JP3463897B2 - Home appliance waste treatment equipment - Google Patents

Home appliance waste treatment equipment

Info

Publication number
JP3463897B2
JP3463897B2 JP29121294A JP29121294A JP3463897B2 JP 3463897 B2 JP3463897 B2 JP 3463897B2 JP 29121294 A JP29121294 A JP 29121294A JP 29121294 A JP29121294 A JP 29121294A JP 3463897 B2 JP3463897 B2 JP 3463897B2
Authority
JP
Japan
Prior art keywords
waste
outlet
inlet
main body
gasification furnace
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.)
Expired - Fee Related
Application number
JP29121294A
Other languages
Japanese (ja)
Other versions
JPH08141538A (en
Inventor
政信 志垣
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.)
Takuma KK
Original Assignee
Takuma KK
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 Takuma KK filed Critical Takuma KK
Priority to JP29121294A priority Critical patent/JP3463897B2/en
Publication of JPH08141538A publication Critical patent/JPH08141538A/en
Application granted granted Critical
Publication of JP3463897B2 publication Critical patent/JP3463897B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

Links

Classifications

    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02EREDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
    • Y02E50/00Technologies for the production of fuel of non-fossil origin
    • Y02E50/30Fuel from waste, e.g. synthetic alcohol or diesel
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W30/00Technologies for solid waste management
    • Y02W30/50Reuse, recycling or recovery technologies
    • Y02W30/62Plastics recycling; Rubber recycling

Description

【発明の詳細な説明】Detailed Description of the Invention

【0001】[0001]

【産業上の利用分野】本発明は、都市ごみや産業廃棄物
等を焼却処理するごみ焼却炉に付設されるものであり、
ごみ焼却炉で発生した高温の排ガスを利用して家電製品
の廃棄物に含まれているプラスチック類を熱分解処理
し、残りの金属類やガラス等を回収するようにした家電
廃棄物処理装置に関する。
[Field of Industrial Application] The present invention is attached to a refuse incinerator for incinerating municipal waste, industrial waste, and the like.
Home appliance waste treatment device that uses high temperature exhaust gas generated in a refuse incinerator to pyrolyze plastics contained in the waste of home appliances and recovers the remaining metals and glass .

【0002】[0002]

【従来の技術】近年、家電製品や家具類等の粗大ごみの
増加が著しく、この粗大ごみは各自治体の粗大ごみ処理
施設で破砕・選別されて鉄,不燃物,可燃物,アルミニ
ウム等に分別され居り、不燃物又は可燃物(プラスチッ
ク含有量が多いもの)は埋立て処理されている。特に、
最近は大型家電製品の廃棄物が多く出回り、自治体とし
ても処理に困っているのが実状である。
2. Description of the Related Art In recent years, the amount of oversized garbage such as home electric appliances and furniture has increased remarkably. However, non-combustible materials or combustible materials (those with a high plastic content) are landfilled. In particular,
Recently, a large amount of waste from large-scale home appliances has been circulating, and the reality is that municipalities are having trouble processing it.

【0003】現在、各自治体での粗大ごみの処理は、回
転破砕機等の破砕機により粗大ごみを約150mm以下
に破砕処理し、鉄類をマグネットで回収すると共に、ア
ルミニウムをリニヤモータ方式で回収するようにしてい
る。ところが、何れも不燃物や可燃物を多く含み、品質
的に不充分で市況により引き取り手がなく、困っている
場合が多い。又、分別回収された可燃物をごみ焼却炉で
焼却すると、プラスチックを多く含んでいる為にごみ焼
却炉内でクリンカートラブルが発生し、様々な問題を生
じることになる。この可燃物は、そのまま埋立て処理す
ると、容積が大きい為に埋立て地の確保が困難になるう
え、腐敗による地下水の汚染や蠅等の発生源となって極
めて不衛生である。
Currently, in the treatment of bulky refuse in each municipality, the bulky refuse is crushed to about 150 mm or less by a crusher such as a rotary crusher, and irons are collected by a magnet and aluminum is collected by a linear motor method. I am trying. However, all of them contain a large amount of incombustibles and combustibles, and there are many cases in which the quality is insufficient and there are no collectors depending on the market conditions. In addition, if the combustible materials that have been separated and collected are incinerated in a refuse incinerator, a clinker trouble occurs in the refuse incinerator because it contains a large amount of plastic, which causes various problems. If this combustible material is landfilled as it is, it is difficult to secure a landfill site because of its large volume, and it is extremely unsanitary as a source of polluted groundwater and flies due to decay.

【0004】[0004]

【発明が解決しようとする課題】ところで、テレビ,冷
蔵庫等の家電製品の廃棄物を破砕分別方式で処理する場
合、破砕機の馬力が大きくて騒音防止対策にコストが掛
かるうえ、選別品の品質も悪くなると云う問題がある。
又、分別回収されたプラスチック等の可燃物も、結局焼
却が必要となり、一般ごみと混焼すると、クリンカート
ラブルが発生する等の問題がある。
By the way, when the waste of household electric appliances such as TVs and refrigerators is processed by the crushing and separating method, the horsepower of the crusher is large and the cost for noise prevention is high, and the quality of the sorted products is high. There is a problem that it gets worse.
In addition, combustible materials such as plastics that have been separated and collected eventually need to be incinerated, and when mixed with general waste, there is a problem that clinker troubles occur.

【0005】本発明は、このような問題点に鑑みて為さ
れたものであり、家電製品の廃棄物に含まれているプラ
スチック類をごみ焼却炉の高温の排ガスを利用してガス
化し、残りの金属類やガラス等を品質を低下させること
なく回収できるようにした家電廃棄物処理装置を提供す
るにある。
The present invention has been made in view of the above problems, and gasifies the plastics contained in the wastes of household electric appliances by using the high temperature exhaust gas of the refuse incinerator, and the remaining gas. An object of the present invention is to provide a household electrical appliance waste treatment device capable of recovering the metals, glass, etc. of the above without deteriorating the quality.

