JP2012159264A - Method and system for waste melting disposal - Google Patents

Method and system for waste melting disposal Download PDF

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JP2012159264A
JP2012159264A JP2011020739A JP2011020739A JP2012159264A JP 2012159264 A JP2012159264 A JP 2012159264A JP 2011020739 A JP2011020739 A JP 2011020739A JP 2011020739 A JP2011020739 A JP 2011020739A JP 2012159264 A JP2012159264 A JP 2012159264A
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waste
exhaust gas
grate
melting
pyrolysis residue
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JP5864865B2 (en
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Junichi Takada
純一 高田
Atsushi Kobayashi
淳志 小林
Ryo Makishi
諒 牧志
Masaharu Hirakura
将治 平倉
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Nippon Steel Engineering Co Ltd
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Abstract

PROBLEM TO BE SOLVED: To provide a method and a system for waste melting disposal which prevent clinker generation of a fire grate part of the same system.SOLUTION: In the waste melting disposal method where the gas generated both in the fire grate part 2 generating thermal decomposition residual substance and in the thermal decomposition residual substance melting part 3 of the melting furnace 6 melting the thermal decomposition residual substance by making coke as heat source is passed through the waste packed bed formed by charging the waste from the top of drying shaft part 1 for drying to dry up the waste, the gas passed through the waste packed bed is emitted from the exhaust discharge port 9 of the drying shaft part 1 to be processed for detoxication with an exhaust treatment system to be discharged through the exhaust flue 24, whereas the waste dried in the drying shaft part 1 is decomposed thermally in the fire grate part 2 to generate the thermal decomposition residual substance 19, which is continuously dropped from the fire grate part 2 to be supplied to the thermal decomposition residual substance melting part 3 for melting, the exhaust is brought out from the exhaust flue 24 to blow into below the fire grate part 2 for controlling temperature of the upper part of fire grate part less than a clinker generation temperature.

Description

本発明は、乾燥用シャフト部と熱分解残渣溶融部が火格子部を介して連設された廃棄物溶融装置による廃棄物溶融処理方法において、火格子部のクリンカ生成を防止する技術に関する。   The present invention relates to a technique for preventing generation of clinker in a grate part in a waste melting method by a waste melting apparatus in which a drying shaft part and a pyrolysis residue melting part are connected via a grate part.

廃棄物を溶融処理するシャフト炉式廃棄物溶融炉では、廃棄物中に生ごみ等の高水分ごみや木等の揮発分が多いため、廃棄物の一部が十分に乾燥されることなくまた、揮発分のガス化が行われることなく炉下部に下降した場合、水分や揮発分はいずれも雰囲気温度を低下させることになる。そのため、雰囲気温度を高く維持し非燃焼物を完全溶融するためには、結果としてコークス使用量を増やす必要があった。   In a shaft furnace type waste melting furnace that melts waste, there is a large amount of high-moisture waste such as garbage and volatile matter such as wood in the waste. When the volatile matter is lowered to the lower part of the furnace without being gasified, both moisture and volatile matter lower the ambient temperature. Therefore, in order to maintain the atmospheric temperature high and completely melt the non-combustible material, it is necessary to increase the amount of coke used as a result.

そこで、廃棄物溶融処理において、乾燥・熱分解を、燃焼・溶融と分離して行うことによりごみ中の水分や揮発分を除去して廃棄物が乾燥や熱分解されない状態で炉下部に下降することを防止し、それによって炉最下部における雰囲気温度の低下による灰分の溶融に使用されるコークス消費量を抑制して熱分解残渣の持つ熱量と少量のコークスの熱量にて完全溶融を達成することができる廃棄物溶融処理技術が提案されている(特許文献1参照)。   Therefore, in waste melting treatment, drying and thermal decomposition are performed separately from combustion and melting to remove moisture and volatiles in the waste, and the waste is lowered to the bottom of the furnace without being dried or pyrolyzed. To suppress the consumption of coke used for melting ash by lowering the ambient temperature at the bottom of the furnace, thereby achieving complete melting with the heat of the pyrolysis residue and the heat of a small amount of coke. A waste melting treatment technique that can be used has been proposed (see Patent Document 1).

前記特許文献1に示す廃棄物溶融炉は、図3に示すように、装入された廃棄物を乾燥する乾燥用シャフト部1、乾燥用シャフト部1で乾燥された廃棄物を熱分解して熱分解残渣を生成する火格子部2、熱分解残渣を燃焼・溶融する熱分解残渣溶融部3を下部に備えた溶融炉6からなる。乾燥用シャフト部1が火格子部2の入側の上方に配置され、熱分解残渣溶融部3が火格子部2の出側の下方に配置されてクランク形状に連通して一体に連設されている。なお、火格子の間から落下した熱分解残渣等は灰搬送装置により排出される。   As shown in FIG. 3, the waste melting furnace shown in Patent Document 1 thermally decomposes the waste dried by the drying shaft 1 and the drying shaft 1 to dry the charged waste. It comprises a melting furnace 6 having a grate part 2 for generating a pyrolysis residue and a pyrolysis residue melting part 3 for burning and melting the pyrolysis residue at the bottom. The drying shaft portion 1 is disposed above the entrance side of the grate portion 2, and the pyrolysis residue melting portion 3 is disposed below the exit side of the grate portion 2, communicated with the crank shape and integrally provided. ing. In addition, the pyrolysis residue etc. which fell from between the grate are discharged | emitted by an ash conveyance apparatus.

