JPS63273715A - Incinerator for large-size refuse - Google Patents

Incinerator for large-size refuse

Info

Publication number
JPS63273715A
JPS63273715A JP10942987A JP10942987A JPS63273715A JP S63273715 A JPS63273715 A JP S63273715A JP 10942987 A JP10942987 A JP 10942987A JP 10942987 A JP10942987 A JP 10942987A JP S63273715 A JPS63273715 A JP S63273715A
Authority
JP
Japan
Prior art keywords
exhaust gas
combustion chamber
temp
primary combustion
chamber
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Pending
Application number
JP10942987A
Other languages
Japanese (ja)
Inventor
Kyosuke Sono
恭輔 園
Yoshihiro Tsuji
辻 義廣
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Kurimoto Ltd
Kurimoto Iron Works Ltd
Original Assignee
Kurimoto Ltd
Kurimoto Iron Works Ltd
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Kurimoto Ltd, Kurimoto Iron Works Ltd filed Critical Kurimoto Ltd
Priority to JP10942987A priority Critical patent/JPS63273715A/en
Publication of JPS63273715A publication Critical patent/JPS63273715A/en
Pending legal-status Critical Current

Links

Abstract

PURPOSE:To improve remarkably the capture effect of heavy metals in case of using a bag filter as a dust collector by a method wherein an incinerator consisting of a primary combustion chamber capable of accomodating uncrushed large-size refuse and a secondary combustion chamber for combustion exhaust gas, a spray cooling system ejecting water into an exhaust gas passage, a feeder for alkali powder, and a dust collector are assembled. CONSTITUTION:The amount of air supplied to a primary combustion chamber 2 is low excess one and the formation of high temp. in the chamber is controlled and the thermal decomposition of plastics is activated. It is proper to keep the temp. in the chamber 1 at a temp. of about 600-700 deg.C. Temp. is controlled by automatic operation in such a manner that the temp. is raised by the ignition of an auxiliary burner 8 and water is sprayed from spray ports 21. It is desirably to keep the temp. in the chamber 2 at 800 deg.C or more and the temp. is raised by the automatic ignition of an after-burner 9. Exhaust gas flowing in a spray cooling system placed in an exhaust gas passage 16 and being cooled is mixed with alkali powder charged from a feeder 26 for alkali powder through a supply port 25 while the exhaust gas is passing through the passage 15 and then dust contained in the exhaust gas is captured by the bags of a bag filter 27.

Description

【発明の詳細な説明】 〔産業上の利用分野〕 この発明は生活系から廃棄される粗大ごみを比較的小規
模な装置で簡単に焼却処理せしめるようにした焼却処理
装置に関するものである。
DETAILED DESCRIPTION OF THE INVENTION [Industrial Field of Application] The present invention relates to an incineration device that can easily incinerate bulky waste discarded from everyday life using a relatively small-scale device.

〔従来の技術〕[Conventional technology]

生活系から廃棄される粗大ごみは、比較的大きな都市で
は、収集してきた粗大ごみを大型の破砕機によって破砕
し、この破砕物を分別装置にて分別して金属類、可燃物
および不燃物に大別する、いわゆる粗大ごみ破砕処理設
備が設置されている。
In relatively large cities, the bulky waste that is discarded from daily life is crushed by a large crusher, and the crushed waste is separated into metals, combustibles, and noncombustibles by a sorting device. Separate, so-called bulky waste crushing equipment is installed.

また、上記の設備で処理されたもののうち、金属は資源
回収され、不燃物は埋立などに用い、可燃物は別途設け
られた焼却炉で焼却される。また、プラスチックは溶解
炉などにより処理される。
Furthermore, among the materials processed in the above equipment, metals are recovered as resources, noncombustible materials are used for landfill, and combustible materials are incinerated in a separately provided incinerator. Additionally, plastics are processed using a melting furnace or the like.

ここで、生活系粗大ごみとは、生ごみを除くその他のご
みであり、例えば家電製品(冷蔵庫、テレビ、洗濯機な
ど)、家具(ソファ、タンスなど)、寝具(フトン、マ
ット、衣服)、陶磁器などであり、これらは金属、プラ
スチック、木、布などの多種の材料が複雑に組合された
ものからなる。
Here, household bulky waste refers to other garbage other than food waste, such as home appliances (refrigerators, televisions, washing machines, etc.), furniture (sofas, chests of drawers, etc.), bedding (futons, mats, clothes), Ceramics, etc., are made of complex combinations of various materials such as metal, plastic, wood, and cloth.