【0006】[0006]

【課題を解決するための手段】上記目的を達成する為
に、本発明の家電廃棄物処理装置は、家電製品の廃棄物
が通過できる入口及び出口を夫々有し、ごみ焼却炉から
プラスチックの熱分解温度以上の高温の排ガスを誘引し
て廃棄物に含まれているプラスチック類を熱分解すると
共に、熱分解により発生したガスをごみ焼却炉の燃焼室
へ戻すようにしたガス化炉本体と、廃棄物を入口側から
出口側へ移送する移送装置と、ガス化炉本体の入口側及
び出口側に夫々設けられ、入口及び出口を適宜に開閉す
る開閉装置とを具備して成るものである。
In order to achieve the above object, the household electric appliance waste treatment apparatus of the present invention has an inlet and an outlet through which the waste of household electric appliances can pass, and heats plastic from a refuse incinerator. A gasification furnace body that attracts high temperature exhaust gas above the decomposition temperature to thermally decompose the plastics contained in the waste and to return the gas generated by the thermal decomposition to the combustion chamber of the refuse incinerator. It comprises a transfer device for transferring the waste from the inlet side to the outlet side, and an opening / closing device which is provided on the inlet side and the outlet side of the gasification furnace main body and which appropriately opens and closes the inlet and the outlet.

【0007】又、開閉装置は、ガス化炉本体の入口内に
一定の間隔を開けて開閉自在に設けられた二重構造の入
口ダンパと、ガス化炉本体の出口内に一定の間隔を開け
て開閉自在に設けられた二重構造の出口ダンパと、各ダ
ンパを駆動する駆動機構と、廃棄物が入口及び出口を通
過する際に廃棄物の有無を検知する検知器と、検知器か
らの検出信号に基づいて各ダンパを自動制御する制御器
とから成り、ガス化炉本体の入口及び出口をシールしな
がら廃棄物が連続的に通過できるように構成しておくこ
とが好ましい。
Further, the switchgear is provided with a dual-structured inlet damper which is openably and closably provided in the inlet of the gasification furnace main body, and a constant gap is provided in the outlet of the gasification furnace main body. , A dual structure outlet damper that can be opened and closed, a drive mechanism that drives each damper, a detector that detects the presence or absence of waste when it passes through the inlet and outlet, and a detector It is preferable that it comprises a controller for automatically controlling each damper based on a detection signal, and is configured so that waste can pass continuously while sealing the inlet and outlet of the gasification furnace main body.

【0008】[0008]

【作用】テレビ,冷蔵庫等の家電製品の廃棄物は、移送
装置によりガス化炉本体の入口から炉内へ移送される。
このとき、入口は二重構造の入口ダンパにより開閉され
る為、入口から炉内への空気の進入が極力防止され、炉
内での燃焼等が防止される。
[Function] Wastes of home electric appliances such as televisions and refrigerators are transferred from the inlet of the gasification furnace body into the furnace by the transfer device.
At this time, since the inlet is opened and closed by the double-structured inlet damper, the invasion of air from the inlet into the furnace is prevented as much as possible, and combustion in the furnace is prevented.

【0009】炉内に移送された廃棄物は、ごみ焼却炉か
ら誘引された高温の排ガスによって廃棄物に含まれてい
るプラスチック類が熱分解されてガス化し、プラスチッ
ク類が完全に取り除かれた状態で出口側へ移送されて行
く。
The waste transferred to the furnace is in a state where the plastics contained in the waste are pyrolyzed and gasified by the high temperature exhaust gas attracted from the refuse incinerator, and the plastics are completely removed. Is transferred to the exit side.

【0010】一方、炉内で発生したガスは、ごみ焼却炉
の燃焼室へ導かれ、完全燃焼せしめられる。その結果、
塩化水素ガス等の不純物を含むガスをガス洗浄装置等で
後処理する必要もなく、処理コストの低減を図れる。
On the other hand, the gas generated in the furnace is introduced into the combustion chamber of the refuse incinerator and completely burned. as a result,
The gas containing impurities such as hydrogen chloride gas does not need to be post-treated by a gas cleaning device or the like, and the treatment cost can be reduced.

【0011】そして、プラスチック類が取り除かれた廃
棄物は、ガス化炉本体の出口から炉外へ移送される。こ
のとき、出口は二重構造の入口ダンパにより開閉される
為、入口から炉内への空気の進入が極力防止される。
Then, the waste from which the plastics have been removed is transferred from the outlet of the gasification furnace main body to the outside of the furnace. At this time, the outlet is opened and closed by the double-structured inlet damper, so that the inflow of air from the inlet into the furnace is prevented as much as possible.

【0012】このように、本考案の家電廃棄物処理装置
は、ガス化炉本体内で家電製品の廃棄物からプラスチッ
ク類を完全に取り除くようにしている為、残物(鉄,非
鉄金属,貴金属,ガラス等)の分別回収も容易になると
共に、分別回収した品物も品質の高いものとなる。又、
可燃物の事後処理も不必要となり、処理コストの低減を
図れる。
As described above, since the household electrical appliances waste treatment device of the present invention is designed to completely remove plastics from the household electrical appliances wastes in the gasification furnace main body, the residual materials (ferrous, non-ferrous metal, precious metal) , Glass, etc.) can be easily collected and the quality of the products collected by separation can be improved. or,
Post-processing of combustibles is also unnecessary and the processing cost can be reduced.