乾燥用シャフト部1の頂部には、排ガス出口9と廃棄物装入口10が設けられ、廃棄物装入口10は、装入の際にガスが吹き出すのを防ぐシール用蓋11が設けられている。乾燥用シャフト部1の下部にはプッシャー等の廃棄物移送装置12が設けられている。   An exhaust gas outlet 9 and a waste charging inlet 10 are provided at the top of the drying shaft portion 1, and the waste charging inlet 10 is provided with a sealing lid 11 for preventing gas from blowing out during charging. . A waste transfer device 12 such as a pusher is provided below the drying shaft portion 1.

排ガス出口9から排出される排ガスは、排ガス処理設備の燃焼室へ送って燃焼させ、燃焼により発生した燃焼排ガスは廃熱ボイラに送られて熱回収され、ボイラの排ガスは減温器で冷却してバグフィルターに導入して集じんする。集じん後の排ガスは、誘引送風機によって誘引され排ガス煙道24を通って煙突から排出される。   The exhaust gas discharged from the exhaust gas outlet 9 is sent to the combustion chamber of the exhaust gas treatment facility for combustion, and the combustion exhaust gas generated by the combustion is sent to the waste heat boiler for heat recovery, and the boiler exhaust gas is cooled by a temperature reducer. Introduce it into the bug filter and collect the dust. The exhaust gas after the dust collection is attracted by the induction fan and is discharged from the chimney through the exhaust gas flue 24.

火格子部2は、乾燥用シャフト部1から装入された廃棄物を熱分解させながら熱分解残渣溶融部3へ移動させる火格子13を備えている。なお、16は起動用のバーナ、17は乾燥用シャフト部に燃焼空気を吹き込むための空気吹込口である。   The grate part 2 includes a grate 13 that moves the waste charged from the drying shaft part 1 to the pyrolysis residue melting part 3 while thermally decomposing the waste. Reference numeral 16 denotes an activation burner, and 17 denotes an air blowing port for blowing combustion air into the drying shaft portion.

溶融炉6の熱分解残渣溶融部3は下方の炉床部4、この炉床部4の上に連なる朝顔部5を備える。炉床部4には酸素源として空気と酸素を吹き込む下段羽口7を備えるとともに、朝顔部5に空気を吹き込む上段羽口8が配置されている。熱分解残渣溶融部3には、従来のシャフト炉式廃棄物溶融炉の炉底部と同じくコークスベット18が形成される。コークス、石灰石などの副資材は溶融炉6の頂部の副資材装入口15から投入する。   The pyrolysis residue melting part 3 of the melting furnace 6 includes a lower hearth part 4 and a morning glory part 5 connected to the hearth part 4. The hearth section 4 includes a lower tuyere 7 for blowing air and oxygen as an oxygen source, and an upper tuyere 8 for blowing air into the morning glory part 5. A coke bed 18 is formed in the pyrolysis residue melting part 3 in the same manner as the bottom of a conventional shaft furnace type waste melting furnace. Auxiliary materials such as coke and limestone are fed from the auxiliary material inlet 15 at the top of the melting furnace 6.

前記構成の廃棄物溶融装置による処理方法について説明する。   A treatment method using the waste melting apparatus having the above-described configuration will be described.

乾燥用シャフト部1の頂部の廃棄物装入口10から装入されて乾燥用シャフト部1内に形成された廃棄物充填層は、火格子部2および熱分解残渣溶融部3から発生したガスが通過し、効率的に熱交換されて乾燥が行われる。乾燥用シャフト部1で乾燥された廃棄物を火格子部2で移動させながら熱分解により熱分解残渣19を生成し、生成した熱分解残渣は熱分解残渣溶融部3内へ落下してコークスベット18の熱源により燃焼・溶融され、溶融物は炉床部4の出湯口14から出湯される。排ガスは、乾燥用シャフト部1の廃棄物中を通過して排ガス出口9から排気される。   The waste packed bed formed in the drying shaft portion 1 by being charged from the waste charging port 10 at the top of the drying shaft portion 1 has gas generated from the grate portion 2 and the pyrolysis residue melting portion 3. It passes through and is efficiently heat exchanged for drying. A pyrolysis residue 19 is generated by pyrolysis while moving the waste dried by the drying shaft unit 1 through the grate unit 2, and the generated pyrolysis residue falls into the pyrolysis residue melting unit 3 to form a coke bed. It is burned and melted by 18 heat sources, and the melt is discharged from the hot water outlet 14 of the hearth part 4. The exhaust gas passes through the waste of the drying shaft portion 1 and is exhausted from the exhaust gas outlet 9.