このような生活系粗大ごみは、前記の破砕処理設備によ
り破砕したのち焼却するシステムが最も効果的かつ能率
的なごみ処理システムといえる。
The most effective and efficient waste treatment system for such bulky household waste is to crush it using the above-mentioned crushing equipment and then incinerate it.

〔発明が解決しようとする問題点〕[Problem that the invention seeks to solve]

上記のようなごみの処理システムは、大都市のような大
量のごみを収集処理する必要のある地域においては経済
的な立場からもきわめて有効な手段であるが、小さい回
付のようにごみの量が少ない自治体地域では、上記のよ
うな大規模な設備を設けることは、多大な設備費を要す
るとともにランニングコストが大であるなどの理由から
不可能であるため、粗大ごみの処理に苦慮している自治
体が多い現状である。
The above-mentioned garbage disposal system is an extremely effective means from an economic standpoint in areas such as large cities where large amounts of garbage need to be collected and processed. In local government areas where there is little waste, it is impossible to install large-scale facilities like the one mentioned above due to the high equipment costs and high running costs. The current situation is that many local governments have

〔問題点を解決するための手段] 上記の問題点を解決するために、この発明は未破砕の粗
大ごみを収納可能な一次燃焼室と、この一次燃焼室で発
生した燃焼排ガスを再燃焼させる二次燃焼室からなる焼
却炉と、この焼却炉から、大気に通じる排ガス通路に、
高温排ガスに水を噴射するスプレー冷却装置、アルカリ
粉供給装置および集塵機を組込んだものである。
[Means for Solving the Problems] In order to solve the above problems, the present invention includes a primary combustion chamber that can store unshredded bulky waste, and re-combusts the combustion exhaust gas generated in this primary combustion chamber. An incinerator consisting of a secondary combustion chamber and an exhaust gas passage leading to the atmosphere from this incinerator.
It incorporates a spray cooling device that injects water into high-temperature exhaust gas, an alkaline powder supply device, and a dust collector.

〔作用〕[Effect]

この発明は上記の構成であり、未破砕のままの粗大ごみ
を一次燃焼室に収容して、ここでガスバーナなどによっ
て粗大ごみの中の可燃物を燃焼および熱分解する。
This invention has the above-mentioned configuration, and uncrushed bulky waste is stored in the primary combustion chamber, where the combustible materials in the bulky waste are combusted and thermally decomposed using a gas burner or the like.

上記の一次燃焼室内で発生した燃焼排ガス、すなわち、
−酸化炭素、炭化水素などの未燃ガス、未燃カーボンお
よび塩化水素のうち、前記未燃ガス、未燃カーボンをつ
ぎの二次燃焼室で完全燃焼させ、この完全燃焼後の高温
ガスをスプレーによる冷却水の噴射により冷却する。
The combustion exhaust gas generated in the above primary combustion chamber, i.e.
- Among unburned gases such as carbon oxides and hydrocarbons, unburned carbon, and hydrogen chloride, the unburned gases and unburned carbon are completely combusted in the next secondary combustion chamber, and the high temperature gas after complete combustion is sprayed. Cooled by jetting cooling water.

こうして冷却された排ガスはアルカリ粉供給装置から供
給されたアルカリ粉を混合して排ガス中に残存する塩化
水素を中和せしめ、ついで、バッグフィルタなどの集塵
機により排ガス中の煤塵や粉塵、中和物の粉などが除去
されて大気中に放出される。
The thus cooled exhaust gas is mixed with alkaline powder supplied from the alkaline powder supply device to neutralize hydrogen chloride remaining in the exhaust gas, and then passed through a dust collector such as a bag filter to remove soot, dust, and neutralized substances from the exhaust gas. dust etc. are removed and released into the atmosphere.

