記減温部とは略鉛直に建てられた円筒からなることを特徴とする。   According to a fifth aspect of the present invention, in the ash treatment facility according to the third aspect, the secondary combustion section and the temperature reducing section are formed of a cylinder built substantially vertically.

請求項6記載の発明は、請求項4に記載の灰処理設備において、前記堆積物排出装置は、解砕部と移送部とからなることを特徴とする。   A sixth aspect of the present invention is the ash treatment facility according to the fourth aspect, wherein the deposit discharging device includes a crushing unit and a transfer unit.

以上の発明の構成から、本発明にあっては次に列挙する効果が得られる。   From the configuration of the above invention, the following effects can be obtained in the present invention.

請求項1記載の発明により、二次燃焼部で生じる飛灰等の堆積物と排ガス中の飛灰、減温部で生じる飛灰等の堆積物と排ガス中の飛灰も一箇所に収集できることを実現した上で、二次燃焼部と減温部の排ガスの干渉を防止し、ダイオキシンの再合成や飛灰の付着防止する温度分布を実現することができる。
また、二次燃焼部が出滓口より下方にあるときのみならず上方にあっても、灰溶融炉と二次燃焼部とを連通するダクトを大きく上方に立ち上げることなく設置でき、灰溶融炉に排ガス取り出し口を設けずに排ガスを取り出すことができる。したがって、灰溶融炉の炉内耐火材に排ガス取り出し口の穴を設けずに済み、そのため耐火材の耐久性が増す。また、ダクトは水平面を有さないので同ダクトに飛灰が堆積して閉塞するのが防止される。
According to the first aspect of the invention, deposits such as fly ash generated in the secondary combustion section and fly ash in the exhaust gas, fly ash generated in the temperature reducing section, and fly ash in the exhaust gas can be collected in one place. In addition, it is possible to realize a temperature distribution that prevents interference between exhaust gases in the secondary combustion section and the temperature reduction section and prevents re-synthesis of dioxins and adhesion of fly ash.
In addition, the duct that connects the ash melting furnace and the secondary combustion section can be installed without raising the ash melting furnace upward, not only when the secondary combustion section is below the taphole, but also at the top. The exhaust gas can be extracted without providing the furnace with an exhaust gas extraction port. Therefore, it is not necessary to provide a hole for the exhaust gas outlet in the in-furnace refractory material of the ash melting furnace, which increases the durability of the refractory material. Further, since the duct does not have a horizontal plane, it is possible to prevent fly ash from accumulating and closing the duct.

請求項2記載の発明により、排ガスを灰溶融炉から二次燃焼部に向かって導く第一ダクトを上方に立ち上げる必要がなく、ダクトの屈曲も従来より小さく、屈曲部分への飛灰の付着、堆積を低減できる。   According to the second aspect of the present invention, it is not necessary to raise the first duct for guiding the exhaust gas from the ash melting furnace toward the secondary combustion section, the duct is bent less than before, and the fly ash adheres to the bent portion. , Can reduce deposition.

請求項3記載の発明により、二次燃焼部と減温部をつなぐダクトが不要となり、ダクト内に飛灰が付着堆積して閉塞する恐れがなくなる。また、ダクトに付着堆積した飛灰を取り除く清掃装置が不要となる。   According to the third aspect of the present invention, a duct connecting the secondary combustion section and the temperature reducing section is not required, and there is no possibility that fly ash adheres and accumulates in the duct and becomes blocked. Further, a cleaning device that removes fly ash adhering to and accumulating on the duct becomes unnecessary.

請求項4記載の発明により、二次燃焼部下方に堆積物搬出装置を設ける必要がなく、減温部に設けた堆積物搬出装置により、二次燃焼部と減温部で生じた堆積物等を排出することができる。   According to the fourth aspect of the present invention, it is not necessary to provide a deposit carry-out device below the secondary combustion section, and deposits generated in the secondary combustion section and the temperature reduction section by the deposit carry-out apparatus provided in the temperature reduction section. Can be discharged.

