JPH1177013A - Nonpolluting regeneration treatment plant for waste - Google Patents

Nonpolluting regeneration treatment plant for waste

Info

Publication number
JPH1177013A
JPH1177013A JP24098797A JP24098797A JPH1177013A JP H1177013 A JPH1177013 A JP H1177013A JP 24098797 A JP24098797 A JP 24098797A JP 24098797 A JP24098797 A JP 24098797A JP H1177013 A JPH1177013 A JP H1177013A
Authority
JP
Japan
Prior art keywords
waste
crushed
crushing
supplied
plastic
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.)
Granted
Application number
JP24098797A
Other languages
Japanese (ja)
Other versions
JP3278384B2 (en
Inventor
Yoshikazu Kobayashi
由和 小林
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.)
Miike Tekkosho KK
Original Assignee
Miike Tekkosho 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 Miike Tekkosho KK filed Critical Miike Tekkosho KK
Priority to JP24098797A priority Critical patent/JP3278384B2/en
Publication of JPH1177013A publication Critical patent/JPH1177013A/en
Application granted granted Critical
Publication of JP3278384B2 publication Critical patent/JP3278384B2/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
    • Y02E50/10Biofuels, e.g. bio-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
    • 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
    • Y02W30/78Recycling of wood or furniture waste

Abstract

PROBLEM TO BE SOLVED: To produce pollution-free fuel and charcoal having many uses other than fuel from solid matter by solidifying combustible waste such as disposable plastics discharged from a place of business and a home, wood chips and waste paper without environmental pollution. SOLUTION: This nonpolluting regeneration treatment plant of waste is constituted of a crushing device 10 for crushing organic substance-based waste containing various kinds of plastics, separators 20, 25 for separating valuables from crushed material W1, a solidification device 80 and a carbonization device 90 for dry-distilling solid matter and carbonizing it. Further, an auxiliary burner or a scrubber pouring an alkaline aqueous solution is equipped in the flue of the carbonization device 90. In the carbonization device 90, after the valuables are removed, plastics and crushed trash other than plastics are supplied so that the former becomes 70-30 wt.% and the latter becomes 30-70 wt.%. The mixture is compressed while being agitated and mixed by feeding through a screw body and heated at 120-300 deg.C, kneaded and made to a fluidized state. Rodlike and granular solid matter is formed b extruding an intermediate product of the fluidized state through a perforated plate and molding it.

Description

【発明の詳細な説明】DETAILED DESCRIPTION OF THE INVENTION

【0001】[0001]

【発明の属する技術分野】この発明は、事業所やオフィ
ス、家庭等から廃棄される各種のプラスチックや木屑や
紙屑等の屑、粗大ごみ等の有機質系廃棄物を破砕及び粉
砕し、混合し、加熱流動化し、固形化してから炭化して
炭を得る廃棄物の無公害化再生処理プラントに関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention crushes and pulverizes and mixes various kinds of plastics, wood waste, paper waste, and other organic waste such as bulky waste, which are discarded from business establishments, offices, and homes. The present invention relates to a non-polluting waste-recycling plant that heats fluidized, solidifies, and then carbonizes to obtain coal.

【0002】[0002]

【従来の技術】従来より、一般の可燃廃棄物は、大部分
多くの自治体の焼却場で焼却処分されていたが、燃焼温
度の管理が不十分な焼却場では猛毒のダイオキシンが発
生し、今日では安易に焼却処分できない状況である。こ
のように、近年廃棄物を取り巻く環境も変わり、また、
資源再利用の観点からも、1995年6月には「容器包
装に係わる分別収集及び再商品化の促進等に関する法律
(容器包装リサイクル法)」の制定、公布に伴い、従来
安定型とされていた廃棄物も管理型に変更されて安易に
埋立ができなくなって来ており、廃棄プラスチックも分
別収集されて再利用し易くなっており、より広くプラス
チックを含む廃棄物のリサイクル法が研究されるように
成ってきた。
2. Description of the Related Art Conventionally, most combustible wastes have been incinerated in most municipal incineration plants. However, in incineration plants where combustion temperature is not sufficiently controlled, highly toxic dioxins are generated. Then it is not easy to incinerate it. In this way, the environment surrounding waste has changed in recent years,
From the viewpoint of resource reuse, in June 1995, the Law on the Promotion of Separated Collection and Recycling of Containers and Packaging (Container and Packaging Recycling Law) was enacted and promulgated, and it was previously considered to be a stable type. Waste has also been changed to a managed type and it is becoming impossible to landfill easily, waste plastic is collected separately and it is easy to reuse it, and a wider recycling method of waste containing plastic is studied It has become like that.

【0003】[0003]

【発明が解決しようとする課題】そのようなプラスチッ
クを含む廃棄物のリサイクルとしては、本願出願人も既
に幾つか提案したように固形燃料の原料として活用する
ことが多かった。このプラスチックからの再生固形燃料
は、染色や晒しの工場やクリーニング所、銭湯やヘルス
センター等のボイラーの燃料として、また石灰やセメン
ト工場、製鉄所等の燃料として広く利用されて好評を博
している。しかし、広く利用されている塩化ビニル等の
塩化物は、必ず廃棄プラスチックに含まれており、従っ
て再生固形燃料も含まれている為に燃焼いかんではダイ
オキシンが発生する。
As the recycling of such waste containing plastic, the applicant of the present invention has often utilized it as a raw material for solid fuel, as already proposed by the present applicant. Recycled solid fuel from plastic is widely used as a fuel for boilers such as dyeing and bleaching factories and cleaning plants, public baths and health centers, and as a fuel for lime, cement factories and steelworks. I have. However, chlorides such as vinyl chloride, which are widely used, are always contained in waste plastics, and therefore contain regenerated solid fuel, so that dioxin is generated by combustion.

【0004】本発明は、上記に鑑み案出されたものであ
って、事業所や家庭等から出る廃棄プラスチックや木屑
や紙屑等の可燃廃棄物を無公害で固形化して、固形物か
ら無公害で燃料やそれ以外にも多くの用途の有る炭を得
る廃棄物の無公害化再生処理プラントを提供することを
目的としている。
The present invention has been devised in view of the above, and is intended to solidify combustible wastes such as waste plastics, wood chips, paper wastes and the like from offices and homes without polluting them, and to make the solids non-polluting. It is an object of the present invention to provide a plant for detoxifying and regenerating waste, which obtains fuel and coal having many other uses.

【0005】[0005]

【課題を解決するための手段】上記目的を達成する本発
明の請求項1記載の廃棄物の無公害化再生処理プラント
は、各種のプラスチックを含む有機質系廃棄物を破砕す
る破砕装置と、破砕された破砕物から有価物を選別する
選別装置と、有価物の除去後の破砕物の内プラスチック
とそれ以外の破砕物を前者が70〜30重量%、後者が
30〜70重量%となるように供給され、螺旋体によっ
て送りをかけて撹拌混合しながら圧縮して120〜30
0℃に加熱し、練り合わせて流動可能状態にし、この流
動状態の中間生成物から多孔板を通して押し出し成形し
て棒状や粒状の固形物を形成する固形化装置と、固形物
を乾留して炭化する炭化装置とから構成されており、上
記炭化装置は、排気ガスの煙道に補助バーナ又はアルカ
リ性水溶液を入れたスクラバーを備えていることを特徴
としている。
According to a first aspect of the present invention, there is provided a plant for detoxifying and regenerating waste, which comprises a crushing apparatus for crushing organic waste containing various plastics, A sorting device for sorting valuable materials from the crushed materials, and a plastic and other crushed materials of the crushed materials after the removal of the valuable materials in which the former is 70 to 30% by weight and the latter is 30 to 70% by weight. And compressed while stirring and mixing by feeding by means of a spiral.
The mixture is heated to 0 ° C., kneaded into a flowable state, a solidifying device for extruding the intermediate product in the fluidized state through a perforated plate to form a rod-shaped or granular solid, and carbonizing the solid by carbonization. And a carbonizing device, wherein the carbonizing device includes an auxiliary burner or a scrubber containing an alkaline aqueous solution in a flue of exhaust gas.