特開2010−255890号公報JP 2010-255890 A

前記引用文献1記載の溶融処理方法では、火格子部では、乾燥された廃棄物を熱分解して熱分解残渣を生成するために火格子の迭風には加熱空気を使用している。加熱空気を使用すると、火格子部での燃焼温度が高くなりすぎて、連続運転を続けていると火格子部に徐々にクリンカが生成していき、クリンカが熱分解残渣の搬送能力の低下等を招き安定運転の妨げとなる。   In the melt processing method described in the cited document 1, in the grate portion, heated air is used as the screen of the grate in order to thermally decompose the dried waste and generate a pyrolysis residue. If heated air is used, the combustion temperature in the grate will become too high, and if continuous operation is continued, clinker will gradually form in the grate, causing the clinker to decrease the pyrolysis residue transport capacity, etc. Will interfere with stable operation.

そこで、本発明は、乾燥用シャフト部と熱分解残渣溶融部が火格子部を介して連設された廃棄物溶融装置による廃棄物溶融処理において、火格子部のクリンカ生成を防止する廃棄物溶融処理方法及びその装置を提供するものである。   Therefore, the present invention provides a waste melting for preventing clinker generation in a grate part in a waste melting process by a waste melting apparatus in which a drying shaft part and a pyrolysis residue melting part are connected via a grate part. A processing method and apparatus are provided.

本発明の廃棄物溶融処理方法は、廃棄物を乾燥する乾燥用シャフト部の頂部から廃棄物を乾燥用シャフト部内に装入して形成した廃棄物充填層に、熱分解残渣を生成する火格子部とコークスを熱源として熱分解残渣を溶融する熱分解残渣溶融部とで発生したガスを通過させて廃棄物を乾燥させ、前記廃棄物充填層を通過したガスを前記乾燥用シャフト部の排ガス排気口から排出して排ガス処理設備で無害化処理して排ガス煙道を経て放出し、乾燥用シャフト部で乾燥した廃棄物を火格子部で熱分解して熱分解残渣を生成し、生成した前記熱分解残渣を前記火格子部から連続的に落下させて前記熱分解残渣溶融部へ供給して溶融する廃棄物溶融処理方法において、前記排ガス煙道から排ガスを取り出して前記火格子部の下方に吹き込んで前記火格子部上部の温度をクリンカ生成温度未満に制御することを特徴とする。   The waste melting method of the present invention is a grate for generating a pyrolysis residue in a waste packed bed formed by charging waste into the drying shaft from the top of the drying shaft for drying the waste. The gas generated in the pyrolysis residue melting portion that melts the pyrolysis residue using the coke as a heat source is passed to dry the waste, and the gas that has passed through the waste packed bed is exhausted to the exhaust gas of the drying shaft portion. It is discharged from the mouth, detoxified in the exhaust gas treatment facility, discharged through the flue gas flue, and the waste dried in the drying shaft part is pyrolyzed in the grate part to produce a pyrolysis residue, In a waste melting method in which pyrolysis residue is continuously dropped from the grate portion, supplied to the pyrolysis residue melting portion and melted, exhaust gas is taken out from the flue gas flue and below the grate portion Infuse the fire And controlling the temperature of the terminal portion upper below the clinker formation temperature.

前記廃棄物溶融処理方法において、前記火格子部上部の温度を検出し、検出温度に応じて前記排ガス煙道からの排ガスを火格子の下方に吹き込んで前記火格子部上部の温度を600℃〜800℃の範囲に維持することを特徴とする。   In the waste melting treatment method, the temperature of the upper part of the grate part is detected, and the exhaust gas from the flue gas flue is blown below the grate according to the detected temperature so that the temperature of the upper part of the grate part is 600 ° C. to It is characterized by maintaining in the range of 800 ° C.

また、本発明の廃棄物溶融処理装置は、廃棄物装入口及び排ガス排気口が頂部に設けられ、前記廃棄物装入口から廃棄物が装入されて形成された廃棄物充填層に火格子部及び熱分解残渣溶融部で発生したガスを通過させて廃棄物を乾燥させるとともに、前記廃棄物充填層を通過したガスが前記排ガス排気口から排出される乾燥用シャフト部と、前記乾燥用シャフト部の前記排ガス排気口から排出された排ガスを無害化処理して排ガス煙道を経て放出する排ガス処理設備と、前記乾燥用シャフト部の下部に連設され、前記乾燥用シャフト部で乾燥した廃棄物を熱分解して熱分解残渣を生成する前記火格子部と、前記火格子部の前記熱分解残渣の出側に接続され、火格子部から落下して供給される熱分解残渣を、コークスを熱源として溶融処理する前記熱分解残渣溶融部とが順次配列された廃棄物処理装置において、前記排ガス煙道から排ガスを取り出し、前記火格子部内へ取り出した排ガスを吹き込む排ガス吹込口を接続する循環排ガス配管と、前記循環排ガス配管に設けられた、前記排ガス煙道から取り出された排ガス流量を調整する排ガス流量調整弁と、前記火格子部の上部に配置された温度計の温度検出信号により前記火格子部の上部の温度をクリンカ生成温度未満に維持するように前記排ガス流量調整弁の排ガス流量を制御する制御装置を配置したことを特徴とする。   Further, the waste melting treatment apparatus of the present invention is provided with a waste charging inlet and an exhaust gas exhaust outlet at the top, and a grate portion on a waste packed layer formed by charging waste from the waste charging inlet. And the drying shaft portion through which the gas generated in the pyrolysis residue melting portion passes and the waste is dried, and the gas that has passed through the waste filling layer is discharged from the exhaust gas exhaust port, and the drying shaft portion An exhaust gas treatment facility that detoxifies the exhaust gas discharged from the exhaust gas exhaust port and discharges it through an exhaust gas flue, and waste that is connected to the lower portion of the drying shaft portion and dried by the drying shaft portion The pyrolysis residue generated by pyrolyzing the pyrolysis residue is connected to the pyrolysis residue outlet side of the grate portion, and the pyrolysis residue supplied by dropping from the grate portion is converted into coke. Melt processing as a heat source In the waste treatment apparatus in which the pyrolysis residue melting part is sequentially arranged, a circulation exhaust gas pipe connecting an exhaust gas inlet for taking out the exhaust gas from the exhaust gas flue and blowing the exhaust gas taken out into the grate part, and the circulation An exhaust gas flow rate adjustment valve for adjusting the exhaust gas flow rate taken out from the exhaust gas flue, provided in the exhaust gas pipe, and a temperature detection signal of a thermometer arranged at the upper part of the grate unit, A control device for controlling the exhaust gas flow rate of the exhaust gas flow rate regulating valve is arranged so as to maintain the temperature below the clinker generation temperature.