請求項5記載の発明により、二次燃焼部で生じた堆積飛灰の堆積物、排ガスの飛灰も減温部で生じた堆積飛灰も同一円筒内を落下し、一箇所で収集することができる。また、従来のように二次燃焼室と減温塔を別個に設置する必要がなくなり機器設置面積を節約することができる。   According to the fifth aspect of the present invention, the accumulated fly ash deposits generated in the secondary combustion section, the exhaust ash as well as the deposited fly ash generated in the temperature reducing section fall within the same cylinder and are collected in one place. Can do. Further, it is not necessary to separately install the secondary combustion chamber and the temperature reducing tower as in the prior art, and the equipment installation area can be saved.

請求項6記載の発明により、大きな塊の堆積物も解砕し、搬出することができる。   According to the invention described in claim 6, a large lump deposit can be crushed and carried out.

以下、図面に示す発明を実施するための最良の形態により、本発明を詳細に説明する。   Hereinafter, the present invention will be described in detail with reference to the best mode for carrying out the invention shown in the drawings.

本発明の実施例1を図1に示す。本実施例の灰処理設備は、少なくとも灰溶融炉3、排ガスを処理する二次燃焼部10・減温部11と除塵装置15等を備える。排ガス処理装置は、少なくとも二次燃焼部10と減温部11を備え、出滓口部ダクト22から、排ガスファン17に至るまでの一連の装置を含めることができる。   A first embodiment of the present invention is shown in FIG. The ash treatment facility of the present embodiment includes at least an ash melting furnace 3, a secondary combustion unit 10 and a temperature reduction unit 11 for treating exhaust gas, a dust removing device 15, and the like. The exhaust gas treatment device includes at least the secondary combustion unit 10 and the temperature reduction unit 11, and can include a series of devices from the tap port duct 22 to the exhaust gas fan 17.

投入灰貯槽1は、灰定量供給装置2を介して灰溶融炉3に接続される。灰溶融炉3は、第一ダクト23により二次燃焼部10に接続される。この第一ダクトには出滓口近傍に出滓口バーナ4、二次燃焼部入口付近に二次燃焼バーナ5が設けられる。また二次燃焼部入口温度計測装置24も設置される。二次燃焼部10の下方に減温部11が設置される。減温部11には、減温部上方で冷却水ノズル12、減温部下方に冷却空気ノズル13が設置される。減温部11の下部にはホッパ28が備えられる。ホッパ28下部には堆積物排出装置14が設置される。減温部下方と除塵装置15は第三ダクト33により接続される。除塵装置15下部には灰排出装置16が設置される。除塵装置15後方から第四ダクト34が接続され排ガスファン17と連通する。図中、一点破線はスラグの排出経路を、破線は排ガスの流れの経路を示す。 The input ash storage tank 1 is connected to an ash melting furnace 3 via an ash quantitative supply device 2. The ash melting furnace 3 is connected to the secondary combustion unit 10 by the first duct 23. The first duct is provided with a tap outlet burner 4 in the vicinity of the tap outlet and a secondary combustion burner 5 in the vicinity of the secondary combustion section inlet. A secondary combustion section inlet temperature measuring device 24 is also installed. A temperature reducing unit 11 is installed below the secondary combustion unit 10. The cooling unit 11 is provided with a cooling water nozzle 12 above the temperature reducing unit and a cooling air nozzle 13 below the temperature reducing unit. A hopper 28 is provided below the temperature reducing unit 11. The sediment discharge device 14 is installed at the lower part of the hopper 28. The lower part of the temperature reducing unit and the dust removing device 15 are connected by a third duct 33. An ash discharging device 16 is installed at the lower part of the dust removing device 15. A fourth duct 34 is connected from behind the dust removing device 15 and communicates with the exhaust gas fan 17. In the figure, the dashed line indicates the slag discharge path, and the broken line indicates the flow path of the exhaust gas.

第一ダクト23から下方に分岐する水砕ノズルカバー35には水砕水ノズル6が設置され、さらにその下方には、冷却水槽7が置かれる。スラグ排出コンベヤ8は冷却水槽7からスラグやメタルを搬出できるよう一部が冷却水に浸る形で設置される。一方の端は、スラグピットもしくはメタルピット9まで導かれている。   The granulated water nozzle 6 is installed in the granulated nozzle cover 35 branched downward from the first duct 23, and the cooling water tank 7 is placed further below. The slag discharge conveyor 8 is installed so that a part of the slag discharge conveyor 8 is immersed in the cooling water so that slag and metal can be carried out from the cooling water tank 7. One end is led to a slag pit or a metal pit 9.