【0006】従って、上記の構成を有した請求項1記載
の廃棄物の無公害化再生処理プラントでは、事業所や家
庭から廃棄されるPP(ポリプロピレン)やPE(ポリ
エチレン)、PS(ポリスチレン)、PET(ポリエチ
レンテレフタレート)、PA(ポリアミド)、ABS
(アクリロニトリルブタジェンスチレン)、PVC(ポ
リ塩化ビニル)等の各種のプラスチックを含む有機質系
廃棄物は、破砕装置で破片に破砕されて後工程での金属
等の有価物の選別作業が楽に出来るようになる。有価物
の除去後の破砕物は、固形化装置において螺旋体によっ
て送りがかけられて70〜30重量%のプラスチックと
30〜70重量%のプラスチック以外の破砕物が撹拌混
合されながら圧縮され、圧縮熱で120〜300℃に加
熱される。プラスチックは、この範囲の温度で塩素分を
含んでいてもダイオキシンを発生させずに溶融し、練り
合わされて流動可能状態のバインダーとしての働きをし
てほかの破砕物を結合する。従って、多孔板を通して押
し出し成形されると棒状や粒状の固形物が生成され、こ
れらは、炭化装置で乾留され有機質は炭化されて用途の
多い炭に転換される。この炭化の乾留過程で発生するダ
イオキシンを含んだガスは、煙道に設けられた補助バー
ナによって摂氏800度以上で完全燃焼されて無害化さ
れるか、又はアルカリ性水溶液を入れたスクラバーでダ
イオキシンが吸収される。かくして、プラスチックを含
んだ廃棄物から無公害で燃料やそれ以外にも多くの用途
の有る炭を得ることが出来る。
Therefore, in the waste reclaiming and reprocessing plant according to claim 1 having the above structure, PP (polypropylene), PE (polyethylene), PS (polystyrene), PET (polyethylene terephthalate), PA (polyamide), ABS
Organic wastes including various plastics such as (acrylonitrile butadiene styrene) and PVC (polyvinyl chloride) are crushed into fragments by a crushing device so that it is easy to sort valuable materials such as metals in the subsequent process. become. The crushed material after the removal of the valuables is fed by a spiral in a solidifying device, and 70 to 30% by weight of the plastic and 30 to 70% by weight of the crushed material other than the plastic are compressed while being stirred and mixed. At 120 to 300 ° C. The plastic melts without generating dioxin even if it contains chlorine at a temperature in this range, and is kneaded to act as a binder in a flowable state to bind other crushed materials. Therefore, when extruded through a perforated plate, rod-like or granular solids are produced, and these are carbonized by a carbonizer to convert the organic matter into carbon and convert it to versatile coal. The gas containing dioxin generated in the carbonization process of carbonization is completely burned at 800 ° C or more by an auxiliary burner provided in the flue to make it harmless, or dioxin is absorbed by a scrubber containing an alkaline aqueous solution. Is done. Thus, it is possible to obtain non-polluting fuel and coal having many other uses from waste containing plastics.

【0007】請求項2に記載のように、廃棄物に含まれ
る生ごみは、廃タイヤ等から生成された廃活性炭と混合
後に破砕装置に送られ、破砕物は、炭化装置からの高温
ガスを利用した乾燥装置に送られると、生ごみの悪臭は
炭によって吸着されて作業環境を良好に維持すると共に
水分が一旦炭に吸収されて高温ガスによる蒸発が効率的
に促進される。また、炭化装置からの排気ガスを有効利
用出来る。
As described in claim 2, the garbage contained in the waste is sent to a crushing device after being mixed with waste activated carbon generated from waste tires and the like, and the crushed material is supplied with hot gas from the carbonization device. When sent to the drying device used, the bad odor of the garbage is adsorbed by the charcoal to maintain a good working environment, and the moisture is once absorbed by the charcoal to efficiently promote evaporation by the high-temperature gas. Further, the exhaust gas from the carbonization device can be effectively used.

【0008】請求項3に記載のように、廃棄物に含まれ
る粗大ごみや廃木材は、破砕装置で破砕され、手選別コ
ンベヤ上で破砕物から磁選機で磁性物を、人手で有価金
属、ビン、危険物を選別し、残り破砕物は選別装置で土
砂等の微小物が除去され、残りの大中破砕物は二次破砕
装置で粉砕後にアルミセパレータでアルミを除去され、
分別装置で木屑チップと廃プラスチックとがそれぞれ分
別されてそれぞれ一旦定量供給機付きサイロへ供給され
た後で上記固形化装置へ供給されるようにすると、金属
や土砂、更にビン、危険物が除去されて炭の原料に好適
な良質な有機質木屑チップを大量に確保出来る。また木
屑チップと廃プラスチックとを分別し一旦サイロに貯蔵
してから定量供給機で固形化装置へ供給すると、バイダ
ーとして使用するプラスチックの混合量を正確に管理す
ることが出来るようになる。
According to a third aspect of the present invention, the oversized garbage and waste wood contained in the waste are crushed by a crusher, and the crushed material is manually separated from the crushed material on a hand-selecting conveyor by a magnetic separator, and the valuable metal is manually processed. Bottles and hazardous materials are sorted out, the remaining crushed materials are removed by a sorting device to remove fine matter such as earth and sand, and the remaining large and medium crushed materials are crushed by a secondary crushing device and then aluminum is removed by an aluminum separator.
If the wood chips and waste plastic are separated by the separation device and supplied to the above-mentioned solidification device after being supplied to the silo with the quantitative feeder once, metals, earth and sand, bottles, and dangerous substances are removed. As a result, a large amount of high-quality organic wood chips suitable for a raw material of charcoal can be secured. In addition, if wood chips and waste plastic are separated and stored in a silo once and then supplied to a solidifying device by a quantitative feeder, the amount of plastic used as a binder can be accurately controlled.

【0009】請求項4に記載のように、廃棄物に含まれ
る廃プラスチック、故紙及び若しくは紙屑は、破砕装置
で破砕され、磁選機で磁性物を選別後に二次破砕装置で
粉砕され、風力選別装置でダストが除去されてから廃プ
ラ・紙屑用定量供給機付きサイロへ一旦供給された後で
上記固形化装置へ供給されると、バイダーとして使用す
るプラスチックを多く含む廃プラ・紙屑が鉄等の磁性物
やダストが除去された粉砕片状態で定量供給機付きサイ
ロに貯蔵でき、定量供給によってバイダーとして使用す
るプラスチックの混合量を正確に管理することが出来る
ようになる。
According to a fourth aspect of the present invention, waste plastic, waste paper and / or paper waste contained in the waste is crushed by a crushing device, the magnetic material is separated by a magnetic separator, then crushed by a secondary crushing device, and the air is separated by wind. Once the dust is removed by the device and once supplied to a silo with a quantitative feeder for waste plastic and paper waste and then fed to the solidifying device, waste plastic and paper waste containing a large amount of plastic used as a binder is removed from iron, etc. The magnetic material and dust can be stored in a silo equipped with a quantitative feeder in a state of a crushed piece, and the amount of plastic used as a binder can be accurately controlled by the quantitative supply.

【0010】請求項5に記載のように、廃棄物に含まれ
る下水汚泥やし尿汚泥糞尿汚泥は、脱水装置で脱水後に
破砕済み紙屑や廃タイヤ等から生成された廃活性炭と混
合後に固形化装置へ供給されると、一般に処理に困る下
水汚泥やし尿汚泥糞尿汚泥でも悪臭を廃活性炭で吸収し
て比較的良好な環境でそれらの有機質を燃料として利用
出来る炭へと転換出来る。
The sewage sludge and human waste sludge and manure sludge contained in the waste are mixed with crushed paper waste and waste activated carbon generated from waste tires and the like after dewatering in a dewatering device, and then solidified in a solidification device. When it is supplied to sewage sludge or manure sludge, which is generally difficult to treat, it can absorb odors by waste activated carbon and convert those organic substances into charcoal that can be used as fuel in a relatively favorable environment.