一方、一次燃焼室で所要時間燃焼したのちの焼却残渣は
一次燃焼室より取出し、除去したのち、つぎの粗大ごみ
を再び一次燃焼室内に収容して前記と同様の焼却を行な
う。
On the other hand, the incineration residue after being burned for the required time in the primary combustion chamber is taken out from the primary combustion chamber and removed, and then the next bulky waste is stored in the primary combustion chamber again and incinerated in the same manner as above.

〔実施例〕〔Example〕

第1図に示す実施例において、1は、一次燃焼室2と二
次燃焼室3からなる焼却炉で、再燃焼室は上部の連通路
4によって通じている。
In the embodiment shown in FIG. 1, reference numeral 1 denotes an incinerator consisting of a primary combustion chamber 2 and a secondary combustion chamber 3, and the re-combustion chamber is communicated with through a communication passage 4 at the top.

5は一次燃焼室2内から屋外に延びた粗大ごみの運搬手
段で、例えばパンコンベヤのような耐熱金属製のもので
ある。
Reference numeral 5 denotes a means for transporting bulky waste extending from the inside of the primary combustion chamber 2 to the outdoors, and is made of heat-resistant metal, such as a pan conveyor.

6は一次燃焼室2および二次燃焼室3の両側壁に設けた
多数の空気吹込口で、送風機7により吸込まれた外気が
多数の吹込口6から一次燃焼室2および二次燃焼室3内
に供給される。
Reference numeral 6 denotes a large number of air inlets provided on both side walls of the primary combustion chamber 2 and the secondary combustion chamber 3, and the outside air sucked in by the blower 7 is passed through the many air inlets 6 into the primary combustion chamber 2 and the secondary combustion chamber 3. supplied to

また一次燃焼室2の一部にはガスまたは重油を燃料とす
る助燃バーナー8を設け、二次燃焼室3の連通路4に近
い部分には同じ燃料によるアフターバーナ9を設ける。
Further, an auxiliary combustion burner 8 using gas or heavy oil as fuel is provided in a part of the primary combustion chamber 2, and an afterburner 9 using the same fuel is provided in a portion of the secondary combustion chamber 3 near the communication path 4.

10は焼却炉1や同炉外に出た運搬手段5、あるいは駐
車場11などを覆う建屋、12は同建屋の天井を走行す
るごみ供給クレーン、13は焼却炉1の入口を開閉する
シャッタである。
10 is a building that covers the incinerator 1, the transportation means 5 outside the incinerator, or the parking lot 11, 12 is a garbage supply crane that runs on the ceiling of the building, and 13 is a shutter that opens and closes the entrance to the incinerator 1. be.

二次燃焼室3の下部には排ガス通路15を連通させ、そ
の途中を倒立U字形に屈曲させてスプレー冷却装置16
を設ける。
An exhaust gas passage 15 is communicated with the lower part of the secondary combustion chamber 3, and a spray cooling device 16 is formed by bending the passage into an inverted U-shape.
will be established.

上記冷却装置16はそめ入口側にベンチュリ一部17を
設け、ここに水噴射ノズル18を設け、このノズル18
を水槽19に設けた給水ポンプ20に連結し、前記焼却
炉1の上部に設けた散水口21も電磁弁22を介してポ
ンプ20に連通させる。
The cooling device 16 is provided with a venturi part 17 on the inlet side, a water injection nozzle 18 is provided here, and this nozzle 18
is connected to a water supply pump 20 provided in a water tank 19, and a water sprinkling port 21 provided in the upper part of the incinerator 1 is also communicated with the pump 20 via a solenoid valve 22.

上記スプレー冷却装置16に続く屈曲した部分にアルカ
リ粉供給口25を設ける。この供給口25はアルカリ粉
供給装置26から供給されたアルカリ粉を排ガス通B1
5中に供給するためのものである。
An alkali powder supply port 25 is provided in a bent portion following the spray cooling device 16. This supply port 25 allows the alkali powder supplied from the alkali powder supply device 26 to pass through the exhaust gas B1.
It is for supplying during 5th.

27はバッグフィルタで、その下部の入口に前記排ガス
通路15が連通し、このバッグフィルタ27の上部を排
風機29の吸込口に連通させ、同排風機の吐出口はスタ
ック30に連通させる。
Reference numeral 27 designates a bag filter, the lower inlet of which communicates with the exhaust gas passage 15, the upper part of the bag filter 27 communicates with the suction port of an exhaust fan 29, and the discharge port of the exhaust fan 29 communicates with the stack 30.