ここで、第一ダクト23とは、灰溶融炉3と二次燃焼部10を連通するダクト、第二ダクト31は二次燃焼室29と減温塔30を連通するダクト、第三ダクト33は減温部11と除塵装置15を連通するダクト、第四ダクト34は除塵装置15と排ガスファン17を連通するダクト、のことをいう。   Here, the first duct 23 is a duct that communicates the ash melting furnace 3 and the secondary combustion unit 10, the second duct 31 is a duct that communicates the secondary combustion chamber 29 and the temperature reducing tower 30, and the third duct 33 is A duct that communicates the temperature reducing section 11 and the dust removing device 15, and a fourth duct 34 refers to a duct that communicates the dust removing device 15 and the exhaust gas fan 17.

投入灰貯槽1は、焼却炉から発生する焼却灰、飛灰を蓄える。灰定量供給装置2は、スクリューコンベヤを駆動させることにより灰溶融炉3に一定量の灰を供給する役割を持つ。灰溶融炉3に投入された灰は溶融処理される。溶融処理は灰溶融炉3の形式によって異なる。プラズマ灰溶融炉では、プラズマトーチにプラズマ生成用ガス(窒素ガス、アルゴンガスなどの不活性ガス等)を供給し、電圧を印加して、2000〜10000℃以上の高温、高速のプラズマ状態を作り、灰を溶融する。灰溶融炉内部は耐火材に覆われ、高温に耐えることができる。なお、本発明の実施の形態は、プラズマ式灰溶融炉に限られるものではなく、アーク式灰溶融炉、抵抗式灰溶融炉などにも適用することができる。   The input ash storage tank 1 stores incineration ash and fly ash generated from the incinerator. The ash quantitative supply device 2 has a role of supplying a certain amount of ash to the ash melting furnace 3 by driving a screw conveyor. The ash charged into the ash melting furnace 3 is melted. The melting process varies depending on the type of the ash melting furnace 3. In the plasma ash melting furnace, a plasma generating gas (inert gas such as nitrogen gas or argon gas) is supplied to the plasma torch, and a voltage is applied to create a high-temperature, high-speed plasma state of 2000 to 10000 ° C or higher. Melt the ash. The inside of the ash melting furnace is covered with a refractory material and can withstand high temperatures. The embodiment of the present invention is not limited to the plasma ash melting furnace, but can be applied to an arc ash melting furnace, a resistance ash melting furnace, and the like.

灰溶融炉3の中で、灰は溶融され、上層にスラグ、下層にメタルとしてわかれている。
スラグは1400℃以上の温度で、出滓口20から連続出滓される。ここで図1の出滓口20、出滓樋21付近の拡大図を図2に示す。出滓口20はスラグやメタルを出滓する灰溶融炉3の側壁下部に設けられた開口部である。出滓口20からは出滓樋21が下方に延び、灰溶融炉内のスラグやメタルは出滓口20、出滓樋21を通り冷却水槽7に落ちる。本実施例における灰溶融炉3は、傾動により炉内底部に溜まったメタルを出滓口20から出滓する。傾動は、傾動装置18が灰溶融炉3を傾動軸19を回転中心にして灰溶融炉3を傾けることをいう。
In the ash melting furnace 3, ash is melted and separated as slag in the upper layer and metal in the lower layer.
The slag is continuously discharged from the outlet 20 at a temperature of 1400 ° C. or higher. Here, FIG. 2 shows an enlarged view of the vicinity of the tapper 20 and the tapper 21 of FIG. The tap outlet 20 is an opening provided in the lower portion of the side wall of the ash melting furnace 3 for discharging slag and metal. From the taphole 20, the taphole 21 extends downward, and slag and metal in the ash melting furnace pass through the taphole 20 and the taphole 21 and fall into the cooling water tank 7. In the present embodiment, the ash melting furnace 3 feeds the metal accumulated at the bottom of the furnace by tilting from the spout 20. The tilting means that the tilting device 18 tilts the ash melting furnace 3 with the tilting shaft 19 as the center of rotation.