前記廃棄物溶融処理装置において、前記制御装置が火格子部の上部の温度を600℃〜800℃の範囲に維持すること特徴とする。   In the waste melting apparatus, the controller maintains the temperature of the upper part of the grate portion in a range of 600 ° C to 800 ° C.

本発明は、煙道の排ガスを火格子部の下方に吹き込むことにより火格子部上部の温度を下げてクリンカ生成温度未満に制御できるので、火格子部のクリンカ付着が防止でき、その結果、長期安定運転が可能となる。   The present invention can control the temperature of the upper part of the grate part by lowering the temperature of the upper part of the grate part by blowing the flue gas into the lower part of the grate part, thereby preventing the clinker from adhering to the grate part. Stable operation is possible.

本発明の廃棄物溶融炉の概略図である。It is the schematic of the waste melting furnace of this invention. 循環排ガス混合割合と火格子燃焼ガス温度の関係を示すグラフである。It is a graph which shows the relationship between a circulating exhaust gas mixing ratio and a grate combustion gas temperature. 従来の廃棄物溶融炉の概略図である。It is the schematic of the conventional waste melting furnace.

図1に示す本発明の廃棄物溶融装置は、図2に示した従来の廃棄物溶融炉と同一構成には同一符号を付している。   In the waste melting apparatus of the present invention shown in FIG. 1, the same components as those of the conventional waste melting furnace shown in FIG.

図1において、本発明の廃棄物溶融処理装置は、装入された廃棄物を乾燥する乾燥用シャフト部1、乾燥用シャフト部1で乾燥された廃棄物を熱分解して熱分解残渣を生成する火格子部2、火格子部2で生成された熱分解残渣を燃焼・溶融する熱分解残渣溶融部3を備えた溶融炉6からなる。廃棄物溶融処理装置は、火格子部2の入側の上方に乾燥用シャフト部1が配置され、火格子部2の出側の下方に熱分解残渣溶融部3が配置されてクランク形状に連通して一体に連設される。   In FIG. 1, the waste melting treatment apparatus of the present invention generates a pyrolysis residue by thermally decomposing waste dried by the drying shaft portion 1 for drying the charged waste and the drying shaft portion 1. And a melting furnace 6 provided with a pyrolysis residue melting section 3 for burning and melting the pyrolysis residue generated in the grate section 2. In the waste melting apparatus, the drying shaft portion 1 is disposed above the entrance side of the grate portion 2 and the pyrolysis residue melting portion 3 is disposed below the exit side of the grate portion 2 so as to communicate with the crank shape. And are integrally connected.

乾燥用シャフト部1の頂部には、シール用蓋11を備えた廃棄物装入口10と、排ガス出口9が設けられる。乾燥用シャフト部1内に廃棄物装入口10から装入された廃棄物により廃棄物充填層が形成される。廃棄物充填層には火格子部2及び熱分解残渣溶融部3で発生した高温のガスが通過して熱交換により廃棄物を乾燥させ、廃棄物充填層を抜けたガスは頂部の排ガス出口9から排出される。   At the top of the drying shaft portion 1, a waste charging inlet 10 having a sealing lid 11 and an exhaust gas outlet 9 are provided. A waste filling layer is formed by the waste charged from the waste loading inlet 10 in the drying shaft portion 1. High-temperature gas generated in the grate portion 2 and the pyrolysis residue melting portion 3 passes through the waste packed bed to dry the waste by heat exchange, and the gas that has passed through the waste packed bed passes through the exhaust gas outlet 9 at the top. Discharged from.