【0011】請求項6に記載のように、廃棄物に含まれ
る廃ゴムタイヤは、破砕装置で破砕後に鉄線等の脱酸素
材と共に炭化装置に供給されて、乾留炭化され、破砕装
置で破砕後に磁選機で磁性物が除去されるようにする
と、本プラントで生ごみや下水汚泥、し尿汚泥糞尿汚泥
を処理するために混入される廃活性炭を自己供給するこ
とが出来る。
According to a sixth aspect of the present invention, the waste rubber tire contained in the waste is crushed by a crushing device, supplied to a carbonizing device together with a deoxidizing material such as an iron wire, carbonized by dry distillation, crushed by the crushing device, and then subjected to magnetic separation. If the magnetic material is removed by the machine, waste activated carbon mixed into the plant for treating garbage, sewage sludge, human waste sludge and manure sludge can be supplied by itself.

【0012】[0012]

【発明の実施の形態と実施例】図1は本発明に係る廃棄
物の無公害化再生処理プラントの再生処理工程のフロー
チャート、図2は同プラントに組み込まれた破砕装置と
してのスクリュークラッシャーの平面図、図3は同プラ
ントに組み込まれたロータセパレータの正面図、図4は
上記ロータセパレータの選別ブロックの要部の平面図、
図5は同プラント用二次破砕装置としてのカッター型粉
砕機の縦断面図、図6は他の二次破砕装置としてのスク
リュークラッシャーの断面図、図7は同アルミ選別機の
側面図、図8は同プラント用破砕装置としての破袋機の
縦断面図、図9は同破袋機の部分平面図、図10は同固
形化装置の断面図、図11は同固形化装置の水平断面
図、図12は同炭化装置の斜視図である。
DESCRIPTION OF THE PREFERRED EMBODIMENTS FIG. 1 is a flowchart of a regeneration process of a waste-free reclaiming plant according to the present invention, and FIG. 2 is a plan view of a screw crusher as a crushing device incorporated in the plant. Fig. 3 is a front view of a rotor separator incorporated in the plant, Fig. 4 is a plan view of a main part of a sorting block of the rotor separator,
FIG. 5 is a longitudinal sectional view of a cutter-type crusher as a secondary crusher for the plant, FIG. 6 is a sectional view of a screw crusher as another secondary crusher, and FIG. 7 is a side view of the aluminum separator. 8 is a longitudinal sectional view of a bag breaking machine as a crushing device for the plant, FIG. 9 is a partial plan view of the bag breaking machine, FIG. 10 is a sectional view of the solidifying device, and FIG. FIG. 12 is a perspective view of the carbonizing device.

【0013】図1に示す様に、ソファ等の家具や冷蔵庫
等の家電製品等の粗大ごみや、家屋の解体で出る廃木材
等の大形廃棄物WAは、木材の他、PP(ポリプロピレ
ン)やPE(ポリエチレン)、PS(ポリスチレン)、
PET(ポリエチレンテレフタレート)、PA(ポリア
ミド)、ABS(アクリルニトリルブタジェンスチレ
ン)、PVC(ポリ塩化ビニル)等の各種プラスチック
WPや鉄FやステンレスSの金具、アルミフレームA、
ガラスG、土砂D、ビンB等を含んでいるが、例えば図
2に示すようなスクリュークラッシャ等の粗大ごみ用破
砕機10によって破片に破砕される。破砕物W1は、フ
レックスコンベヤ15によって手選別コンベヤ20上に
搬送され、コンベヤ20で移動している間に先ず磁選装
置25の電気磁石によって鉄F等の磁性物が除去され、
作業員によってビンB、銅やアルミA、ステンレスS、
ガスボンベ等の危険物Zが選別除去される。
As shown in FIG. 1, oversized garbage such as furniture such as sofas and household electric appliances such as refrigerators, and large-sized wastes WA such as waste woods generated by dismantling houses are made of PP (polypropylene) in addition to wood. And PE (polyethylene), PS (polystyrene),
Various plastics WP such as PET (polyethylene terephthalate), PA (polyamide), ABS (acrylonitrile butadiene styrene), PVC (polyvinyl chloride), metal fittings of iron F and stainless steel, aluminum frame A,
Although it contains glass G, earth and sand D, bottle B, etc., it is crushed into fragments by a bulky crusher 10 such as a screw crusher as shown in FIG. 2, for example. The crushed material W1 is conveyed by a flex conveyor 15 onto a manual sorting conveyor 20, and while moving on the conveyor 20, first, a magnetic substance such as iron F is removed by an electric magnet of a magnetic separation device 25,
Bin B, copper or aluminum A, stainless steel S,
Dangerous goods Z such as gas cylinders are sorted out.

【0014】その後、破砕物W1’は、例えば図3と図
4に示すような傾斜したロータセパレータ30の下部に
送られ、上方に送りがかけられる間にプラスチック系や
木質系の可燃軽量物W2は上端部から、煉瓦や除去忘れ
のボンベZやビンB等の反発性重量物は下端部から、土
砂Dはセパレータ30の下から分別される。可燃軽量物
W2は、コンベヤ21で図5に示すような剪断型破砕粉
砕機等の二次破砕装置35に搬送され、細片に粉砕され
る。粉砕物W3は、フレックスコンベヤ15によって、
図7に示すようなアルミセパレータ40に搬送され、そ
の入口部で再度磁選装置25の電気磁石によって鉄F等
の磁性物が除去された後に、アルミAが、選別除去され
る。かくして金属F、S、Aや土砂Dの混入していない
粉砕物W4は、コンベヤ22上で手選別等でプラスチッ
ク系粉砕物WPと木質系粉砕物WWとに分別されてそれ
ぞれ定量供給機付きサイロ5、6に集められ、貯蔵され
る。二次破砕装置としては、他にも幾多の種類が有る
が、図6に示すような螺旋体方式のスクリュークラッシ
ャー38を採用することも出来る。
Thereafter, the crushed material W1 'is sent to, for example, a lower portion of the inclined rotor separator 30 as shown in FIGS. 3 and 4, and while being sent upward, a plastic or wood-based combustible lightweight material W2 is sent. Is separated from the upper end, repulsive heavy objects such as bricks and cylinders B and bottles B left unremoved are separated from the lower end, and earth and sand D is separated from under the separator 30. The combustible lightweight material W2 is conveyed by the conveyor 21 to a secondary crushing device 35 such as a shearing type crushing crusher as shown in FIG. 5, and crushed into small pieces. The crushed material W3 is formed by the flex conveyor 15
After being conveyed to an aluminum separator 40 as shown in FIG. 7 and a magnetic substance such as iron F is removed again by the electric magnet of the magnetic separation device 25 at the entrance, aluminum A is selectively removed. Thus, the crushed material W4 not containing the metals F, S, A and the earth and sand D is separated into the plastic crushed material WP and the wood crushed material WW by manual selection on the conveyor 22, and the silos with the quantitative feeders are respectively provided. Collected in 5 and 6 and stored. As the secondary crushing device, there are many other types, but a screw crusher 38 of a helical type as shown in FIG. 6 can also be employed.