出滓樋21には出滓樋を覆う出滓口部ダクト22が設置される。出滓口部ダクト22は、第一ダクト23に隙間なく挿入されており、円弧を描く形状をしている。この出滓口部ダクト22の形状により傾動時も出滓口部ダクト22と第一ダクト23の間に隙間を生じず、傾動することができ、排ガスをもらさず排ガス処理装置に導くことができる。出滓口20から排ガスを取り出すことで、灰溶融炉に別途排ガス取り出し口を設けずに済む。したがって灰溶融炉の耐火材に穴を開けずに済み、耐火材の維持に都合が良い。なお、本発明の実施の形態は、排ガスを出滓口から取り出すことに限定されるものではなく、炉蓋等に別途排ガス取り出し口を設けて排ガスを処理する灰処理設備にも適用できる。   An output port 21 is provided on the output 21 so as to cover the output. The tap outlet duct 22 is inserted into the first duct 23 without a gap, and has a shape of drawing an arc. Due to the shape of the tap outlet duct 22, even when tilted, no gap is formed between the tap outlet duct 22 and the first duct 23, and the tilt can be tilted, leading to the exhaust gas treatment device without getting exhaust gas. . By removing the exhaust gas from the tap outlet 20, it is not necessary to provide a separate exhaust gas outlet in the ash melting furnace. Therefore, it is not necessary to make a hole in the refractory material of the ash melting furnace, which is convenient for maintaining the refractory material. The embodiment of the present invention is not limited to taking out the exhaust gas from the outlet, but can also be applied to an ash treatment facility in which an exhaust gas outlet is provided in a furnace lid or the like to treat the exhaust gas.

本実施例では、出滓口20より下方に排ガス処理装置の二次燃焼部10を設け、灰溶融炉3において発生した排ガスは出滓樋21の延長した先にある排ガス処理装置に導かれる。排ガスには、一酸化炭素ガス、ナトリウム・カリウム等の塩化物、亜鉛・カドミウム・鉛・砒素等の重金属類が含まれる。排ガス処理装置には、二次燃焼部10と二次燃焼部の下方に配置される減温部11が設けられている。排ガスは出滓口20から出た後、排ガス処理装置の上部の二次燃焼部10に導かれ、二次燃焼部下方の減温部11に向かって下向きに流れる。第一ダクト23内、出滓口付近には出滓口バーナ4が、二次燃焼部入口付近には二次燃焼バーナ5が設置され、排ガスの温度が一定温度(800℃)を下回らないよう必要に応じて点火される。   In the present embodiment, the secondary combustion unit 10 of the exhaust gas treatment device is provided below the tap outlet 20, and the exhaust gas generated in the ash melting furnace 3 is guided to the exhaust gas treatment device at the tip of the tap 21. The exhaust gas contains carbon monoxide gas, chlorides such as sodium and potassium, and heavy metals such as zinc, cadmium, lead and arsenic. The exhaust gas treatment apparatus is provided with a secondary combustion unit 10 and a temperature reduction unit 11 disposed below the secondary combustion unit. After the exhaust gas exits from the outlet 20, the exhaust gas is guided to the secondary combustion unit 10 at the upper part of the exhaust gas treatment device, and flows downward toward the temperature reducing unit 11 below the secondary combustion unit. An outlet outlet burner 4 is installed in the first duct 23 and in the vicinity of the outlet, and a secondary combustion burner 5 is installed in the vicinity of the inlet of the secondary combustion section so that the temperature of the exhaust gas does not fall below a certain temperature (800 ° C.). It is ignited as necessary.

出滓口バーナ4、二次燃焼バーナ5からは、燃料(石油、都市ガス、LPGガス等)と空気の混合ガスが噴出する。二次燃焼部10を一定温度以上を保つことで、ダイオキシン類及びその前駆物質を抑制でき、また、飛灰の付着を防止することができる。したがって排ガス温度がダイオキシン類の抑制等に必要な温度が保たれる限り二次燃焼バーナ5は必須の構成要素とは限らない。   From the tap outlet burner 4 and the secondary combustion burner 5, a mixed gas of fuel (oil, city gas, LPG gas, etc.) and air is ejected. By maintaining the secondary combustion unit 10 at a certain temperature or higher, dioxins and precursors thereof can be suppressed, and adhesion of fly ash can be prevented. Therefore, the secondary combustion burner 5 is not necessarily an essential component as long as the exhaust gas temperature is maintained at a temperature necessary for suppressing dioxins.