排ガス出口9から排出される排ガスは、従来から使用されている廃棄物溶融装置の排ガス処理設備において処理する。すなわち、燃焼室で燃焼させ、燃焼により発生した燃焼排ガスをボイラに送って熱回収し、さらに、減温器で冷却してバグフィルターに導入して集じんする。集じん後の排ガスは、送風機によって誘引され排ガス煙道24を通って煙突から排出される。   The exhaust gas discharged from the exhaust gas outlet 9 is processed in an exhaust gas treatment facility of a waste melting apparatus that has been conventionally used. That is, it is burned in the combustion chamber, the flue gas generated by the combustion is sent to a boiler for heat recovery, further cooled by a temperature reducer, introduced into a bag filter and collected. The exhaust gas after the dust collection is attracted by the blower and is discharged from the chimney through the exhaust gas flue 24.

火格子部2は、乾燥用シャフト部1で乾燥された廃棄物を熱分解により熱分解残渣を生成させながら熱分解残渣溶融部3へ移動させる火格子13を備えている。火格子部2は、スト−カ炉と同様に、可動火格子13aと固定火格子13bとを交互に階段状又は傾斜状に組み合せることにより形成されており、各可動火格子13aを流体圧シリンダ等の駆動装置で前後方向へ一定のピッチで往復動させることによって、火格子上の廃棄物を撹拌しながら上流側から下流側へ前進させるようになっている。火格子部2へは下方から空気が送風される。火格子構造とすることによって、熱分解残渣溶融部3への熱分解残渣19の供給が連続的且つ安定的となって熱分解残渣溶融部3において熱分解残渣の安定的な溶融を確保することが可能となる。   The grate part 2 includes a grate 13 that moves the waste dried by the drying shaft part 1 to the thermal decomposition residue melting part 3 while generating a thermal decomposition residue by thermal decomposition. The grate part 2 is formed by combining the movable grate 13a and the fixed grate 13b alternately in a staircase shape or an inclined shape, as in the case of the stoker furnace. The waste on the grate is advanced from the upstream side to the downstream side while being agitated by reciprocating at a constant pitch in the front-rear direction with a driving device such as a cylinder. Air is blown into the grate portion 2 from below. By providing the grate structure, the supply of the pyrolysis residue 19 to the pyrolysis residue melting section 3 is continuous and stable, and the pyrolysis residue melting section 3 ensures stable melting of the pyrolysis residue. Is possible.

火格子部2は前段の火格子群2aと後段の火格子群2bの2段階に分かれ、前段の火格子群2aと後段火格子群2bがそれぞれ独立した駆動装置を有している。火格子部を前段の火格子群2aと後段の火格子群2bの2段とすることで、火格子部2における廃棄物の撹搾を強化することができ、より効率的に乾燥、熱分解を行うことが可能となる。   The grate unit 2 is divided into two stages, a front-stage grate group 2a and a rear-stage grate group 2b. The front-stage grate group 2a and the rear-stage grate group 2b have independent drive devices. By making the grate part into two stages of the front grate group 2a and the rear grate group 2b, it is possible to enhance the waste mixing in the grate part 2, and to dry and thermally decompose more efficiently. Can be performed.

また、火格子部2における廃棄物の熱分解状況によって、前段の火格子群2aと後段火格子群2bの独立した駆動装置により可動火格子13aの駆動速度、火格子からの送風量、送風温度等を個別に変化させて火格子部2における廃棄物の乾燥、熱分解状況を容易に制御することが可能となるので、廃棄物の乾燥、熱分解を適正化することが可能となる。例えば、廃棄物の乾燥・熱分解状態が不十分である場合は、前段の火格子群2aと比較して後段火格子群2bの火格子駆動速度を遅くすることによって熱分解状態を改善することが可能となる。   Further, depending on the thermal decomposition state of the waste in the grate part 2, the driving speed of the movable grate 13a, the air flow rate from the grate, the air temperature by the independent drive devices of the front grate group 2a and the rear grate group 2b It is possible to easily control the drying and thermal decomposition status of the waste in the grate portion 2 by changing the above individually, so that the drying and thermal decomposition of the waste can be optimized. For example, when the dry / pyrolytic state of the waste is insufficient, the pyrolysis state is improved by slowing the grate driving speed of the rear grate group 2b as compared with the front grate group 2a. Is possible.