【0013】[0013]

【実施例】以下、本発明の実施例を図面に基づいて詳細
に説明する。図1は本発明の実施例に係る家電廃棄物処
理装置の概略縦断正面図であって、当該家電廃棄物処理
装置は、ガス化炉本体1と、移送装置2と、開閉装置3
とを具備して居り、都市ごみや産業廃棄物を焼却処理す
るごみ焼却炉に付設されている。
Embodiments of the present invention will now be described in detail with reference to the drawings. FIG. 1 is a schematic vertical sectional front view of a household electrical appliance waste processing apparatus according to an embodiment of the present invention. The household electrical appliance waste processing apparatus includes a gasification furnace body 1, a transfer device 2, and an opening / closing device 3.
It is equipped with a waste incinerator that incinerates municipal waste and industrial waste.

【0014】尚、ごみ焼却炉は、焼却炉本体4、ストー
カ5、ごみホッパ6及びごみ供給装置7等から成り、ご
みをごみホッパ6からストーカ5上に投入して該ストー
カ5により順次乾燥・焼却し、その焼却灰を灰排出口か
ら排出するように構成されている。又、焼却炉本体4の
燃焼室4a内で発生した高温の排ガスGは、ごみ焼却炉
に付設されたボイラ8で冷却され、電気集塵機9で煤塵
を除去された後、誘引通風機10を経て煙突11から排
出されるようになっている。
The waste incinerator is composed of an incinerator body 4, a stoker 5, a waste hopper 6, a waste feeder 7 and the like. The waste is put into the stoker 5 from the waste hopper 6 and dried sequentially by the stoker 5. It is configured to be incinerated and to discharge the incinerated ash from the ash outlet. The high-temperature exhaust gas G generated in the combustion chamber 4a of the incinerator body 4 is cooled by the boiler 8 attached to the refuse incinerator, the dust is removed by the electric dust collector 9, and then the hot air is passed through the induction draft fan 10. It is designed to be discharged from the chimney 11.

【0015】前記ガス化炉本体1は、テレビ,洗濯機等
の家電製品の廃棄物12に含まれているプラスチック類
をごみ焼却炉の高温の排ガスGにより熱分解してガス化
すると共に、熱分解により発生したガスG′をごみ焼却
炉の燃焼室4aへ戻すようにしたものである。即ち、ガ
ス化炉本体1は、耐火煉瓦等の耐火物や鋼板により断面
形状が略五角形の筒状に形成されて居り、両端部には家
電製品の廃棄物12が通過できる断面形状が矩形状の入
口1a及び出口1bが夫々形成されている。又、ガス化
炉本体1の底壁部分には、炉内1cへごみ焼却炉の排ガ
スGを導入する為の排ガス供給口1dが一定間隔毎に形
成されている。この各排ガス供給口1dは、排ガス供給
管13、ガスダンパ14、サイクロン等の脱塵装置15
及び誘引通風機16を介してボイラの入口1a側及び出
口1b側に夫々接続されて居り、ごみ焼却炉の高温排ガ
スGと低温排ガスGとを混合して所定温度(各種プラス
チックを熱分解できる程度の温度、例えば300℃〜4
00℃又は助燃により700℃)の排ガスGにし、この
排ガスGを炉内1cへ誘引できるように構成されてい
る。更に、ガス化炉本体1の天井壁部分には、ガス出口
1eが形成されて居り、このガス出口1eは、炉内1c
で発生したガスG′をごみ焼却炉の燃焼室4a内へ戻せ
るようにガス排出管17を介してごみ焼却炉の燃焼室4
a下部へ接続されている。
The gasification furnace main body 1 thermally decomposes and gasifies the plastics contained in the waste 12 of household electric appliances such as TVs and washing machines by the high temperature exhaust gas G of the refuse incinerator and heats them. The gas G'generated by the decomposition is returned to the combustion chamber 4a of the refuse incinerator. That is, the gasification furnace main body 1 is formed of a refractory such as refractory bricks or a steel plate into a tubular shape having a substantially pentagonal cross section, and both ends thereof have a rectangular cross section through which the waste 12 of home electric appliances can pass. Has an inlet 1a and an outlet 1b. Further, in the bottom wall portion of the gasification furnace main body 1, exhaust gas supply ports 1d for introducing the exhaust gas G of the refuse incinerator into the furnace interior 1c are formed at regular intervals. Each of the exhaust gas supply ports 1d is provided with an exhaust gas supply pipe 13, a gas damper 14, a dust removing device 15 such as a cyclone.
Also, they are connected to the inlet 1a side and the outlet 1b side of the boiler via the induction fan 16, respectively, and mix the high temperature exhaust gas G and the low temperature exhaust gas G of the refuse incinerator at a predetermined temperature (to the extent that various plastics can be thermally decomposed). Temperature, for example 300 ° C to 4
The exhaust gas G is heated to 00 ° C. or 700 ° C. by auxiliary combustion, and the exhaust gas G can be attracted to the furnace interior 1c. Further, a gas outlet 1e is formed in the ceiling wall portion of the gasification furnace main body 1, and this gas outlet 1e is in the furnace 1c.
The combustion chamber 4 of the refuse incinerator via the gas discharge pipe 17 so that the gas G'generated in step 1 can be returned to the combustion chamber 4a of the refuse incinerator.
a Connected to the bottom.