上記の実施例において、クレーン12により運搬手段5
上へ粗大ごみ31を供給し、シャッタ13を開いて運搬
手段5の駆動により粗大ごみ31を一次燃焼室2内に搬
入する。
In the above embodiment, the crane 12 transports the conveyor 5
The bulky waste 31 is supplied upward, the shutter 13 is opened, and the transport means 5 is driven to carry the bulky waste 31 into the primary combustion chamber 2.

つぎにシャッタ13を閉じ、運搬手段5を止めて粗大ご
み31を設置した状態で助燃バーナ8に点火して粗大ご
み31を燃焼させるが、このとき送風機7を運転して各
空気吹込口6から新鮮な外気を吹き込んで燃焼をたすけ
る。
Next, the shutter 13 is closed, the transportation means 5 is stopped, and the oversized garbage 31 is placed in the auxiliary combustion burner 8 to ignite the oversized garbage 31. Blow in fresh outside air to aid combustion.

ここで、一次燃焼室2に供給される空気量は低過剰空気
量とし、高発熱量を有するプラスチックなどの急激な燃
焼と、これによる室内の高温化を抑制し、プラスチック
の熱分解を促進する。
Here, the amount of air supplied to the primary combustion chamber 2 is set to a low excess amount to suppress the rapid combustion of plastics with a high calorific value and the resulting rise in temperature in the room, and promote the thermal decomposition of the plastics. .

一次燃焼室2内の温度は600〜700°C程度が適当
である。この温度は、プラスチックの熱分解、木材、布
などの燃焼に必要な温度である。従って、前記温度域を
下まわれば助燃バーナ8を点火して温度を上げ、上まわ
れば電磁弁22を開き、給水ポンプ20を運転して、散
水孔21より水をスプレーするという自動操作により温
度制御を行なう。
The temperature within the primary combustion chamber 2 is suitably about 600 to 700°C. This temperature is required for the pyrolysis of plastics and the combustion of wood, cloth, etc. Therefore, if the temperature falls below the above range, the auxiliary combustion burner 8 is ignited to raise the temperature, and if the temperature rises above the temperature range, the solenoid valve 22 is opened, the water supply pump 20 is operated, and water is sprayed from the water sprinkling hole 21. control.

こうして一次燃焼室2内で粗大ごみ中の可燃物は部分燃
焼および熱分解する。
In this way, the combustibles in the bulky waste are partially combusted and thermally decomposed within the primary combustion chamber 2.

上記の一次燃焼室2内で発生した燃焼排ガス(未燃ガス
、未燃カーボンを含む)は連通路4を通ってつぎの二次
燃焼室3内に入り、ここで、空気吹込口6から吹込まれ
る燃焼用空気により高温を維持しながら完全燃焼させ、
前記一次燃焼室2におけるプラスチックの熱分解などで
発生した未燃ガス、未燃カーボンを完全燃焼させる。
The combustion exhaust gas (including unburned gas and unburned carbon) generated in the primary combustion chamber 2 passes through the communication passage 4 and enters the secondary combustion chamber 3, where it is blown from the air inlet 6. The injected combustion air ensures complete combustion while maintaining high temperature.
Unburned gas and unburned carbon generated by thermal decomposition of plastic in the primary combustion chamber 2 are completely combusted.

二次燃焼を完全に行なうためには二次燃焼室2内の温度
は800 ’C以上であることが好ましく、従ってこれ
を下まわれば温度センサー等により温度を検知してアフ
ターバーナSを自動点火して昇温する。
In order to perform secondary combustion completely, it is preferable that the temperature inside the secondary combustion chamber 2 is 800'C or higher. Therefore, if the temperature falls below this, the temperature is detected by a temperature sensor etc. and the afterburner S is automatically ignited. and raise the temperature.