また、後段の火格子群2bの傾斜角度は前段の火格子群2aの傾斜角度より小さくすることが望ましい。図1では、後段の火格子群2bを水平にすることにより、後段の火格子群2b側に向かって下方向に傾斜している前段の火格子群2aの傾斜角度より小さくしている。傾斜角度を変えることで、ごみの撹拌を強化することが可能となる。さらに後段の火格子2bの傾斜角度を前段の火格子2aよりも緩やかにすることで、火格子部2から熱分解が不十分な熱分解残渣が熱分解残渣溶融部3に供給されることを抑制することが容易となる。そうすることによって、熱分解残渣溶融部3におけるコークス等の外部燃焼使用量を適正化することが可能となる。なお、乾燥用シャフト部1から火格子部2へ廃棄物を確実に供給するため、前段の火格子群2aは、図1に示すように、水平階段状に設置されていることが望ましい。なお、火格子部2から落下した熱分解残渣等はコンベア20で排出される。   Further, it is desirable that the inclination angle of the rear-stage grate group 2b be smaller than the inclination angle of the front-stage grate group 2a. In FIG. 1, the rear grate group 2 b is leveled to be smaller than the inclination angle of the front grate group 2 a that is inclined downward toward the rear grate group 2 b side. By changing the inclination angle, it is possible to enhance the stirring of the garbage. Furthermore, by making the inclination angle of the rear grate 2b gentler than that of the front grate 2a, the pyrolysis residue that is not sufficiently pyrolyzed is supplied from the grate part 2 to the pyrolysis residue melting part 3. It becomes easy to suppress. By doing so, it becomes possible to optimize the amount of external combustion used such as coke in the pyrolysis residue melting part 3. In order to reliably supply waste from the drying shaft portion 1 to the grate portion 2, it is desirable that the front grate group 2a is installed in a horizontal step shape as shown in FIG. In addition, the thermal decomposition residue etc. which fell from the grate part 2 are discharged | emitted by the conveyor 20. FIG.

熱分解残渣溶融部3は、炉床部4には酸素源として空気と酸素を吹き込む下段羽口7を備えるとともに、朝顔部5に空気を吹き込む上段羽口8が配置されている。炉床部4には、従来のシャフト炉式廃棄物溶融炉と同じくコークスベット18が形成され、溶融物を出湯する出湯口14が設けられる。コークス、石灰石などの副資材は、溶融炉6の頂部に設けられ、装入の際にガスが吹き出すのを防ぐシール用蓋を備えた副資材装入口15から投入する。   The pyrolysis residue melting part 3 includes a lower tuyere 7 for blowing air and oxygen as an oxygen source in the hearth part 4, and an upper tuyere 8 for blowing air into the morning glory part 5. In the hearth 4, a coke bed 18 is formed as in the conventional shaft furnace type waste melting furnace, and a hot water outlet 14 for pouring the melt is provided. Auxiliary materials such as coke and limestone are provided at the top of the melting furnace 6 and are introduced from an auxiliary material charging port 15 provided with a sealing lid for preventing gas from blowing out during charging.

排ガス煙道24と火格子部2は循環排ガス配管25で接続され、排ガス煙道24から取り出した排ガスは循環排ガス配管25を通って火格子部2の排ガス吹込口21から火格子部2内の下方へ供給可能になっている。循環排ガス配管25からの排ガス吹込量は排ガス流量調整弁22により調整される。   The exhaust gas flue 24 and the grate part 2 are connected by a circulation exhaust gas pipe 25, and the exhaust gas taken out from the exhaust gas flue 24 passes through the circulation exhaust gas pipe 25 from the exhaust gas inlet 21 of the grate part 2 in the grate part 2. It can be supplied downward. The exhaust gas injection amount from the circulation exhaust gas pipe 25 is adjusted by the exhaust gas flow rate adjustment valve 22.

火格子部2の温度は火格子部の上部に配置された温度計T1により検出される。温度計T1の温度検出信号は制御装置23に入力され、制御装置23では、検出温度が設定温度と比較され、その結果に応じて排ガス吹込量が演算され、排ガス流量調整弁22を制御して排ガス吹込量が調整される。   The temperature of the grate part 2 is detected by a thermometer T1 arranged at the upper part of the grate part. The temperature detection signal of the thermometer T1 is input to the control device 23. The control device 23 compares the detected temperature with the set temperature, calculates the exhaust gas injection amount according to the result, and controls the exhaust gas flow rate adjustment valve 22. The exhaust gas injection amount is adjusted.

前記構成を有する廃棄物処理装置において、乾燥用シャフト部1の頂部の廃棄物装入口10から廃棄物が乾燥用シャフト部1内に装入されて廃棄物充填層が形成され、この廃棄物充填層に火格子部2および熱分解残渣溶融部3で発生した排ガスが通過することによって熱交換され、廃棄物が効率的に乾燥される。乾燥用シャフト部1の廃棄物充填層を通過した熱交換後のガスは、排ガス出口9から排気される。乾燥用シャフト部1で乾燥された廃棄物は火格子部2に移動し、ここで熱分解させて熱分解残渣19を生成する。   In the waste treatment apparatus having the above-described configuration, waste is charged into the drying shaft portion 1 from the waste inlet 10 at the top of the drying shaft portion 1 to form a waste filling layer. When the exhaust gas generated in the grate part 2 and the pyrolysis residue melting part 3 passes through the layer, heat exchange is performed, and the waste is efficiently dried. The heat-exchanged gas that has passed through the waste-filled layer of the drying shaft portion 1 is exhausted from the exhaust gas outlet 9. The waste dried by the drying shaft portion 1 moves to the grate portion 2 where it is thermally decomposed to generate a pyrolysis residue 19.