【0015】家庭やレストラン等から出される生ごみの
廃棄物WBは、定量供給機付き生ごみ受け入れホッパー
45に投入され、また使用済みの物や後述の廃タイヤか
ら生成された物等の廃活性炭WCも定量供給機付き活性
炭ホッパー47に投入され、それらホッパー45、47
から1:1等の一定量ずつそれぞれの定量供給機46、
48によってフライトコンベヤ23上に送り出され、粉
砕装置50へ共に供給されて、そこで撹拌混合されなが
ら粉砕される。撹拌混合中に、生ごみの悪臭は活性炭W
Cによって吸着されて、また生ごみの水分は一旦活性炭
に吸収されて後述の乾燥装置55における高温ガスによ
る蒸発が効率的に促進される。粉砕混合物W5は、スク
リューコンベヤ及びフライトコンベヤ23と定量供給機
付き活性炭ホッパー53に一時貯蔵され、そこからその
定量供給機54を介して一定量ずつ乾燥装置55に搬送
される。生ごみが、袋に詰め込まれている場合は、図3
と図4に示すような破袋機43を生ごみ受け入れホッパ
ー45の前に配置することが出来る。上記粉砕装置50
は、竪型でギヤードモータ51で回転駆動させる垂直軸
周りに複数隔設された回転刃とケーシング52の内壁か
ら上記回転刃の間に突設された複数の固定刃とで粉砕
し、混合するもので、広く使用されているものである。
[0015] The garbage waste WB discharged from homes and restaurants is put into a garbage receiving hopper 45 equipped with a quantitative feeder, and waste activated carbon such as used ones and those generated from waste tires described later. WC is also charged into the activated carbon hopper 47 with a fixed-rate feeder, and the hoppers 45 and 47
, A fixed amount feeder 46 for each fixed amount such as 1: 1
It is sent out onto the flight conveyor 23 by 48 and fed together to the crushing device 50, where it is crushed while being stirred and mixed. During stirring and mixing, the odor of the garbage is activated carbon W
The water of the garbage is adsorbed by C and is once absorbed by the activated carbon, and the evaporation by the high-temperature gas in the drying device 55 described later is efficiently promoted. The ground mixture W5 is temporarily stored in a screw conveyor and a flight conveyor 23 and an activated carbon hopper 53 with a quantitative feeder, and is conveyed therefrom to a drying device 55 via the quantitative feeder 54 by a fixed amount. If garbage is packed in a bag,
4 can be arranged in front of the garbage receiving hopper 45. The above crushing device 50
Is pulverized and mixed by a plurality of rotating blades, which are vertically spaced around a vertical axis driven to rotate by a geared motor 51, and a plurality of fixed blades projecting from the inner wall of the casing 52 between the rotating blades. It is widely used.

【0016】乾燥装置のロータリドライヤー55は、一
端部のバーナ56が発生するガスや後述の炭化装置90
からの高温排気ガスを熱風炉57で合流させてから回転
胴体58内に送り、回転胴体58の内壁付き螺旋羽根で
送りがかけられている粉砕混合物W5を乾燥する。排気
ガスは、サイクロン61でダストを分離してから、冷却
機62を経てファン63によってバイオ脱臭装置64を
通して大気中に排出される。分離ダストD1は、乾燥粉
砕混合物W5’と共にフライトコンベヤ23によって定
量供給機付き乾燥生ごみ用サイロ7に搬送され、貯蔵さ
れる。
The rotary dryer 55 of the drying device is provided with a gas generated by the burner 56 at one end and a carbonizing device 90 described later.
The high-temperature exhaust gas from the furnace is combined in the hot air stove 57 and then sent into the rotating body 58, and the pulverized mixture W5 fed by the spiral blade with the inner wall of the rotating body 58 is dried. The exhaust gas is separated into dust by a cyclone 61 and then discharged to the atmosphere through a biodeodorizer 64 by a fan 63 through a cooler 62. The separated dust D1 is transported by the flight conveyor 23 together with the dry and crushed mixture W5 'to the dry garbage silo 7 with a quantitative feeder and stored.

【0017】関連事業所から大量に出される廃プラスチ
ック、故紙及び若しくは紙屑の廃棄物WDは、上記破砕
装置10とほぼ同じ構造の廃プラ・故紙用破砕装置70
で破砕され、ベルトコンベヤ24で二次破砕装置73へ
搬送中に磁選機25で磁性物Fが選別される。その後に
上記粉砕装置35又は38と同じ構造の二次破砕装置7
5で粉砕され、粉砕物W6は、ベルトコンベヤ24で風
力選別装置80へ搬送されてダストが除去される。風力
選別装置75は、バイブロフィーダを備えた水平供給部
76と直交する略垂直な選別部77の上端において上記
ファン67に接続されいる。従って、選別部77には、
上方への空気流が存在してその屈曲部78をゆっくりと
落下して行く粉砕物W6の内軽い物はその上方への空気
流によってサイクロン61へ搬送され、重いダストD2
は落下除去される。サイクロン61内の廃プラ・故紙の
粉砕物W7は、大部分廃プラ・紙屑用定量供給機付きサ
イロ8へコンベヤ22で搬送され、貯蔵される。一部分
は、手選別等で上記定量供給機付き乾燥生ごみ用サイロ
7に搬送され、貯蔵される。
A large amount of waste plastic, waste paper, and / or paper waste WD discharged from related offices is provided with a waste plastic / waste paper crusher 70 having substantially the same structure as the crusher 10 described above.
The magnetic material F is sorted by the magnetic separator 25 while being conveyed to the secondary crusher 73 by the belt conveyor 24. Thereafter, the secondary crusher 7 having the same structure as the crusher 35 or 38 is used.
The crushed material W6 is conveyed to the wind separation device 80 by the belt conveyor 24 to remove dust. The wind separation device 75 is connected to the fan 67 at an upper end of a substantially vertical selection portion 77 orthogonal to a horizontal supply portion 76 having a vibratory feeder. Therefore, in the sorting unit 77,
The lighter crushed material W6, which has an upward air flow and slowly falls down the bent portion 78, is conveyed to the cyclone 61 by the upward air flow, and the heavy dust D2
Is dropped and removed. Most of the waste plastic / waste paper pulverized material W7 in the cyclone 61 is conveyed by the conveyor 22 to the silo 8 with a quantitative feeder for waste plastic / paper waste and stored therein. A part is conveyed to the said dry food waste silo 7 with a fixed-quantity feeder by hand sorting, etc., and stored.

【0018】図1に図示していないが、下水汚泥やし尿
汚泥糞尿汚泥は、遠心式脱水装置で脱水後に破砕済み紙
屑や、廃タイヤ等から生成された廃活性炭WCと混合後
に生ごみWBと同様に乾燥装置55を経て上記定量供給
機付き乾燥生ごみ用サイロ7に搬送され、貯蔵される。
廃タイヤは、そのまま又は破砕後に炭化装置で乾留炭化
されて、上記のように生ごみWBや下水汚泥や糞尿汚泥
に混合される。
Although not shown in FIG. 1, sewage sludge and human waste sludge excrement sludge is mixed with crushed paper waste after dewatering by a centrifugal dewatering device, waste activated carbon WC generated from waste tires and the like, and garbage WB. Similarly, the garbage is conveyed to the above-mentioned silicide for dry garbage 7 with the quantitative feeder via the drying device 55 and stored.
The waste tire is subjected to dry distillation carbonization by a carbonization apparatus as it is or after crushing, and mixed with the garbage WB, sewage sludge, and manure sludge as described above.

【0019】各廃プラスチック用サイロ5、木屑チップ
用サイロ6、乾燥生ごみ用サイロ7、廃プラ・紙屑用定
量供給機付きサイロ8からそれぞれの定量供給機によっ
てプラスチック分が70〜30重量%、その他が30〜
70重量%となるように供給されて混合物WMが定量供
給機付きサイロ9内に一時的に貯蔵される。そこから固
形装置80に消費量に合わせて定量供給機とコンベヤを
介して混合物WMは供給される。固形装置80では、後
述するように螺旋体82A、82Bによって混合物WM
に送りをかけて撹拌混合しながら圧縮してダイオイキシ
ンが発生しない範囲の120〜300℃に加熱し、プラ
スチックを溶融して練り合わせて流動可能状態にし、こ
の流動状態の中間生成物から多孔板85に通して押し出
し成形して棒状や粒状の有機物から成る固形物WSを形
成する。プラスチック分が上記含有量であれば、形崩れ
の起きない保形性の良い固形物WSが得られる。
Each of the waste plastic silo 5, the wood waste chip silo 6, the dry garbage silo 7, and the waste plastic / paper waste constant feeder silo 8 has a plastic content of 70 to 30% by weight by each quantitative feeder. Others are 30 ~
The mixture WM is supplied so as to be 70% by weight, and is temporarily stored in the silo 9 with the metering device. From there, the mixture WM is supplied to the solidifying device 80 via the metering feeder and the conveyor according to the consumption. In the solid device 80, the mixture WM is formed by the spiral bodies 82A and 82B as described later.
The mixture is heated to 120 to 300 ° C. in a range where dioxin is not generated while stirring and mixing, and the plastic is melted and kneaded to make it flowable. Then, the mixture is extruded to form a solid WS composed of a rod-like or granular organic substance. When the content of the plastic is the above-mentioned content, a solid WS having good shape retention and without shape collapse can be obtained.