二次燃焼部10ではダイオキシン類及びその前駆物質を抑制するため、(i)800℃以上での燃焼、(ii)2秒以上の滞留時間、(iii)燃焼ガスとの混合を保つことが要される。一方、飛灰の融点は300℃から800℃にある。飛灰の付着防止には、この融点温度を避けることが求められる。   In order to suppress dioxins and their precursors in the secondary combustion section 10, it is necessary to maintain (i) combustion at 800 ° C. or higher, (ii) residence time of 2 seconds or more, and (iii) mixing with combustion gas. Is done. On the other hand, the melting point of fly ash is 300 ° C to 800 ° C. In order to prevent adhesion of fly ash, it is required to avoid this melting point temperature.

減温部11には冷却水ノズル12と冷却空気ノズル13が設置され、排ガスの温度を下げるために水、空気を吹き込む。短い時間でおよそ200℃程度にまで排ガスを冷却することができ、ダイオキシン類の再合成が行われ易い温度を避けることができる。二次燃焼部10から減温部11に800℃以上で送り込まれる排ガスは、まず冷却水ノズル12から噴出される水により、およそ500℃にまで冷却され、次に冷却空気ノズル13から噴出される空気によりおよそ200℃にまで冷却される。   A cooling water nozzle 12 and a cooling air nozzle 13 are installed in the temperature reducing unit 11 and blow water and air in order to lower the temperature of the exhaust gas. The exhaust gas can be cooled to about 200 ° C. in a short time, and the temperature at which dioxins are easily re-synthesized can be avoided. The exhaust gas sent from the secondary combustion unit 10 to the temperature reducing unit 11 at 800 ° C. or higher is first cooled to about 500 ° C. by water ejected from the cooling water nozzle 12 and then ejected from the cooling air nozzle 13. Cooled to about 200 ° C. by air.

二次燃焼部10で分解されたダイオキシン類は300℃から400℃程度の温度環境下で再合成してしまうため、短い時間で排ガスの冷却が行われる必要がある。すなわち、排ガス処理装置内の温度分布は、二次燃焼部10の800℃以上の高温部と減温部11のおよそ200℃以下の低温部に明確に分かれ、その中間である温度の空間が広がらないことが望ましい。なお、排ガスを冷却空気のみでも冷却可能なときは、冷却水は噴霧されないこともある。   Since dioxins decomposed in the secondary combustion section 10 are re-synthesized in a temperature environment of about 300 ° C. to 400 ° C., it is necessary to cool the exhaust gas in a short time. That is, the temperature distribution in the exhaust gas treatment apparatus is clearly divided into a high temperature part of 800 ° C. or higher in the secondary combustion part 10 and a low temperature part of approximately 200 ° C. or less in the temperature reducing part 11, and a temperature space in the middle is widened. Desirably not. When the exhaust gas can be cooled only with cooling air, the cooling water may not be sprayed.

二次燃焼部10と減温部11が一体になる排ガス処理装置は、外部材質は、耐熱性のある金属材料で円筒形状をなす。内部の二次燃焼部10には耐火キャスタブルを設置し、二次燃焼部10に比べ温度の低い減温部11には耐熱塗装を施して、排ガス処理装置の構造体を熱から保護する。   In the exhaust gas treatment apparatus in which the secondary combustion unit 10 and the temperature reduction unit 11 are integrated, the external material is a cylindrical shape made of a heat-resistant metal material. A fireproof castable is installed in the internal secondary combustion section 10, and a heat-resistant coating is applied to the temperature reducing section 11 having a lower temperature than the secondary combustion section 10 to protect the structure of the exhaust gas treatment apparatus from heat.