【0016】前記移送装置2は、廃棄物12をガス化炉
本体1の入口1a側から出口1b側へ移送するものであ
り、ガス化炉本体1内及び炉本体1の外方位置に、ロー
ラ2aを並列配置することにより構成されている。この
各ローラ2aは、ステンレス製内部ライニング厚肉鋼管
又は断熱層を挟んだ二重鋼管(外管の露点腐食を防ぐ)
により形成されて居り、チェーン伝動機構及びモータ等
から成る駆動装置(図示省略)によって、同一方向へ同
一速度で回転駆動されるようになっている。又、ガス化
炉本体1内に配置される各ローラ2aは、クリンカーの
付着や腐食を防止できるように後述する水冷式の冷却装
置18により冷却されている。即ち、冷却装置18は、
図3に示す如く、ローラ2aの側方位置に配置され、ロ
ーラ2aの一端部が回転自在に接続される入口ヘッダー
19と、ローラ2aの側方位置に配置され、ローラ2a
の他端部が回転自在に接続される出口ヘッダー20と、
両ヘッダー19,20に接続されて冷却水Wを循環する
冷却水管21と、冷却水管21に介設されたクーラー2
2及び循環ポンプ23とから成り、ローラ2aに冷却水
Wを供給してローラ2aを冷却し、温度の上昇した水を
クーラー22により冷却してローラ2aへ再循環するよ
うに構成されている。更に、ローラ2aは、一端部から
供給された冷却水Wを内部の略下半分に溜めてローラ2
aを冷却し、他端部からオーバーフローにより水と蒸気
Sに分離して排出できるように構成されている。尚、ロ
ーラ2aから排出された蒸気Sは、出口ヘッダー20か
ら外部へ排出されるようになっている。
The transfer device 2 transfers the waste 12 from the inlet 1a side of the gasification furnace main body 1 to the outlet 1b side, and the rollers are provided inside the gasification furnace main body 1 and outside the furnace main body 1. It is configured by arranging 2a in parallel. Each roller 2a is a stainless steel inner lining thick steel pipe or a double steel pipe sandwiching a heat insulating layer (prevents dew point corrosion of the outer pipe).
And is driven to rotate in the same direction at the same speed by a driving device (not shown) including a chain transmission mechanism, a motor, and the like. Further, each roller 2a arranged in the gasification furnace main body 1 is cooled by a water-cooling type cooling device 18 described later so as to prevent adhesion and corrosion of clinker. That is, the cooling device 18 is
As shown in FIG. 3, the inlet header 19 is disposed at the lateral position of the roller 2a, and one end of the roller 2a is rotatably connected, and the inlet header 19 is disposed at the lateral position of the roller 2a.
An outlet header 20 whose other end is rotatably connected,
A cooling water pipe 21 that is connected to both headers 19 and 20 and circulates the cooling water W, and a cooler 2 interposed in the cooling water pipe 21.
2 and a circulation pump 23, and is configured to supply cooling water W to the roller 2a to cool the roller 2a, cool water having an increased temperature by the cooler 22 and recirculate it to the roller 2a. Further, the roller 2a collects the cooling water W supplied from one end into the substantially lower half of the inside of the roller 2a.
It is configured so that a can be cooled and separated from the other end into water and steam S by overflow and discharged. The steam S discharged from the roller 2a is discharged from the outlet header 20 to the outside.

【0017】前記開閉装置3は、ガス化炉本体1の入口
1a側及び出口1b側に夫々設けられて居り、廃棄物1
2が入口1a及び出口1bを通過する際に空気の炉内1
cへの進入を極力防止すると共に、廃棄物12が連続的
に通過できるように、入口1a及び出口1bを適宜に開
閉するものである。本実施例では、開閉装置3は、ガス
化炉本体1の入口1a内に一定の間隔を開けて開閉自在
に設けられた二重構造の入口ダンパ24a,24bと、
ガス化炉本体1の出口1b内に一定の間隔を開けて開閉
自在に設けられた二重構造の出口ダンパ25a,25b
と、各ダンパ24a,24b,25a,25bを駆動す
るモータ,流体圧シリンダ等から成る駆動機構26と、
廃棄物12が入口1a及び出口1bを通過する際に廃棄
物12の有無を検知する複数の検知器27(光電管やマ
イクロ波検知器等)と、各検知器27からの検出信号に
基づいて各ダンパ24a,24b,25a,25bを自
動制御する制御器28とから成り、ガス化炉本体1の入
口1a及び出口1bを極力シールしながら廃棄物12が
連続的に通過できるように構成されている。即ち、入口
ダンパ24a,24bは、移送装置2により廃棄物12
がガス化炉本体1の入口1a近傍に移送されて来ると、
先ず外側の入口ダンパ24aが開放され、次に廃棄物1
2が入口1a内(外側の入口ダンパ24aと内側の入口
ダンパ24bとの間)へ移送されると、先に外側の入口
ダンパ24aが閉じ、その後内側の入口ダンパ24aが
開放され、そして廃棄物12が炉内1cへ移送される
と、内側の入口ダンパ24bが閉じるように夫々駆動制
御されている。一方、出口ダンパ25a,25bは、移
送装置2により廃棄物12が炉内1cを移送されて内側
の出口ダンパ25aの近傍に来ると、先ず内側の出口ダ
ンパ25aが開放され、次に廃棄物12が出口1b内
(内側の出口ダンパ25aと外側の出口ダンパ25bと
の間)へ移送されると、先に内側の出口ダンパ25aが
閉じ、その後外側の出口ダンパ25bが開放され、そし
て廃棄物12が炉外へ移送されると、外側の出口ダンパ
25bが閉じるように夫々駆動制御されている。
The switchgear 3 is provided on each of the inlet 1a side and the outlet 1b side of the gasification furnace main body 1, and the waste 1
2 inside the furnace when air passes through the inlet 1a and the outlet 1b
The entrance 1a and the exit 1b are appropriately opened and closed so that the waste 12 can pass continuously while preventing the entry into c as much as possible. In the present embodiment, the opening / closing device 3 includes dual-structured inlet dampers 24a and 24b that are provided in the inlet 1a of the gasification furnace main body 1 so as to be opened and closed at regular intervals.
The dual-structured outlet dampers 25a and 25b provided in the outlet 1b of the gasification furnace main body 1 so as to be openable and closable at regular intervals.
And a drive mechanism 26 including a motor for driving the dampers 24a, 24b, 25a, 25b, a fluid pressure cylinder, and the like,
A plurality of detectors 27 (photoelectric tubes, microwave detectors, etc.) that detect the presence or absence of the waste 12 when the waste 12 passes through the inlet 1a and the outlet 1b, and the respective detectors 27 based on the detection signals from the detectors 27. It comprises a controller 28 for automatically controlling the dampers 24a, 24b, 25a, 25b, and is configured so that the waste 12 can continuously pass while sealing the inlet 1a and the outlet 1b of the gasification furnace main body 1 as much as possible. . That is, the inlet dampers 24a and 24b are used for the waste 12 by the transfer device 2.
Is transferred to the vicinity of the inlet 1a of the gasification furnace main body 1,
First the outer inlet damper 24a is opened, then the waste 1
When 2 is transferred into the inlet 1a (between the outer inlet damper 24a and the inner inlet damper 24b), the outer inlet damper 24a is closed first, then the inner inlet damper 24a is opened, and the waste When 12 is transferred into the furnace 1c, the inner inlet damper 24b is controlled to be closed. On the other hand, in the outlet dampers 25a and 25b, when the waste 12 is transferred in the furnace 1c by the transfer device 2 and reaches the vicinity of the inner outlet damper 25a, the inner outlet damper 25a is first opened, and then the waste 12 is discharged. Is transferred into the outlet 1b (between the inner outlet damper 25a and the outer outlet damper 25b), the inner outlet damper 25a is first closed, then the outer outlet damper 25b is opened, and the waste 12 Are transferred to the outside of the furnace, the outer outlet dampers 25b are each controlled to be closed.