【0020】固形物WSを炭化する炭化装置90は、例
えば図12に示すようなバッチ方式では、バーナ92で
かご93に入れられた固形物WSに点火し、排熱誘引装
置94で炭化炉本体91内において摂氏300〜350
度の範囲で炉内温度を均一化して蒸し焼きするべく空気
供給量を絞って乾留し、炭化する。ほぼ全体に炭化が行
き渡った時点で摂氏800度以上で高温燃焼させて残留
揮発分を焼却する。その後、消火してから放冷して炭を
得る。乾留・炭化工程で発生する排気ガスは、固形物W
Sが塩化物を含んでいればダイオイキシンを含むことに
なるが、煙道91Aのスクラバー91B内の石灰等を入
れたアルカリ性水溶液にダイオイキシンを吸収させた
り、図示はしていないが補助バーナを付設して摂氏80
0度以上で高温燃焼させて無害化できる。この他、本出
願人による特願平8−162843号出願の明細書と図
面に記載した炭化装置も使用される。
In a batch system as shown in FIG. 12, for example, a carbonizer 90 for carbonizing the solid WS ignites the solid WS put in the basket 93 by a burner 92 and a carbonization furnace main body by an exhaust heat induction device 94. 300-350 Celsius within 91
In order to equalize the temperature inside the furnace within a range of degrees and to perform roasting, the amount of air supplied is reduced and carbonized by carbonization. At the time when carbonization is almost completely spread, high-temperature combustion is performed at 800 ° C. or more to incinerate residual volatile matter. After extinguishing the fire, let it cool to obtain charcoal. Exhaust gas generated in the carbonization / carbonization process is solid W
If S contains chloride, it will contain dioxin. However, dioxin may be absorbed in an alkaline aqueous solution containing lime or the like in the scrubber 91B of the flue 91A, or an auxiliary burner (not shown) may be provided. 80 centigrade
It can be made harmless by burning at a high temperature at 0 degrees or more. In addition, the carbonization apparatus described in the specification and drawings of Japanese Patent Application No. 8-162843 filed by the present applicant is also used.

【0021】粗大ごみ用破砕機のスクリュークラッシャ
10は、例えば図2に示すように、ホッパー11の下方
のケーシング12内部の作業室12Aに上から下に噛み
込むようにモータ14Aと減速機14Bとで等速回転駆
動される2本の破砕スクリュー13A、13Bを水平に
軸承しており、コンテナーや各種容器等大形廃棄物を粗
砕して下方から粗いスクリーン12Bを通して排出する
ようにしている。この破砕によって金属やプラスッチ
ク、木材などを複合材製品から分離して磁力選別装置2
5による選別を行い易くしている。破砕スクリュー13
A、13Bの外周縁には、被破砕物に対する噛み込みを
促進する各種形状の突出刃を適宜設けることが出来る。
他に、破砕機として従来からあるハンマークラッシャー
やロータリプレスクラッシャーが廃棄物中の多い混入物
に応じて適宜選択使用される。スクリュークラッシャー
は、二軸式や一軸式もあり、回転テーパ状破砕スクリュ
ー部やストレート破砕スクリュー部とケーシング内面の
複数の長手方向固定刃やテーパ状部とストレート部との
間のリング状固定刃の間で破砕を行い、粉砕を省き得る
大きさまで破砕することが出来る。
As shown in FIG. 2, for example, the screw crusher 10 of the crusher for oversized refuse is provided with a motor 14A and a speed reducer 14B so as to bite into the working chamber 12A inside the casing 12 below the hopper 11. , Two crushing screws 13A and 13B which are driven to rotate at a constant speed are horizontally supported, and large wastes such as containers and various containers are crushed and discharged from below through a coarse screen 12B. By this crushing, metal, plastic, wood, etc. are separated from the composite material product and the magnetic separation device 2
5 makes it easier to sort. Crushing screw 13
Protruding blades of various shapes for promoting biting of the crushed material can be appropriately provided on the outer peripheral edges of A and 13B.
In addition, a conventional hammer crusher or rotary press crusher is appropriately selected and used as a crusher according to a large amount of contaminants in the waste. The screw crusher is also available in two-shaft and single-shaft types, with a rotating tapered crushing screw part, a straight crushing screw part and a plurality of longitudinal fixed blades on the inner surface of the casing and a ring-shaped fixed blade between the tapered part and the straight part. The crushing can be performed between the crushed pieces, and the crushed pieces can be crushed to a size that can eliminate the crushing.

【0022】ロータセパレータ30は、図3と図4に示
すように、大径輪体31Aと小径輪体31Bとが軸方向
に交互に配列された複数の回転ロータ31を隣接ロータ
同士の大径輪体31Aと小径輪体31Bとを篩目用間隔
Gをおいて傾斜フレーム30A上に配列しており、中間
部上方から供給された被処理物W1’に上方に送りを掛
けるように各ロータ31を回転駆動装置32で回転駆動
して非反発性軽量物W2を上方に搬送し、反発性重量物
を下方に転落させ、混合微小物Dをロータの大径輪体3
1A及び小径輪体31Bの間の篩目Gから落下させて選
別する。またセパレータ30は、底を開放し、中間部上
面に中小被処理物の供給開口33Aを、上端部に非反発
性軽量物の取り出し開口33Bを且つ下端部に反発性重
量物の取り出し開口33Cを各々有した筐体33で被わ
れており、防塵、防音が対策されている。また、筐体3
3の反発性重量物の取り出し開口33C近傍上方に、ロ
ータ上面上に上昇空気流A1を供給する空気噴出手段3
3Dが設けられており、筐体33の下端部から噴き上が
る上昇空気流A1によって、混合中小被処理物W1’の
解放を促進し、非反発性軽量物W2の上方への搬送を促
進する。ロータ31は、一端に回転駆動装置32を成す
歯車32Aを固定した六角軸30Cに大径輪体31Aと
間隔片の小径輪体31Bとを軸方向に交互に嵌合配列し
ている。大径輪体31Aと小径輪体31Bは、一体物と
して形成される。回転駆動装置32は、ロータ付き歯車
32A間にアイドル歯車32Bを介在させ、モータ32
Mで大径輪体32A付き歯車32Aを上記のような送り
を掛けるように回転駆動す様にしている。回転駆動装置
32は、上記歯車式に替えてチエーン式を採用すること
が出来る。また大径輪体31Aの形状は、上記以外に色
々な形状をとることが出来る。ロータセパレータ30
は、伸縮手段34Bによってフレーム30Aごと傾斜角
度が調節されるようになっている。
As shown in FIGS. 3 and 4, the rotor separator 30 includes a plurality of rotating rotors 31 in which large-diameter annular bodies 31A and small-diameter annular bodies 31B are alternately arranged in the axial direction. The wheel body 31A and the small-diameter wheel body 31B are arranged on the inclined frame 30A with a sieve gap G therebetween, and each rotor is arranged to feed the workpiece W1 'supplied from above the middle part upward. 31 is rotated by a rotary driving device 32 to convey the non-repulsive lightweight object W2 upward, to drop the repulsive heavy object downward, and to mix the minute mixed substance D with the large-diameter wheel 3 of the rotor.
It is dropped from the sieve G between 1A and the small-diameter annular body 31B and sorted. Further, the separator 30 has an opening at the bottom, a supply opening 33A for small and medium-sized workpieces at the upper surface of the intermediate portion, a take-out opening 33B for the non-repulsive lightweight material at the upper end, and a take-out opening 33C for the repulsive heavy material at the lower end. Each of them is covered with a housing 33, and dustproofing and soundproofing are taken. In addition, case 3
Air ejecting means 3 for supplying a rising air flow A1 above the upper surface of the rotor above the vicinity of the take-out opening 33C of the repulsive heavy object 3
3D is provided, and the rising airflow A1 blown up from the lower end portion of the housing 33 promotes the release of the small and medium workpiece W1 'to be mixed, and facilitates the upward transport of the non-repulsive lightweight object W2. In the rotor 31, a large-diameter ring 31A and a small-diameter ring 31B of a spacing piece are alternately fitted and arranged in an axial direction on a hexagonal shaft 30C to which a gear 32A constituting a rotation drive device 32 is fixed at one end. The large-diameter ring 31A and the small-diameter ring 31B are formed as an integral body. The rotation drive device 32 has an idle gear 32B interposed between a gear 32A with a rotor and a motor 32.
At M, the gear 32A with the large-diameter ring 32A is driven to rotate so as to feed as described above. The rotation drive device 32 can adopt a chain type instead of the gear type. Further, the shape of the large-diameter ring body 31A can take various shapes other than the above. Rotor separator 30
The inclination angle of the frame 30A is adjusted by the expansion and contraction means 34B.