二次燃焼室3で燃焼し終えた高温排ガスは排ガス通路1
5中のスプレー冷却装置16に流入し、ペンチエリ一部
17を通過する際に、給水ポンプ20よりの高圧水をノ
ズル18から噴射することにより、瞬間的に霧化、蒸発
するため効率的なガス冷却が行なわれる。ここで、高温
ガスは200〜250°Cに冷却される。
The high-temperature exhaust gas that has finished burning in the secondary combustion chamber 3 is transferred to the exhaust gas passage 1.
The high-pressure water from the water supply pump 20 is injected from the nozzle 18 when it flows into the spray cooling device 16 in 5 and passes through the pentieri part 17, and is instantaneously atomized and evaporated, resulting in efficient gas flow. Cooling takes place. Here, the hot gas is cooled to 200-250°C.

なお、上記ノズル18からの水噴射量は排ガスの温度を
温度センサなとで検知することにより自動制御される。
Note that the amount of water jetted from the nozzle 18 is automatically controlled by detecting the temperature of the exhaust gas with a temperature sensor or the like.

冷却された排ガスは排ガス通路15を通過中アルカリ粉
供給装置26から供給口25を経て投入されるアルカリ
粉と混合し、排ガス中の塩化水素がアルカリと反応して
アルカリ塩(中和物)となる。
While passing through the exhaust gas passage 15, the cooled exhaust gas mixes with the alkali powder introduced from the alkali powder supply device 26 through the supply port 25, and the hydrogen chloride in the exhaust gas reacts with the alkali to form an alkali salt (neutralized product). Become.

7一 ついで、バッグフィルタ27において排ガス中に含まれ
る粉塵がバッグに捕集される。
7, the dust contained in the exhaust gas is collected in the bag filter 27.

また、前記のように投入されたアルカリ粉の一部が未反
応のままバッグの表面に付着して付着層が形成され、こ
の付着層を排ガスが通過する際、未反応の塩化水素がこ
の付着層のアルカリと反応してアルカリ塩となってバッ
グに堆積捕集される。
Additionally, some of the alkali powder added as described above remains unreacted and adheres to the surface of the bag, forming an adhesion layer, and when the exhaust gas passes through this adhesion layer, unreacted hydrogen chloride is absorbed into this adhesion layer. It reacts with the alkali in the layer to form an alkali salt, which is deposited and collected in a bag.

こうして、バッグを通過して清浄化された排ガスは排風
機29を経てスタック30より大気に放出されるととも
に、アルカリ塩粉塵はバッグより脱塵されて下方に落下
し、適宜な手段で機外に排出される。
In this way, the purified exhaust gas passes through the bag and is discharged into the atmosphere from the stack 30 via the exhaust fan 29, while the alkali salt dust is removed from the bag, falls downward, and is removed from the machine by an appropriate means. be discharged.

また、前記の一次、二次燃焼時において家電などの中に
含まれる重金属が、気化(この気化ガスをヒユームと称
する)し、排ガスに含まれることになるが、この排ガス
中のヒユームは、冷却装置17で冷却されることにより
固形物(煤煙)となって排ガスとともに搬送されるが、
この煤煙はバッグフィルタ27を採用することによって
高回収率に捕集され、前記アルカリ塩、粉塵とともにバ
ラグフィルタ27の下部に落下除去される。
Also, during the primary and secondary combustion mentioned above, heavy metals contained in household appliances, etc. are vaporized (this vaporized gas is called fume) and are included in the exhaust gas. By being cooled in the device 17, it becomes a solid substance (soot) and is transported together with the exhaust gas,
This soot is collected with a high recovery rate by employing the bag filter 27, and is dropped to the lower part of the bag filter 27 and removed together with the alkali salt and dust.

前記収集されたものは重金属とアルカリ塩、粉塵とに分
けられ、前記は無害化処理され後者はそのまま埋立処分
される。
The collected materials are divided into heavy metals, alkali salts, and dust, and the former are treated to render them harmless, and the latter are directly disposed of in a landfill.

つぎに前記一次燃焼室2で所要時間可燃物置を燃焼した
後の金属などの不燃物である焼却残渣はシャッタ13を
あけ運搬手段5を駆動して一次燃焼室2外に取り出し、
この運搬手段5から取り除かれ、再び粗大ごみを載せ一
次燃焼室2に投入してつぎの焼却工程の繰返しとなる。
Next, the incineration residue, which is incombustible material such as metal, after burning the combustible material in the primary combustion chamber 2 for a required period of time, is taken out of the primary combustion chamber 2 by opening the shutter 13 and driving the conveying means 5.
The waste is removed from the transport means 5, and oversized waste is loaded again into the primary combustion chamber 2 to repeat the next incineration process.