【0018】尚、図1に於いて、29はガス化炉本体1
の炉底に配設され、落下物を炉外へ排出する水封式フラ
イトコンベヤ、30はガス化炉本体1に配設され、プラ
スチックの種類に応じて炉内1cを高温にする必要があ
る場合に使用する助燃バーナであり、この助燃バーナ3
0は炉内1cの温度を温度検出器(図示省略)により検
出し、この温度検出器による検出温度に基づいて制御さ
れるように構成されている。又、31はガス化炉本体1
の出口1b後方位置に設けられ、廃棄物12の鉄,非鉄
金属,貴金属,ガラスを回収する選別場、32は回収し
た鉄を鉄塊にするプレス機である。
In FIG. 1, 29 is a gasification furnace main body 1
A water-sealed flight conveyor, 30 that is disposed on the bottom of the furnace and discharges fallen substances to the outside of the furnace, is disposed on the gasification furnace main body 1, and it is necessary to raise the temperature inside the furnace 1c according to the type of plastic. This is an auxiliary combustion burner used when
0 is configured to detect the temperature of the inside of the furnace 1c by a temperature detector (not shown) and control based on the temperature detected by this temperature detector. Further, 31 is the gasification furnace main body 1
A sorting station provided at a position behind the exit 1b for collecting iron, non-ferrous metal, noble metal, and glass of the waste 12, and a pressing machine 32 for converting the collected iron into an iron ingot.

【0019】次に、前記家電廃棄物処理装置の作用につ
いて説明する。テレビ,冷蔵庫等の家電製品の廃棄物1
2が移送装置2によりガス化炉本体1の入口1a近傍に
移送されて来ると、外側の入口ダンパ24aが開放され
る。これにより、廃棄物12は、入口1a内(外側の入
口ダンパ24aと内側の入口ダンパ24bとの間)へ移
送される。
Next, the operation of the household appliances waste treatment device will be described. Waste from home appliances such as TVs and refrigerators 1
When 2 is transferred to the vicinity of the inlet 1a of the gasification furnace main body 1 by the transfer device 2, the outer inlet damper 24a is opened. As a result, the waste 12 is transferred into the inlet 1a (between the outer inlet damper 24a and the inner inlet damper 24b).

【0020】廃棄物12が入口1a内に移送されると、
先に外側の入口ダンパ24aが閉じ、その後内側の入口
ダンパ24bが開放される。これにより、廃棄物12
は、炉内1cへ移送されて行く。このとき、外側の入口
ダンパ24aを閉じてから内側の入口ダンパ24bを開
放するようにしている為、入口1aから炉内1cへの空
気の進入が極力防止される。
When the waste 12 is transferred into the inlet 1a,
The outer inlet damper 24a is closed first, and then the inner inlet damper 24b is opened. As a result, waste 12
Are transferred to the furnace 1c. At this time, since the outer inlet damper 24a is closed and the inner inlet damper 24b is opened, air is prevented from entering from the inlet 1a into the furnace 1c as much as possible.