【0023】粉砕装置35としては、図5に示すような
二軸式剪断型のものが有り、ある程度の大きさの粗砕さ
れた軽量物W2をケーシング35A内で左右一対の上か
ら下へ噛み込む回転破砕刃36Bと対応した相手軸の突
出刃36B及びスクリーン35Cをなす縦通固定刃35
Bとで細断していきスクリーン35Cによって所望の大
きさの破片を得る。粉砕装置としては、この図示例の二
軸式剪断型の他に一軸式カッター型のものも使用され
る。他に、図6に示すような粉砕装置38として二軸式
又は一軸式のロータリプレスクラッシャーが有り、ケー
シング39C内において、回転テーパ状破砕スクリュー
部38A及びストレート破砕スクリュー部38Bとケー
シング内面の複数の長手方向固定刃39Aやテーパ状部
とストレート部との間のリング状固定刃39Bの間で粉
砕することが出来る。
As the crushing device 35, there is a two-shaft type shearing type as shown in FIG. 5. A crushed lightweight material W2 having a certain size is bitten from a pair of left and right tops to bottoms in a casing 35A. The blade 36B of the mating shaft corresponding to the rotary crushing blade 36B to be inserted and the longitudinal fixed blade 35 forming the screen 35C
B, and a piece having a desired size is obtained by the screen 35C. As the pulverizer, a single-shaft cutter type besides the two-shaft shear type shown in the illustrated example is used. In addition, there is a rotary press crusher of a biaxial type or a uniaxial type as a crushing device 38 as shown in FIG. Grinding can be performed between the longitudinal fixed blade 39A and the ring-shaped fixed blade 39B between the tapered portion and the straight portion.

【0024】アルミ選別機40は、図7に示すように、
永久磁石式ドラム回転型アルミセパレータであって、投
入されたアルミニウムは良伝導体で磁力線によって電磁
誘導現象をおこしてうず電流を発生し、永久磁石41A
を備えた高速回転ドラム41によって強力な交流磁界を
受けてアルミニウム内部に発生するうず電流と反発し合
い弾き出されることになる。即ち、アルミニウムやプラ
スチックを含む廃棄物はショートストッパーを備えた周
動ループベルト42の上に供給されて、ギヤドモータ4
2Aで回転駆動される一方のベルトロータの永久磁石式
ドラム41において弾き出され、端排出口40Aからア
ルミが選別され、残りの処理物W4は内側排出口40B
から排出され、フレックスコンベヤ15へ送られる。
The aluminum sorter 40 is, as shown in FIG.
It is a permanent magnet type drum rotating type aluminum separator, and the inputted aluminum is a good conductor, generates an eddy current by causing an electromagnetic induction phenomenon by magnetic field lines, and generates a permanent magnet 41A.
When a strong alternating magnetic field is received by the high-speed rotating drum 41 provided with, the eddy current generated inside the aluminum is repelled and ejected. That is, the waste containing aluminum and plastic is supplied onto the peripheral loop belt 42 having the short stopper, and the geared motor 4
The aluminum material is ejected from the permanent magnet drum 41 of one of the belt rotors driven to rotate at 2A, aluminum is sorted out from the end discharge port 40A, and the remaining processed material W4 is removed from the inner discharge port 40B.
And is sent to the flex conveyor 15.

【0025】破袋機43としては、図8と図9に示すよ
うに、下方に狭くなった処理空間43Cを形成する傾斜
側板付きホッパー43Bを有したケーシング43A内で
矢印R1へ回転駆動されるロータ44と、ロータ44の
長手方向に複数組配列されたなぎなた状破袋刃44Aと
から成るものが使用される。ロータ44は、なぎなた状
破袋刃44A間において横断した上仕切り板43Dの中
央部上で軸受43Eで軸承されている。上仕切り板43
Dの下には、円弧面上に固定刃の縦通材43Fを複数固
定して粗いスクリーン43Gを形成した下仕切り板43
Hが設けられている。
As shown in FIGS. 8 and 9, the bag-breaking machine 43 is driven to rotate in the direction of arrow R1 in a casing 43A having a hopper 43B with inclined side plates forming a processing space 43C narrowed downward. A rotor composed of a rotor 44 and a plurality of sets of blades 44A arranged in a longitudinal direction of the rotor 44 is used. The rotor 44 is supported by bearings 43E on the central portion of the upper partition plate 43D that crosses between the plywood blades 44A. Upper partition plate 43
Below D, a lower partition plate 43 in which a plurality of longitudinal members 43F of fixed blades are fixed on an arc surface to form a coarse screen 43G.
H is provided.

【0026】固形装置80では、図10と図11に示す
ように、混合廃棄物WMは、螺旋体82A、82Bで破
砕混練され、圧搾部83で圧縮粉砕されて発熱し、溶融
後に多孔板成形部85で固形物の燃料WSとして押し出
し形成される。これは、カロリーが安定し、臭やカビの
発生も無くボイラーの燃料としも好適である。より具体
的に説明すると、固形燃料形成機80は、一端部の投入
口81Aから投入されたプラスチックを含む混合廃棄物
WMを他端部の取り出し口81Bに至る長手方向にかけ
て搬送しながら破砕、混練、圧縮及び粉砕を行い、摩擦
や圧縮の発熱で温度を上げ、プラスチックを溶融したり
するもので、細長ケーシング81内の長手方向に並設さ
れ対向方向に回転駆動される一対の回転軸80S、80
Sと、それらの各々に取り付けられた螺旋体82A、8
2B及び圧搾体83A、83Bと、これらに対して所定
の隙間をとってケーシング81内に取り外し可能に付設
された耐摩耗性内張体81Cと、取り出し口81Bの固
形化用ノズル付き多孔板85とから構成されている。圧
搾体は、特に粉砕と溶解を促進する臼状圧搾部83を構
成している。固形燃料成形機80で、発熱量が大きて塩
素ガスが発生するおそれがある時、適宜給水して温度上
昇を抑制するように給水ラインを付設することが出来
る。
In the solidifying device 80, as shown in FIGS. 10 and 11, the mixed waste WM is crushed and kneaded by the spirals 82A and 82B, compressed and pulverized by the pressing unit 83, generates heat, and after melting, forms the perforated plate forming unit. At 85, it is extruded as a solid fuel WS. It has a stable calorie, does not generate odor or mold, and is suitable for boiler fuel. More specifically, the solid fuel forming machine 80 crushes and kneads while transporting the mixed waste WM containing plastic injected from the input port 81A at one end in the longitudinal direction to the outlet 81B at the other end. A pair of rotating shafts 80S, which perform compression and pulverization, raise the temperature by the heat generated by friction and compression, and melt the plastic, and are arranged side by side in the elongated casing 81 in the longitudinal direction and driven to rotate in the opposite direction. 80
S and the spirals 82A, 8 attached to each of them
2B and compressed bodies 83A and 83B, a wear-resistant lining body 81C detachably provided in the casing 81 with a predetermined gap therebetween, and a perforated plate 85 with a nozzle for solidification at a take-out port 81B. It is composed of The squeezed body constitutes a mortar-shaped squeezed portion 83 that particularly promotes pulverization and dissolution. In the solid fuel molding machine 80, when the calorific value is large and there is a possibility that chlorine gas is generated, a water supply line can be provided so as to supply water appropriately and suppress a rise in temperature.