なお、前記焼却残渣は金属類と不燃物灰分とに分けられ
金属は有価物として回収され、他は埋立処分されるので
ある。
Incidentally, the incineration residue is separated into metals and non-combustible ash, and the metals are recovered as valuable materials while the others are disposed of in a landfill.

第2図ないし第4図は搬送手段としてコンベヤとパレッ
トを用いたものである。
2 to 4 use a conveyor and a pallet as conveyance means.

この場合、コンベヤ35と2枚のパレット36.37を
用いるもので、コンベヤ35の炉外の部分の両側にブツ
シャ38.39を設けて、パレット36.37のコンベ
ヤ35上へ積み卸しを行なうようにする。
In this case, a conveyor 35 and two pallets 36.37 are used, and pushers 38.39 are provided on both sides of the portion of the conveyor 35 outside the furnace to load and unload the pallets 36.37 onto the conveyor 35. Make it.

すなわち、第2図のように停止している炉外のコンベヤ
35上に粗大ごみ31を載せたパレット36を載せ、シ
ャッタ13を開き、コンベヤ35によりパレット36を
一次燃焼室2内に投入し、コンベヤ35を止め、シャッ
タ13を閉じ焼却を始める。
That is, as shown in FIG. 2, a pallet 36 carrying bulky waste 31 is placed on the stopped conveyor 35 outside the furnace, the shutter 13 is opened, and the pallet 36 is thrown into the primary combustion chamber 2 by the conveyor 35. The conveyor 35 is stopped, the shutter 13 is closed, and incineration begins.

一方、つぎのパレット37は第3図、第4図(a)のよ
うに炉外のコンベヤ35の側方に待機し、この間につぎ
の粗大ごみの積込みを行なっている。
On the other hand, the next pallet 37 is waiting on the side of the conveyor 35 outside the furnace as shown in FIGS. 3 and 4(a), and during this time the next oversized waste is being loaded.

また、第4図(b)のように焼却炉1内で焼却し、焼却
が完了すると、第4図(C)のようにコンベヤ35によ
り炉外に引出し、ついで、ブツシャ39の作用によりパ
レット37をコンベヤ35上へ押出し、焼却残渣を載せ
たパレット36はパレット37により第4図(d)のよ
うにコンベヤ35の側方へ押し出す。
Further, as shown in FIG. 4(b), the incinerator 1 is incinerated, and when the incineration is completed, it is pulled out of the incinerator by a conveyor 35 as shown in FIG. 4(c). is pushed onto the conveyor 35, and the pallet 36 carrying the incineration residue is pushed out to the side of the conveyor 35 by the pallet 37 as shown in FIG. 4(d).

ついで、コンベヤ35によりパレット37を焼却炉1内
に送り込み、焼却を始める。
Next, the pallet 37 is sent into the incinerator 1 by the conveyor 35, and incineration is started.

また、コンベヤ35の側方へ押し出されたパレット36
上の焼却残渣は適宜に搬出し、つぎの粗大ごみの積み込
みを開始する。
Also, the pallet 36 pushed out to the side of the conveyor 35
The above incineration residue will be carried out as appropriate, and loading of the next bulky waste will begin.

上記の作業の繰返しによりパレット36.37を交互に
焼却炉内に送り込む。    □〔効果〕 この発明は上記のように粗大ごみを、破砕せずにそのま
ま一次燃焼室に投入して、この粗大ごみ中の可燃物を部
分焼却、熱分解するようにしたものであるから、粗大ご
みの破砕処理設備が不要となり、このような設備の設置
に伴う設備費やランニングコストが大巾に低減できる。
By repeating the above operations, pallets 36 and 37 are alternately fed into the incinerator. □ [Effects] As described above, this invention is designed to directly inject bulky garbage into the primary combustion chamber without crushing it, and partially incinerate and thermally decompose the combustibles in this bulky garbage. Bulky waste crushing equipment is not required, and the equipment costs and running costs associated with installing such equipment can be significantly reduced.