【0021】廃棄物12が炉内1cへ移送されると、内
側の入口ダンパ24bが閉じ、廃棄物12は移送装置2
により炉内1cを入口1a側から出口1b側へ移送され
て行く。このとき、炉内1cにはごみ焼却炉から誘引さ
れた所定温度(各種プラスチックを熱分解できる程度の
温度、例えば300℃〜400℃又は助燃により700
℃)の排ガスGが排ガス供給口1dから供給されている
為、廃棄物12に含まれているプラスチック類が熱分解
されてガス化する。その結果、廃棄物12はプラスチッ
ク類が完全に取り除かれた状態で出口1b側へ移送され
て行く。尚、図4はプラスチックの種類による熱分解曲
線を示し、大抵のプラスチックは650℃で略完全ガス
化している。従って、前記排ガスGの温度でプラスチッ
ク類を略完全にガス化することができる。
When the waste 12 is transferred to the furnace 1c, the inner inlet damper 24b is closed, and the waste 12 is transferred to the transfer device 2.
Thus, the inside of the furnace 1c is transferred from the inlet 1a side to the outlet 1b side. At this time, a predetermined temperature (a temperature at which various plastics can be thermally decomposed, for example, 300 ° C. to 400 ° C.) or 700
Since the exhaust gas G of (° C.) is supplied from the exhaust gas supply port 1d, the plastics contained in the waste 12 are thermally decomposed and gasified. As a result, the waste 12 is transferred to the outlet 1b side with the plastics completely removed. Incidentally, FIG. 4 shows a thermal decomposition curve depending on the type of plastic, and most plastics are almost completely gasified at 650 ° C. Therefore, plastics can be almost completely gasified at the temperature of the exhaust gas G.

【0022】一方、炉内1cで発生したガスG′は、ガ
ス出口1eから排出されてごみ焼却炉の燃焼室4a内へ
導かれ、完全燃焼せしめられる。その結果、塩化水素ガ
ス等の不純物を含むガスG′をガス洗浄装置等で後処理
する必要もなく、処理コストの低減を図れる。
On the other hand, the gas G'generated in the furnace 1c is discharged from the gas outlet 1e, introduced into the combustion chamber 4a of the refuse incinerator, and completely burned. As a result, the gas G ′ containing impurities such as hydrogen chloride gas does not need to be post-treated by a gas cleaning device or the like, and the treatment cost can be reduced.

【0023】尚、ごみ焼却炉の燃焼室4aの下部は炉内
ガスの浮力により−10〜−15mmH2Oになってい
る為、炉内1cで発生したガスG′は自動的に燃焼室4
aへ吸引されて行く。又、炉内1cに配置されている各
ローラ2aは、冷却装置18により冷却されている為、
クリンカーの付着等が防止される。更に、炉底に落下し
た落下物(プラスチックの熱分解により生じた残滓等)
は冷却された後、水封式フライトコンベヤにより外部へ
排出されて回収される。
[0023] Incidentally, since the lower portion of the combustion chamber 4a of incinerator has become -10 to-15 mmH 2 O by the buoyancy of the furnace gas, gas G generated in the furnace 1c 'is automatically combustion chamber 4
It is sucked to a. Further, since each roller 2a arranged in the furnace 1c is cooled by the cooling device 18,
Adhesion of clinker is prevented. Furthermore, fallen objects that have fallen to the bottom of the furnace (residues generated by the thermal decomposition of plastic)
After being cooled, it is discharged to the outside by a water-sealed flight conveyor and collected.

【0024】そして、プラスチック類が取り除かれた廃
棄物12が炉内1cを移送されて内側の出口ダンパ25
aの近傍に来ると、内側の出口ダンパ25aが開放され
る。これにより、廃棄物12は、出口1b内(内側の出
口ダンパ25aと外側の出口ダンパ25bとの間)へ移
送される。
Then, the waste 12 from which the plastics have been removed is transferred through the furnace 1c and the outlet damper 25 inside
When it comes near a, the inner outlet damper 25a is opened. Thereby, the waste 12 is transferred into the outlet 1b (between the inner outlet damper 25a and the outer outlet damper 25b).

【0025】廃棄物12が出口1b内に移送されると、
先に内側の出口ダンパ25aが閉じ、その後外側の出口
ダンパ25bが開放される。これにより、廃棄物12
は、炉外へ移送される。このとき、内側の出口ダンパ2
5aを閉じてから外側の出口ダンパ25bを開放するよ
うにしている為、出口1bから炉内1cへの空気の進入
が極力防止される。
When the waste 12 is transferred into the outlet 1b,
The inner outlet damper 25a is closed first, and then the outer outlet damper 25b is opened. As a result, waste 12
Are transferred outside the furnace. At this time, the inner outlet damper 2
Since the outer outlet damper 25b is opened after closing 5a, air is prevented from entering the furnace 1c through the outlet 1b as much as possible.

【0026】ガス化炉本体1の出口1bから選別場31
に移送された廃棄物12は、ここで機械的若しくは人手
により分解されて鉄,非鉄金属,貴金属,ガラス等に分
別回収され、鉄はプレス機32によって三方絞めされて
鉄塊として回収される。このとき、プラスチック類は既
に取り除かれている為、残物(鉄,非鉄金属,貴金属,
ガラス等)の回収も容易になると共に、分別回収した品
物も品質の高いものとなる。尚、ガラスを含むテレビ等
の廃棄物12は、ガス化の温度を少し低くすることによ
りガラスも回収することができる。
From the outlet 1b of the gasifier main body 1 to the sorting station 31
The waste 12 transferred to (1) is mechanically or manually decomposed and separated into iron, non-ferrous metal, noble metal, glass, etc., and the iron is squeezed on three sides by the press machine 32 to be collected as an iron ingot. At this time, since the plastics have already been removed, the remains (ferrous, non-ferrous metal, precious metal,
The collection of glass etc. will be easy and the quality of the sorted and collected products will be high. Incidentally, the waste 12 such as a television including glass can also be recovered by slightly lowering the gasification temperature.

【0027】上記実施例に於いては、開閉装置3に二重
ダンパ構造のものを使用したが、他の実施例に於いて
は、開閉装置3に二重シャッター構造のものを使用する
ようにしても良い。
In the above embodiment, the opening / closing device 3 has the double damper structure, but in other embodiments, the opening / closing device 3 has the double shutter structure. May be.