【0027】[0027]

【発明の効果】以上の説明から明らかなように、本発明
の請求項1記載の廃棄物の無公害化再生処理プラントに
よれば、各種のプラスチックを含む有機質系廃棄物を破
砕する破砕装置と、破砕された破砕物から有価物を選別
する選別装置と、有価物の除去後の破砕物の内プラスチ
ックとそれ以外の破砕物を前者が70〜30重量%、後
者が30〜70重量%となるように供給され、螺旋体に
よって送りをかけて撹拌混合しながら圧縮して120〜
300℃に加熱し、練り合わせて流動可能状態にし、こ
の流動状態の中間生成物から多孔板を通して押し出し成
形して棒状や粒状の固形物を形成する固形化装置と、固
形物を乾留して炭化する炭化装置とから構成されてお
り、また上記炭化装置は、排気ガスの煙道に補助バーナ
又はアルカリ性水溶液を入れたスクラバーを備えている
ために、事業所や家庭から廃棄される各種のプラスチッ
クを含む有機質系廃棄物は、先ず破砕装置で破片に破砕
されて後工程での金属等の有価物の選別作業が楽に出来
るようになる。更に、有価物の除去後の破砕物は、固形
化装置において螺旋体によって送りがかけられて70〜
30重量%のプラスチックと30〜70重量%のプラス
チック以外の破砕物が撹拌混合されながら圧縮され、圧
縮熱で120〜300℃に加熱され、プラスチックは、
この範囲の温度で塩素分を含んでいてもダイオキシンを
発生させずに溶融し、練り合わされて流動可能状態のバ
インダーとしての働きをしてほかの破砕物を結合する。
従って、多孔板を通して押し出し成形されると棒状や粒
状の固形物が生成され、これらは、炭化装置で乾留され
有機質は炭化されて用途の多い炭に転換される。この炭
化の乾留過程で発生するダイオキシンを含んだガスは、
煙道に設けられた補助バーナによって摂氏800度以上
で完全燃焼されて無害化されるか、又はアルカリ性水溶
液を入れたスクラバーでダイオキシンが吸収される。か
くして、プラスチックを含んだ廃棄物から無公害で燃料
やそれ以外にも多くの用途の有る炭を得ることが出来
る。
As is apparent from the above description, according to the waste reclaiming and reprocessing plant according to the first aspect of the present invention, a crushing apparatus for crushing organic waste including various plastics is provided. A sorting device for sorting valuable materials from the crushed crushed materials, and a plastic and other crushed materials of the crushed materials after the removal of the valuable materials of 70 to 30% by weight of the former and 30 to 70% by weight of the latter. And compressed by stirring and mixing while feeding by a spiral.
The mixture is heated to 300 ° C., kneaded into a flowable state, a solidifying device for extruding the intermediate product in the fluidized state through a perforated plate to form a rod-shaped or granular solid, and carbonizing the solid by carbonizing. And a carbonization device.The carbonization device includes an auxiliary burner or a scrubber containing an alkaline aqueous solution in the flue of exhaust gas, and thus includes various types of plastic discarded from business establishments and homes. The organic waste is first crushed into fragments by a crushing device, so that it is possible to easily sort valuable materials such as metals in a subsequent process. Furthermore, the crushed material after the removal of the valuables is fed by a spiral in a solidifying device, and
30% by weight of plastic and 30 to 70% by weight of crushed materials other than plastic are compressed while being stirred and mixed, and heated to 120 to 300 ° C. by heat of compression.
Even at a temperature in this range, even if it contains chlorine, it is melted without generating dioxin, kneaded and acts as a binder in a flowable state to bind other crushed materials.
Therefore, when extruded through a perforated plate, rod-like or granular solids are produced, and these are carbonized by a carbonizer to convert the organic matter into carbon and convert it to versatile coal. The gas containing dioxin generated in the carbonization process of carbonization is
Auxiliary burners installed in the flue completely burn at 800 ° C. or higher to make them harmless, or dioxins are absorbed by a scrubber containing an alkaline aqueous solution. Thus, it is possible to obtain non-polluting fuel and coal having many other uses from waste containing plastics.

【0028】請求項2記載の廃棄物の無公害化再生処理
プラントによれば、廃棄物に含まれる生ごみは、廃タイ
ヤ等から生成された廃活性炭と混合後に破砕装置に送ら
れ、破砕物は、炭化装置からの高温ガスを利用した乾燥
装置に送られるので、生ごみの悪臭は炭によって吸着さ
れて作業環境を良好に維持すると共に水分が一旦炭に吸
収されて高温ガスによる蒸発が効率的に促進される。ま
た、炭化装置からの排気ガスを有効利用出来る。
According to the second aspect of the present invention, the garbage contained in the waste is sent to a crushing device after being mixed with waste activated carbon generated from waste tires and the like, and the crushed material is removed. Is sent to a drying device that uses hot gas from the carbonization device, so the odor of garbage is adsorbed by the charcoal and maintains a good working environment, while moisture is once absorbed by the charcoal and evaporation by the hot gas is efficient. Promoted. Further, the exhaust gas from the carbonization device can be effectively used.

【0029】請求項3記載の廃棄物の無公害化再生処理
プラントによれば、廃棄物に含まれる粗大ごみや廃木材
は、破砕装置で破砕され、手選別コンベヤ上で破砕物か
ら磁選機で磁性物を、人手で有価金属、ビン、危険物を
選別し、残り破砕物は選別装置で土砂等の微小物が除去
され、残りの大中破砕物は二次破砕装置で粉砕後にアル
ミセパレータでアルミを除去され、分別装置で木屑チッ
プと廃プラスチックとがそれぞれ分別されてそれぞれ一
旦定量供給機付きサイロへ供給された後で上記固形化装
置へ供給されるので、金属や土砂、更にビン、危険物が
除去されて炭の原料に好適な良質な有機質木屑チップを
大量に確保出来る。また木屑チップと廃プラスチックと
を分別し一旦サイロに貯蔵してから定量供給機で固形化
装置へ供給すると、バイダーとして使用するプラスチッ
クの混合量を正確に管理することが出来るようになる。
According to the third aspect of the present invention, the oversized refuse and waste wood contained in the waste are crushed by a crusher, and the crushed material is separated from the crushed material by a magnetic separator on a hand-selection conveyor. Magnetic materials are manually separated into valuable metals, bottles, and hazardous materials.Remaining crushed materials are removed by a separation device to remove fines such as earth and sand.The remaining large and medium crushed materials are crushed by a secondary crusher and then separated by an aluminum separator. The aluminum is removed, and the wood chips and waste plastic are separated by a separation device, and once supplied to a silo with a quantitative feeder, respectively, and then supplied to the solidification device. The material is removed, and a large amount of high-quality organic wood chips suitable for a raw material of charcoal can be secured. In addition, if wood chips and waste plastic are separated and stored in a silo once and then supplied to a solidifying device by a quantitative feeder, the amount of plastic used as a binder can be accurately controlled.

【0030】請求項4記載の廃棄物の無公害化再生処理
プラントによれば、廃棄物に含まれる廃プラスチック、
故紙及び若しくは紙屑は、破砕装置で破砕され、磁選機
で磁性物を選別後に二次破砕装置で粉砕され、風力選別
装置でダストが除去されてから廃プラ・紙屑用定量供給
機付きサイロへ一旦供給された後で上記固形化装置へ供
給されるので、バイダーとして使用するプラスチックを
多く含む廃プラ・紙屑が鉄等の磁性物やダストが除去さ
れた粉砕片状態で定量供給機付きサイロに貯蔵でき、定
量供給によってバイダーとして使用するプラスチックの
混合量を正確に管理することが出来るようになる。
According to the plant for detoxifying and reclaiming waste according to claim 4, waste plastic contained in the waste,
Waste paper and / or paper debris is crushed by a crusher, the magnetic material is separated by a magnetic separator, then crushed by a secondary crusher, dust is removed by a wind separator, and then once into a silo with a quantitative feeder for waste plastic and paper waste. Since it is supplied to the above-mentioned solidification device after it is supplied, waste plastic and paper waste containing a large amount of plastic used as a binder is stored in a silo with a quantitative feeder in the form of crushed pieces from which magnetic substances such as iron and dust have been removed. It is possible to accurately control the mixing amount of the plastic used as a binder by the quantitative supply.