また、焼却炉で処理された残渣のうち、家電品などの金
属系のものの減容積効果が大である。すなわち、例えば
家電品中の木材、プラスチック類が燃焼して灰などの小
容積となり、金属類のみが残るので容積が減少し、焼却
残渣中の金属類の純度も高くなる。
Moreover, among the residues processed in the incinerator, the volume reduction effect of metal-based products such as home appliances is significant. That is, for example, wood and plastics in home appliances are burned and become a small volume of ash, and only metals remain, reducing the volume and increasing the purity of the metals in the incineration residue.

さらに集塵機としてバッグフィルタを用いた場合は重金
属の捕集効果を著しく高めることができる。従って、比
較的小容量の粗大ごみの処理用として安価に設置でき、
維持費も少なくて済むので−11= 特に小自治体向けに極めて有効である。
Furthermore, when a bag filter is used as a dust collector, the effect of collecting heavy metals can be significantly enhanced. Therefore, it can be installed at a low cost for processing relatively small volumes of bulky waste.
-11 = Extremely effective, especially for small municipalities, as maintenance costs are low.

【図面の簡単な説明】[Brief explanation of the drawing]

第1図はこの発明の実施例を示す一部縦断側面図、第2
図は他の実施例を示す一部切欠側面図、第3図は同上の
一部縦断正面図、第4図(a)、(ロ)、(C)、(d
)は同上の作用を示す平面図である。  Jl・・・・
・・焼却炉、2・・・・・・一次燃焼室、3・・・・・
・二次燃焼室、5・・・・・・運搬手段、16・・・・
・・スプレー冷却装置、26・・・・・・アルカリ粉供
給装置、27・・・・・・集塵機。
FIG. 1 is a partially longitudinal side view showing an embodiment of the present invention, and FIG.
The figure is a partially cutaway side view showing another embodiment, FIG. 3 is a partially longitudinal front view of the same as the above, and FIGS.
) is a plan view showing the same effect as above. Jl...
...Incinerator, 2...Primary combustion chamber, 3...
・Secondary combustion chamber, 5...Transportation means, 16...
... Spray cooling device, 26 ... Alkaline powder supply device, 27 ... Dust collector.

Claims (1)

【特許請求の範囲】[Claims] 未破砕の粗大ごみを収納可能な一次燃焼室と、この一次
燃焼室で発生した燃焼排ガスを再燃焼させる二次燃焼室
からなる焼却炉と、この焼却炉から、大気に通じる排ガ
ス通路に、高温排ガスに水を噴射するスプレー冷却装置
、アルカリ粉供給装置および集塵機を組込んだことを特
徴とする粗大ごみの焼却処理装置。
The incinerator consists of a primary combustion chamber that can store unshredded bulky waste, and a secondary combustion chamber that reburns the combustion exhaust gas generated in the primary combustion chamber. A bulky waste incineration processing device characterized by incorporating a spray cooling device that injects water into exhaust gas, an alkali powder supply device, and a dust collector.
JP10942987A 1987-04-30 1987-04-30 Incinerator for large-size refuse Pending JPS63273715A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP10942987A JPS63273715A (en) 1987-04-30 1987-04-30 Incinerator for large-size refuse

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP10942987A JPS63273715A (en) 1987-04-30 1987-04-30 Incinerator for large-size refuse

Publications (1)

Publication Number Publication Date
JPS63273715A true JPS63273715A (en) 1988-11-10

Family

ID=14510020

Family Applications (1)

Application Number Title Priority Date Filing Date
JP10942987A Pending JPS63273715A (en) 1987-04-30 1987-04-30 Incinerator for large-size refuse

Country Status (1)

Country Link
JP (1) JPS63273715A (en)

Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5017401A (en) * 1973-06-15 1975-02-24
JPS5912733A (en) * 1982-07-13 1984-01-23 Hitachi Zosen Corp Removal of harmful gas in drying system of organic waste material

Patent Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5017401A (en) * 1973-06-15 1975-02-24
JPS5912733A (en) * 1982-07-13 1984-01-23 Hitachi Zosen Corp Removal of harmful gas in drying system of organic waste material

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