【0028】上記実施例に於いては、各ローラ2aを水
冷式としたが、他の実施例に於いては、各ローラ2aを
空冷式としても良い。
In the above embodiment, each roller 2a is water-cooled, but in other embodiments, each roller 2a may be air-cooled.

【0029】上記実施例に於いては、各ローラ2aをス
テンレス製厚肉鋼管により形成したが、他の実施例に於
いては、各ローラ2aをセラミック材等の耐熱・耐火材
で形成するようにしても良い。
In the above embodiment, each roller 2a is made of a thick stainless steel tube, but in other embodiments, each roller 2a is made of a heat-resistant / refractory material such as a ceramic material. You can

【0030】[0030]

【発明の効果】上述の通り、本発明の家電廃棄物処理装
置は、ガス化炉本体内にごみ焼却炉の高温の排ガスを導
き、炉内で家電製品の廃棄物に含まれているプラスチッ
ク類を前記排ガスにより熱分解してガス化し、廃棄物を
プラスチック類を取り除いた状態で取り出せるようにし
ている。その結果、可燃物の事後処理も不要となって処
理コストの低減を図れると共に、鉄,非鉄金属,貴金
属,ガラス等の回収も容易になり、回収された金属類等
も品質の高いものとなる。又、ごみ焼却炉の廃熱を利用
すると共に、ガス化炉本体内で発生した有害ガスを焼却
炉内に戻して完全燃焼させるようにしている為、ガスの
後処理装置も不要となり、より一層処理コストの低減を
図れる。更に、ガス化炉本体の入口側及び出口側に設け
る開閉装置を二重ダンパ構造とし、炉内に空気が進入す
るのを極力防止するようにしている為、炉内での燃焼や
爆発等を防止でき、装置を安全に運転することができ
る。然も、廃棄物を連続してガス化炉本体内を通過させ
ることができ、連続運転が可能となる。
As described above, the apparatus for treating household electric appliances according to the present invention introduces high-temperature exhaust gas from the refuse incinerator into the main body of the gasification furnace, and the plastics contained in the waste of household electric appliances in the furnace. Is thermally decomposed into gas by the exhaust gas, and the waste can be taken out in a state where plastics are removed. As a result, post-treatment of combustibles is not required, and the treatment cost can be reduced, and the ferrous, non-ferrous metals, precious metals, glass, etc. can be easily recovered, and the recovered metals, etc. will be of high quality. . Moreover, since the waste heat of the waste incinerator is used and the harmful gas generated in the gasification furnace main body is returned to the incinerator and completely burned, a gas post-treatment device is not required, and further The processing cost can be reduced. Furthermore, the switchgear provided on the inlet side and outlet side of the gasification furnace main body has a double damper structure to prevent air from entering the furnace as much as possible, so that combustion and explosion in the furnace are prevented. It can be prevented and the device can be operated safely. However, the waste can be continuously passed through the inside of the gasification furnace main body, which enables continuous operation.

【図面の簡単な説明】[Brief description of drawings]

【図1】本発明の実施例に係る家電廃棄物処理装置をご
み焼却炉へ付設した状態の概略縦断正面図である。
FIG. 1 is a schematic vertical cross-sectional front view showing a state in which a household appliances waste treatment device according to an embodiment of the present invention is attached to a refuse incinerator.

【図2】家電廃棄物処理装置の概略横断面図である。FIG. 2 is a schematic cross-sectional view of a household electrical appliance waste processing device.

【図3】家電廃棄物処理装置の概略縦断側面図である。FIG. 3 is a schematic vertical cross-sectional side view of the household electrical appliances waste treatment device.

【図4】各種プラスチックの温度による分解度を示すグ
ラフである。
FIG. 4 is a graph showing the degree of decomposition of various plastics with temperature.

【符号の説明】[Explanation of symbols]

1はガス化炉本体、1aは入口、1bは出口、2は移送
装置、3は開閉装置、4aは燃焼室、12は廃棄物、2
4a,24bは入口ダンパ、25a,25bは出口ダン
パ、26は駆動機構、27は検知器、28は制御器。
1 is a gasification furnace main body, 1a is an inlet, 1b is an outlet, 2 is a transfer device, 3 is an opening / closing device, 4a is a combustion chamber, 12 is waste, 2
4a and 24b are inlet dampers, 25a and 25b are outlet dampers, 26 is a drive mechanism, 27 is a detector, and 28 is a controller.

───────────────────────────────────────────────────── フロントページの続き (58)調査した分野(Int.Cl.7,DB名) B09B 3/00 B29B 17/00 F23G 5/027 ZAB ─────────────────────────────────────────────────── ─── Continuation of front page (58) Fields surveyed (Int.Cl. 7 , DB name) B09B 3/00 B29B 17/00 F23G 5/027 ZAB

Claims (2)