排ガスはその後除塵装置15へ送出される。このとき除塵装置入口付近では排ガス温度は150℃にまで冷却されている。除塵装置15は、電気集塵装置、バグフィルタ、マルチサイクロンなどがある。本実施例ではバグフィルタにより塵を収集する。バグフィルタで使われるろ布にはポリエステル、ポリアミド、ポリプロピレンなどの繊布、または、フエルト、耐熱ナイロン、ガラス繊維、テフロン(商標)が用いられる。そのため排ガスはこれらのろ布を通すことができる温度にまで冷却されている必要がある。集められた塵は、除塵装置下部に設けられた灰排出装置16により除塵装置外へ排出される。除塵装置後方には排ガスファン17が配置され、排ガスファン17は排ガスが灰溶融炉3から二次燃焼部10、減温部11、除塵装置15に順次流れるよう排ガスを引いている。塵を除いた排ガスは、脱硝装置、脱硫装置等を経て無害化される。   The exhaust gas is then sent to the dust removing device 15. At this time, the exhaust gas temperature is cooled to 150 ° C. in the vicinity of the entrance of the dust removing device. Examples of the dust removing device 15 include an electric dust collector, a bag filter, and a multi-cyclone. In this embodiment, dust is collected by a bug filter. As the filter cloth used in the bag filter, a fine cloth such as polyester, polyamide, or polypropylene, or felt, heat-resistant nylon, glass fiber, or Teflon (trademark) is used. Therefore, the exhaust gas needs to be cooled to a temperature at which these filter cloths can be passed. The collected dust is discharged out of the dust removing device by the ash discharging device 16 provided at the lower part of the dust removing device. An exhaust gas fan 17 is disposed behind the dust removal device, and the exhaust gas fan 17 draws the exhaust gas so that the exhaust gas sequentially flows from the ash melting furnace 3 to the secondary combustion unit 10, the temperature reduction unit 11, and the dust removal device 15. Exhaust gas excluding dust is rendered harmless through a denitration device, a desulfurization device, or the like.

排ガスの温度を監視するため、二次燃焼部入口、減温部入口、減温部出口、除塵装置入口、除塵装置出口に温度計測装置24、25、26、27を設置する。温度計測装置の排ガス温度の計測結果により、二次燃焼部バーナ5からの燃焼ガス噴霧、減温部の冷却水ノズル12より水噴霧を必要に応じて行う。   In order to monitor the temperature of the exhaust gas, temperature measuring devices 24, 25, 26, and 27 are installed at the secondary combustion unit inlet, the temperature reducing unit inlet, the temperature reducing unit outlet, the dust removing device inlet, and the dust removing device outlet. Depending on the measurement result of the exhaust gas temperature of the temperature measuring device, the combustion gas spray from the secondary combustion section burner 5 and the water spray from the cooling water nozzle 12 of the temperature reducing section are performed as necessary.

一方、灰溶融炉3で溶融された灰からは、メタルとスラグが生成される。出滓口20から出滓されたスラグは出滓樋21を流れ、第一ダクト下方に分岐した水砕ノズルカバー35を通り排出される。スラグは、分岐したダクト内において水砕水ノズル6から放出された冷却水によって砕かれ冷却される。その後スラグは冷却水槽7にたまりスラグ排出コンベヤ8によりスラグピット/メタルピット9へ運ばれる。なお、スラグの冷却は空気によるものでもよく、急冷、徐冷でもよい。メタルも傾動により、出滓口から出滓され、スラグ同様冷却され、スラグピット/メタルピット9に運ばれる。   On the other hand, metal and slag are generated from the ash melted in the ash melting furnace 3. The slag discharged from the tap outlet 20 flows through the tap 21 and is discharged through the granulated nozzle cover 35 branched below the first duct. The slag is crushed and cooled by the cooling water discharged from the granulated water nozzle 6 in the branched duct. Thereafter, the slag accumulates in the cooling water tank 7 and is transported to the slag pit / metal pit 9 by the slag discharge conveyor 8. The slag may be cooled by air, or may be rapidly cooled or gradually cooled. The metal is also tilted out from the spout, cooled in the same way as the slag, and transported to the slag pit / metal pit 9.