火格子部2の火格子13には廃棄物の自己燃焼に必要な空気が供給される。空気比は0.1〜0.8が好ましい。火格子部2の温度は温度計T1で検出されており、検出温度に応じて制御装置23により排ガス流量調整弁22を制御して排ガス煙道からの排ガスの吹込量を調節して、火格子部2の温度が600℃〜800℃に収まるように調整して、クリンカ生成温度にならないように運転される。   Air necessary for self-combustion of waste is supplied to the grate 13 of the grate unit 2. The air ratio is preferably 0.1 to 0.8. The temperature of the grate part 2 is detected by the thermometer T1, and the exhaust gas flow rate adjusting valve 22 is controlled by the control device 23 according to the detected temperature to adjust the amount of exhaust gas blown from the exhaust gas flue. The temperature of the part 2 is adjusted so as to be within a range of 600 ° C. to 800 ° C., and is operated so as not to reach the clinker generation temperature.

生成された熱分解残渣19は火格子部2の出側の残渣落とし口から熱分解残渣溶融部3内へ落下し、コークスベット18の熱源により燃焼、溶融される。溶融物は炉床部4の出湯口14から排出される。   The generated pyrolysis residue 19 falls from the residue drop outlet on the exit side of the grate part 2 into the pyrolysis residue melting part 3 and is burned and melted by the heat source of the coke bed 18. The melt is discharged from the outlet 14 of the hearth part 4.

以下、本発明を適用した実施例について説明する。   Examples to which the present invention is applied will be described below.

従来、通常は火格子部には空気比が設定値(例えば0.3)になるように制御して送風(100%空気)している。   Conventionally, normally, the grate portion is blown (100% air) by controlling the air ratio to be a set value (for example, 0.3).

一方、本発明では、火格子部ガス温度T1が設定温度(例えば600℃)となるように、循環排ガス量を加える。なお、循環排ガス混合割合の目標範囲は、火格子燃焼ガス温度が600℃〜800℃に収まるように制御する。   On the other hand, in the present invention, the amount of circulating exhaust gas is added so that the grate gas temperature T1 becomes a set temperature (for example, 600 ° C.). In addition, the target range of the circulating exhaust gas mixture ratio is controlled so that the grate combustion gas temperature falls within 600 ° C to 800 ° C.

このとき、総酸素流量は変化しないよう、火格子送風空気量の方を絞る必要がある。具体的には、循環排ガス量と、循環排ガスO濃度(=煙突O分析計指示値)から、循環排ガス中のO量を演算し、そのO量に見合う分の空気量(=O量/0.21)を、火格子送風空気量から減らすような流量制御を行う。 At this time, it is necessary to squeeze the grate air flow so that the total oxygen flow rate does not change. Specifically, the amount of O 2 in the circulating exhaust gas is calculated from the circulating exhaust gas amount and the circulating exhaust gas O 2 concentration (= indicated value of the chimney O 2 analyzer), and the amount of air corresponding to the O 2 amount (= The flow rate control is performed so that the amount of O 2 /0.21) is reduced from the amount of grate blown air.

図2に循環排ガス混合割合と火格子燃焼ガス温度の関係を示す。循環排ガス混合により、総酸素量を変えることなく(空気比を変えることなく)、ごみを燃焼させ、燃焼温度は所定の設定温度に下げることができる。   FIG. 2 shows the relationship between the circulating exhaust gas mixture ratio and the grate combustion gas temperature. By circulating exhaust gas mixing, waste can be burned without changing the total oxygen amount (without changing the air ratio), and the combustion temperature can be lowered to a predetermined set temperature.

1:乾燥用シャフト部 2:火格子部
3:熱分解残渣溶融部 4:炉床部
5:朝顔部 6:溶融炉
7:下段羽口 8:上段羽口
9:排ガス排気口 10:廃棄物装入口
11:シール用蓋 12:廃棄物供給装置
13:火格子 14:出湯口
15:副資材装入口 16:バーナ
17:乾燥用シャフト部羽口 18:コークスベット
19:熱分解残渣 20:コンベア
21:排ガス吹込口 22:排ガス流量調整弁
23:制御装置 24:排ガス煙道
25:循環排ガス配管
1: Drying shaft part 2: Grate part 3: Pyrolysis residue melting part 4: Hearth part 5: Morning glory part 6: Melting furnace 7: Lower tuyere 8: Upper tuyere 9: Exhaust vent 10: Waste Inlet 11: Sealing lid 12: Waste supply device 13: Grate 14: Outlet 15: Sub-material inlet 16: Burner 17: Drying shaft tuyere 18: Coke bed 19: Pyrolysis residue 20: Conveyor 21: Exhaust gas inlet 22: Exhaust gas flow rate adjustment valve 23: Control device 24: Exhaust gas flue 25: Circulating exhaust gas piping

Claims (4)