(57)【特許請求の範囲】(57) [Claims] 【請求項1】 家電製品の廃棄物(12)が通過できる
入口(1a)及び出口(1b)を夫々有し、ごみ焼却炉
からプラスチックの熱分解温度以上の高温の排ガス
(G)を誘引して廃棄物(12)に含まれているプラス
チック類を熱分解すると共に、熱分解により発生したガ
ス(G′)をごみ焼却却炉の燃焼室(4a)へ戻すよう
にしたガス化炉本体(1)と、廃棄物(12)を入口
(1a)側から出口(1b)側へ移送する移送装置
(2)と、ガス化炉本体(1)の入口(1a)側及び出
口(1b)側に夫々設けられ、入口(1a)及び出口
(1b)を適宜に開閉する開閉装置(3)とを具備した
ことを特徴とする家電廃棄物処理装置。
1. An exhaust gas (G) having a temperature higher than the thermal decomposition temperature of plastics is attracted from a refuse incinerator, each having an inlet (1a) and an outlet (1b) through which a waste product (12) of home electric appliances can pass. The main body of the gasification furnace, which is configured to thermally decompose the plastics contained in the waste (12) and to return the gas (G ') generated by the thermal decomposition to the combustion chamber (4a) of the refuse incinerator (4a). 1), a transfer device (2) for transferring the waste (12) from the inlet (1a) side to the outlet (1b) side, and the inlet (1a) side and the outlet (1b) side of the gasification furnace main body (1). And a switchgear (3) for opening and closing the entrance (1a) and the exit (1b) as needed.
【請求項2】 開閉装置(3)が、ガス化炉本体(1)
の入口(1a)内に一定の間隔を開けて開閉自在に設け
られた二重構造の入口ダンパ(24a),(24b)
と、ガス化炉本体(1)の出口(1b)内に一定の間隔
を開けて開閉自在に設けられた二重構造の出口ダンパ
(25a),(25b)と、各ダンパ(24a),(2
4b),(25a),(25b)を駆動する駆動機構
(26)と、廃棄物(12)が入口(1a)及び出口
(1b)を通過する際に廃棄物(12)の有無を検知す
る検知器(27)と、検知器(27)からの検出信号に
基づいて各ダンパ(24a),(24b),(25
a),(25b)を自動制御する制御器(28)とから
成り、ガス化炉本体(1)の入口(1a)及び出口(1
b)をシールしながら廃棄物(12)が連続的に通過で
きるように構成したことを特徴とする請求項1に記載の
家電廃棄物処理装置。
2. The switchgear (3) comprises a gasification furnace main body (1).
Dual-structured inlet dampers (24a), (24b) that are openable and closable at regular intervals inside the inlet (1a) of the
And dual-structured outlet dampers (25a), (25b) provided in the outlet (1b) of the gasification furnace main body (1) at regular intervals so as to be opened and closed, and the dampers (24a), ( Two
4b), (25a), a drive mechanism (26) for driving (25b) and the presence or absence of waste (12) when the waste (12) passes through the inlet (1a) and the outlet (1b). A detector (27) and each damper (24a), (24b), (25) based on the detection signal from the detector (27).
a) and (25b) are automatically controlled by a controller (28), and an inlet (1a) and an outlet (1) of the gasifier main body (1) are provided.
The household appliance waste treatment device according to claim 1, wherein the waste (12) is configured to be able to pass continuously while sealing b).
JP29121294A 1994-11-25 1994-11-25 Home appliance waste treatment equipment Expired - Fee Related JP3463897B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP29121294A JP3463897B2 (en) 1994-11-25 1994-11-25 Home appliance waste treatment equipment

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP29121294A JP3463897B2 (en) 1994-11-25 1994-11-25 Home appliance waste treatment equipment

Publications (2)

Publication Number Publication Date
JPH08141538A JPH08141538A (en) 1996-06-04
JP3463897B2 true JP3463897B2 (en) 2003-11-05

Family

ID=17765921

Family Applications (1)

Application Number Title Priority Date Filing Date
JP29121294A Expired - Fee Related JP3463897B2 (en) 1994-11-25 1994-11-25 Home appliance waste treatment equipment

Country Status (1)

Country Link
JP (1) JP3463897B2 (en)

Families Citing this family (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
ME02387B (en) * 2011-05-19 2016-09-20 Carrera Varela Jose Antonio Process and apparatus for the production of a solid fuel from combustible wastes

Also Published As

Publication number Publication date
JPH08141538A (en) 1996-06-04

Similar Documents

Publication Publication Date Title
JP2957627B2 (en) Municipal waste incineration melting equipment
WO2016021785A1 (en) Multi-layer high-temperature pyrolysis incineration apparatus
US6024931A (en) Process for removing mercury from mercury contaminated materials
KR101483751B1 (en) High-temperature pyrolysis incineration apparatus
JP3266591B2 (en) Intermittent flow type pyrolysis equipment
JP3463897B2 (en) Home appliance waste treatment equipment
IE904486A1 (en) Apparatus for hazardous waste to form non-hazardous aggregate
AU743972B2 (en) Pyrolytic oven with dust extraction of the gas stream output resulting from pyrolysis
CN112044921A (en) Domestic waste burns slag processing system
CN2469328Y (en) Plasma incineration furnace for special garbage
JP4374773B2 (en) Waste pyrolysis kiln char removal device
JP3145446B2 (en) Dioxin decomposition equipment
CN215723234U (en) Movable small-sized domestic garbage incinerator
CN212284316U (en) Waste oil barrel recycling and treating system
JPH10122536A (en) Emission device of thermal decomposition reactor
CN218033146U (en) Automatic feeding device of rotary kiln incinerator
JPH1085703A (en) Thermal decomposition reaction apparatus
CN212362027U (en) Domestic waste pyrolysis gasification equipment
JP3810149B2 (en) Operation method of pyrolysis reactor
JP3747537B2 (en) Pyrolysis gas extraction method and apparatus for waste pyrolysis gasifier
TW318880B (en) A connecting type turning furnace
KR20230035537A (en) Movable and continuous all in one incineration system
JPH10332125A (en) Wastes treatment equipment
JP3891754B2 (en) Waste incineration ash melting system using fine combustion of waste plastics
JPH1061928A (en) Waste treatment device

Legal Events

Date Code Title Description
R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20070822

Year of fee payment: 4

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20080822

Year of fee payment: 5

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20080822

Year of fee payment: 5

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20090822

Year of fee payment: 6

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20100822

Year of fee payment: 7

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20100822

Year of fee payment: 7

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20110822

Year of fee payment: 8

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20120822

Year of fee payment: 9

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20130822

Year of fee payment: 10

R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250

LAPS Cancellation because of no payment of annual fees