二次燃焼部10と減温部11が一体且つ同一の円筒内存在することから、排ガス処理装置において堆積物搬出装置14は一つ設置するだけで足りる。二次燃焼部10と減温部11から落下する堆積物や飛灰は、減温部下方のホッパ28に集まる。ホッパ28は二次燃焼部・減温部の塔と堆積物排出装置14をつなぐため堆積物搬出装置に向かって絞り込まれている。ホッパ28に集まった堆積物等は堆積物搬出装置14にて取り除かれる。従来のように二次燃焼室下部及び減温塔下部に別個に堆積物搬出装置14を置く必要がなくなった。堆積物搬出装置14は解砕部と搬送部からなる。解砕部はホッパ28にたまった堆積物を砕く役割を果たす。砕かれた堆積物は搬送部に載せられ、溶融飛灰貯槽に集められる。その後堆積物はキレートとコンクリートで固められ処分される。解砕部にはロータリーバルブ等を、移送部にはコンベヤ(ベルトコンベヤ、エプロンコンベヤ、パンコンベヤ、スクリューコンベヤ等)を用いることができる。   Since the secondary combustion unit 10 and the temperature reducing unit 11 are integrated and exist in the same cylinder, it is only necessary to install one deposit carry-out device 14 in the exhaust gas treatment device. Deposits and fly ash falling from the secondary combustion unit 10 and the temperature reducing unit 11 gather in the hopper 28 below the temperature reducing unit. The hopper 28 is narrowed down toward the deposit carry-out device in order to connect the tower of the secondary combustion section / temperature reduction section and the deposit discharge device 14. The deposits collected in the hopper 28 are removed by the deposit carry-out device 14. It is no longer necessary to separately place the deposit carry-out device 14 at the lower part of the secondary combustion chamber and the lower part of the temperature reduction tower as in the prior art. The deposit carry-out device 14 includes a crushing unit and a conveying unit. The crushing part plays a role of crushing the sediment accumulated in the hopper 28. The crushed deposit is placed on a transport unit and collected in a molten fly ash storage tank. The sediment is then hardened with chelate and concrete and disposed of. A rotary valve or the like can be used for the crushing unit, and a conveyor (a belt conveyor, an apron conveyor, a bread conveyor, a screw conveyor, or the like) can be used for the transfer unit.

従来必要であった第二ダクト31が不要になったことで、この部位の飛灰堆積がなくなった。すなわち清掃装置を取り付ける必要がなくなった。   Since the second duct 31 that has been necessary in the past is no longer necessary, the fly ash accumulation at this portion is eliminated. That is, it is no longer necessary to install a cleaning device.

図3に示す本発明を実施する第2の形態において、二次燃焼部10が出滓口20より下方に設置することができない場合において、第一ダクト23は、大きく上方に立ち上げることなく二次燃焼部10に接続する。出滓口部ダクト22は水砕ノズルカバー35に接続され、この水砕ノズルカバー35の上部は第一ダクト23に接続される。第一ダクト23は水平面を有さず、飛灰が堆積して閉塞するのを防止している。他は第1の実施例と同じである。   In the second mode for carrying out the present invention shown in FIG. 3, when the secondary combustion unit 10 cannot be installed below the tap outlet 20, the first duct 23 does not rise greatly upward. It connects to the next combustion part 10. The spout opening portion duct 22 is connected to the water granulation nozzle cover 35, and the upper portion of the water granulation nozzle cover 35 is connected to the first duct 23. The first duct 23 does not have a horizontal surface and prevents fly ash from accumulating and blocking. Others are the same as the first embodiment.

本発明を実施するための第1の形態の排ガス処理装置を有する灰処理設備の図。The figure of the ash treatment equipment which has the exhaust gas treatment equipment of the 1st form for carrying out the present invention. 本発明を実施するための第1の形態の排ガス処理装置を有する灰処理設備における出滓口部ダクトの形状と傾動の関係を示した図。The figure which showed the relationship between the shape and tilting of the tap outlet duct in the ash processing equipment which has the waste gas processing apparatus of the 1st form for implementing this invention. 本発明を実施するための第2の形態の排ガス処理装置を有する灰処理設備の図。The figure of the ash treatment equipment which has an exhaust gas treatment device of the 2nd form for carrying out the present invention. 従来技術の排ガス処理装置を有する灰処理設備の図。The figure of the ash processing equipment which has an exhaust gas processing apparatus of a prior art. 従来技術の排ガス処理装置を有する灰処理設備の図。The figure of the ash processing equipment which has an exhaust gas processing apparatus of a prior art.