廃棄物を乾燥する乾燥用シャフト部の頂部から廃棄物を乾燥用シャフト部内に装入して形成した廃棄物充填層に、熱分解残渣を生成する火格子部とコークスを熱源として熱分解残渣を溶融する熱分解残渣溶融部とで発生したガスを通過させて廃棄物を乾燥させ、
前記廃棄物充填層を通過したガスを前記乾燥用シャフト部の排ガス排気口から排出して排ガス処理設備で無害化処理して排ガス煙道を経て放出し、
乾燥用シャフト部で乾燥した廃棄物を火格子部で熱分解して熱分解残渣を生成し、
生成した前記熱分解残渣を前記火格子部から連続的に落下させて前記熱分解残渣溶融部へ供給して溶融する廃棄物溶融処理方法において、
前記排ガス煙道から排ガスを取り出して前記火格子部の下方に吹き込んで前記火格子部上部の温度をクリンカ生成温度未満に制御することを特徴とする廃棄物溶融処理方法。
The waste packed bed formed by charging the waste into the drying shaft from the top of the drying shaft that dries the waste contains the grate and coke that generate the pyrolysis residue as the heat source. The gas generated in the melting part of the pyrolysis residue that melts is passed through to dry the waste,
The gas that has passed through the waste packed bed is discharged from the exhaust gas exhaust port of the drying shaft part, detoxified in the exhaust gas treatment facility and discharged through the exhaust gas flue,
Wastes dried on the drying shaft are pyrolyzed in the grate to produce pyrolysis residues,
In the waste melting treatment method in which the generated pyrolysis residue is continuously dropped from the grate portion and supplied to the pyrolysis residue melting portion to be melted,
A waste melting method, wherein exhaust gas is taken out from the flue gas flue and blown below the grate part to control the temperature of the upper part of the grate part below a clinker generation temperature.
前記火格子部上部の温度を検出し、検出温度に応じて前記排ガス煙道からの排ガスを火格子の下方に吹き込んで前記火格子部上部の温度を600℃〜800℃の範囲に維持することを特徴とする請求項1に記載の廃棄物溶融処理方法。   The temperature of the upper part of the grate part is detected, and the exhaust gas from the flue gas flue is blown below the grate according to the detected temperature to maintain the temperature of the upper part of the grate part in a range of 600 ° C to 800 ° C. The waste melting method according to claim 1. 廃棄物装入口及び排ガス排気口が頂部に設けられ、前記廃棄物装入口から廃棄物が装入されて形成された廃棄物充填層に火格子部及び熱分解残渣溶融部で発生したガスを通過させて廃棄物を乾燥させるとともに、前記廃棄物充填層を通過したガスが前記排ガス排気口から排出される乾燥用シャフト部と、
前記乾燥用シャフト部の前記排ガス排気口から排出された排ガスを無害化処理して排ガス煙道を経て放出する排ガス処理設備と、
前記乾燥用シャフト部の下部に連設され、前記乾燥用シャフト部で乾燥した廃棄物を熱分解して熱分解残渣を生成する前記火格子部と、
前記火格子部の前記熱分解残渣の出側に接続され、火格子部から落下して供給される熱分解残渣を、コークスを熱源として溶融処理する前記熱分解残渣溶融部とが順次配列された廃棄物処理装置において、
前記排ガス煙道から排ガスを取り出し、前記火格子部内へ取り出した排ガスを吹き込む排ガス吹込口を接続する循環排ガス配管と、
前記循環排ガス配管に設けられた、前記排ガス煙道から取り出された排ガス流量を調整する排ガス流量調整弁と、
前記火格子部の上部に配置された温度計の温度検出信号により前記火格子部の上部の温度をクリンカ生成温度未満に維持するように前記排ガス流量調整弁の排ガス流量を制御する制御装置を配置したことを特徴とする廃棄物溶融処理装置。
A waste charging inlet and exhaust gas exhaust outlet are provided at the top, and gas generated in the grate and pyrolysis residue melting part passes through the waste filling layer formed by charging waste from the waste charging inlet. And drying the waste, and the drying shaft portion through which the gas that has passed through the waste filling layer is discharged from the exhaust gas exhaust port,
Exhaust gas treatment equipment for detoxifying exhaust gas discharged from the exhaust gas exhaust port of the drying shaft portion and releasing it through an exhaust gas flue,
The grate portion that is connected to the lower portion of the drying shaft portion and pyrolyzes the waste material dried by the drying shaft portion to generate a pyrolysis residue;
The pyrolysis residue melting part connected to the outlet side of the pyrolysis residue of the grate part and dropping the pyrolysis residue supplied from the grate part using the coke as a heat source is sequentially arranged. In waste treatment equipment,
Extracting the exhaust gas from the exhaust gas flue, circulating exhaust gas piping connecting the exhaust gas inlet for blowing the exhaust gas extracted into the grate portion,
An exhaust gas flow rate adjusting valve for adjusting an exhaust gas flow rate provided in the circulating exhaust gas pipe and taken out from the exhaust gas flue;
A control device is provided for controlling the exhaust gas flow rate of the exhaust gas flow rate adjusting valve so as to maintain the temperature of the upper portion of the grate portion below a clinker generation temperature by a temperature detection signal of a thermometer disposed at the upper portion of the grate portion. A waste melting treatment apparatus characterized by that.
前記制御装置が火格子部の上部の温度を600℃〜800℃の範囲に維持すること特徴とする請求項3に記載の廃棄物溶融処理装置。   The waste melting apparatus according to claim 3, wherein the controller maintains the temperature of the upper part of the grate portion in a range of 600C to 800C.
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KR101760443B1 (en) 2017-05-23 2017-07-21 주식회사 하은산업 Device and method for recovering nonferrous metal and fine aggregate from printed circuit board

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