符号の説明Explanation of symbols

1…投入灰貯槽
2…灰定量供給装置
3…灰溶融炉
4…出滓口バーナ
5…二次燃焼バーナ
6…水砕水ノズル
7…冷却水槽
8…スラグ排出コンベヤ
9…スラグピット/メタルピット
10…二次燃焼部
11…減温部
12…冷却水ノズル
13…冷却空気ノズル
14…堆積物排出装置
15…除塵装置
16…灰排出装置
17…排ガスファン
18…傾動装置
19…傾動軸
20…出滓口
21…出滓樋
22…出滓口部ダクト
23…第一ダクト
24…二次燃焼部入口温度計測装置
25…減温部入口温度計測装置
26…減温部出口温度計測装置
27…除塵装置入口温度計測装置
28…ホッパ
29…二次燃焼室
30…減温塔
31…第二ダクト
32…エアブラスタ
33…第三ダクト
34…第四ダクト
35…水砕ノズルカバー
DESCRIPTION OF SYMBOLS 1 ... Input ash storage tank 2 ... Ash fixed quantity supply apparatus 3 ... Ash melting furnace 4 ... Outlet burner 5 ... Secondary combustion burner 6 ... Granulated water nozzle 7 ... Cooling water tank 8 ... Slag discharge conveyor 9 ... Slag pit / metal pit DESCRIPTION OF SYMBOLS 10 ... Secondary combustion part 11 ... Temperature reduction part 12 ... Cooling water nozzle 13 ... Cooling air nozzle 14 ... Sediment discharge device 15 ... Dust removal device 16 ... Ash discharge device 17 ... Exhaust gas fan 18 ... Tilt device 19 ... Tilt shaft 20 ... Outlet port 21 ... Outlet port 22 ... Outlet port duct 23 ... First duct 24 ... Secondary combustion section inlet temperature measuring device 25 ... Temperature reducing section inlet temperature measuring device 26 ... Temperature reducing section outlet temperature measuring device 27 ... Dust removal device inlet temperature measuring device 28 ... Hopper 29 ... Secondary combustion chamber 30 ... Temperature reducing tower 31 ... Second duct 32 ... Air blaster 33 ... Third duct 34 ... Fourth duct 35 ... Granulated nozzle cover

Claims (6)

灰溶融炉と、前記灰溶融炉からの排ガスを処理する二次燃焼部と減温部とからなる排ガス処理装置とを備えた灰処理設備において、
前記減温部は前記二次燃焼部の下方に配置されるとともに、
前記灰溶融炉に設けられた出滓口に出滓口部ダクトを介して連通して、冷却水によってスラグを砕き冷却する水砕水ノズルが設置された水砕ノズルカバーが設けられ、
同水砕ノズルカバーの上部と前記第二次燃焼部の上部とを水平面を有さないダクトによって連通してなることを特徴とする灰処理設備。
In an ash treatment facility comprising an ash melting furnace, and an exhaust gas treatment device comprising a secondary combustion section for treating the exhaust gas from the ash fusion furnace and a temperature reduction section,
The reduced temperature portion Rutotomoni disposed below the secondary combustion unit,
A granulation nozzle cover provided with a granulated water nozzle that is connected to the tap port provided in the ash melting furnace via a tap port duct and crushes and cools the slag with cooling water is provided,
Ash treatment equipment, wherein Rukoto such communicates the upper portion of the upper and the secondary combustion unit of Domizu砕nozzle cover by the duct having no horizontal plane.
請求項1に記載の灰処理設備において、灰溶融炉の出滓口より下方に前記二次燃焼部を設けることを特徴とする灰処理設備。   The ash treatment facility according to claim 1, wherein the secondary combustion section is provided below the outlet of the ash melting furnace. 請求項1又は請求項2に記載の灰処理設備において、前記二次燃焼部と前記減温部を一体に備えたことを特徴とする灰処理設備。   The ash treatment facility according to claim 1 or 2, wherein the secondary combustion unit and the temperature reducing unit are integrally provided. 請求項1又は請求項2に記載の灰処理設備において、前記排ガス処理装置には前記減温部の下方にのみ堆積物排出装置が配置されていることを特徴とする灰処理設備。   3. The ash treatment facility according to claim 1, wherein a deposit discharge device is disposed only below the temperature reducing unit in the exhaust gas treatment device. 4. 請求項3に記載の灰処理設備において、前記二次燃焼部と前記減温部とは略鉛直に建てられた円筒からなることを特徴とする灰処理設備。   4. The ash treatment facility according to claim 3, wherein the secondary combustion section and the temperature reducing section are formed of a cylinder built substantially vertically. 請求項4に記載の灰処理設備において、前記堆積物排出装置は、解砕部と移送部とからなることを特徴とする灰処理設備 5. The ash treatment facility according to claim 4, wherein the deposit discharge device includes a crushing unit and a transfer unit .
JP2003376477A 2003-11-06 2003-11-06 Ash processing equipment Expired - Fee Related JP4197289B2 (en)

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JP5802070B2 (en) * 2011-06-30 2015-10-28 川崎重工業株式会社 Dust collector for fluidized bed gasification and melting equipment
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