【0031】請求項5記載の廃棄物の無公害化再生処理
プラントによれば、廃棄物に含まれる下水汚泥やし尿汚
泥糞尿汚泥は、脱水装置で脱水後に破砕済み紙屑や廃タ
イヤ等から生成された廃活性炭と混合後に固形化装置へ
供給されるので、一般に処理に困る下水汚泥やし尿汚泥
糞尿汚泥でも悪臭を廃活性炭で吸収して比較的良好な環
境でそれらの有機質を燃料として利用出来る炭へと転換
出来る。
According to the fifth aspect of the present invention, the sewage sludge and human waste sludge and manure sludge contained in the waste are generated from crushed paper waste, waste tires and the like after dewatering by the dewatering device. The waste activated carbon is mixed with waste activated carbon and fed to the solidification device, so even sewage sludge and human waste sludge and manure sludge, which are generally difficult to treat, can absorb odors by waste activated carbon and use those organic substances as fuel in a relatively favorable environment. Can be converted to

【0032】請求項6記載の廃棄物の無公害化再生処理
プラントによれば、廃棄物に含まれる廃ゴムタイヤは、
破砕装置で破砕後に鉄線等の脱酸素材と共に炭化装置に
供給されて、乾留炭化され、破砕装置で破砕後に磁選機
で磁性物が除去されるので、本プラントで生ごみや下水
汚泥、し尿汚泥糞尿汚泥を処理するために混入される廃
活性炭を自己供給することが出来る。
According to the waste reclaiming plant according to the sixth aspect, the waste rubber tire contained in the waste is:
After being crushed by the crushing device, it is supplied to the carbonization device together with the deoxidizing material such as iron wire, and carbonized by dry distillation.The crushing device removes the magnetic material after the crushing by the magnetic separator. The waste activated carbon mixed for treating manure sludge can be supplied by itself.

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

【図1】本発明に係る廃棄物の無公害化再生処理プラン
トの再生処理工程のフローチャートである。
FIG. 1 is a flowchart of a regeneration treatment process of a waste decontamination regeneration treatment plant according to the present invention.

【図2】同プラントに組み込まれた破砕装置としてのス
クリュークラッシャーの平面図である。
FIG. 2 is a plan view of a screw crusher as a crushing device incorporated in the plant.

【図3】同プラントに組み込まれたロータセパレータの
正面図である。
FIG. 3 is a front view of a rotor separator incorporated in the plant.

【図4】上記ロータセパレータの選別ブロックの要部の
平面図である。
FIG. 4 is a plan view of a main part of a sorting block of the rotor separator.

【図5】同プラント用二次破砕装置としてのカッター型
粉砕機の縦断面図である。
FIG. 5 is a longitudinal sectional view of a cutter-type crusher as a secondary crusher for the plant.

【図6】他の二次破砕装置としてのスクリュークラッシ
ャーの断面図である。
FIG. 6 is a sectional view of a screw crusher as another secondary crushing device.

【図7】同アルミ選別機の側面図である。FIG. 7 is a side view of the aluminum sorting machine.

【図8】同プラント用破砕装置としての破袋機の縦断面
図である。
FIG. 8 is a longitudinal sectional view of a bag breaking machine as the crushing apparatus for the plant.

【図9】同破袋機の部分平面図である。FIG. 9 is a partial plan view of the bag breaking machine.

【図10】同固形化装置の断面図である。FIG. 10 is a sectional view of the solidifying device.

【図11】同固形化装置の水平断面図である。FIG. 11 is a horizontal sectional view of the solidifying device.

【図12】同炭化装置の斜視図である。FIG. 12 is a perspective view of the carbonizing device.

【符号の説明】[Explanation of symbols]

5、6、7、8 量供給機付きサイロ 10 破砕装置 20 選別装置(手選別コンベヤ) 25 選別装置(磁選機) 35 二次選別装置 40 アルミセパレータ 55 乾燥装置 75 風力選別装置 80 固形化装置 82A、82B 螺旋体 85 多孔板 90 炭化装置 91B スクラバー 5, 6, 7, 8 Silo with quantity feeder 10 Crusher 20 Sorting device (hand sorting conveyor) 25 Sorting device (magnetic separator) 35 Secondary sorting device 40 Aluminum separator 55 Drying device 75 Wind separator 80 Solidifying device 82A , 82B spiral body 85 perforated plate 90 carbonizing device 91B scrubber

───────────────────────────────────────────────────── フロントページの続き (51)Int.Cl.6 識別記号 FI C10L 5/46 B09B 3/00 302B 5/48 5/00 Q ──────────────────────────────────────────────────の Continued on the front page (51) Int.Cl. 6 Identification code FI C10L 5/46 B09B 3/00 302B 5/48 5/00 Q

Claims (6)

【特許請求の範囲】[Claims] 【請求項1】 各種のプラスチックを含む有機質系廃棄
物を破砕する破砕装置と、破砕された破砕物から有価物
を選別する選別装置と、有価物の除去後の破砕物の内プ
ラスチックとそれ以外の破砕屑を前者が70〜30重量
%、後者が30〜70重量%となるように供給され、螺
旋体によって送りをかけて撹拌混合しながら圧縮して1
20〜300℃に加熱し、練り合わせて流動可能状態に
し、この流動状態の中間生成物から多孔板を通して押し
出し成形して棒状や粒状の固形物を形成する固形化装置
と、固形物を乾留して炭化する炭化装置とから構成され
ており、上記炭化装置は、排気ガスの煙道に補助バーナ
又はアルカリ性水溶液を入れたスクラバーを備えている
ことを特徴とする廃棄物の無公害化再生処理プラント。
1. A crushing device for crushing organic waste containing various plastics, a sorting device for sorting valuable materials from the crushed crushed materials, a plastic crushed material from which valuable materials have been removed, Is supplied so that the former is 70 to 30% by weight and the latter is 30 to 70% by weight, and is compressed by being fed by a spiral while stirring and mixing.
Heating to 20 to 300 ° C., kneading to a flowable state, a solidifying device for forming a rod-like or granular solid by extruding the intermediate product in the flowing state through a perforated plate, and carbonizing the solid A carbonization device for carbonizing, wherein the carbonization device is provided with an auxiliary burner or a scrubber containing an alkaline aqueous solution in a flue of exhaust gas, and the plant for detoxification and regeneration of wastes.
【請求項2】 上記廃棄物に含まれる生ごみは、廃タイ
ヤ等から生成された廃活性炭と混合後に上記破砕装置に
送られ、破砕物は、上記炭化装置からの高温ガスを利用
した乾燥装置に送られる請求項1記載の再生処理プラン
ト。
2. The garbage contained in the waste is sent to the crushing device after being mixed with waste activated carbon generated from waste tires and the like, and the crushed material is dried by using a high-temperature gas from the carbonization device. The reprocessing plant according to claim 1, which is sent to a plant.
【請求項3】 上記廃棄物に含まれる粗大ごみや廃木材
は、破砕装置で破砕され、手選別コンベヤ上で破砕物か
ら磁選機で磁性物を、人手で有価金属、ビン、危険物を
選別し、残り破砕物は選別装置で土砂等の微小物が除去
され、残りの大中破砕物は二次破砕装置で粉砕後にアル
ミセパレータでアルミが除去され、分別装置で木屑チッ
プと廃プラスチックとがそれぞれ分別されてそれぞれ一
旦定量供給機付きサイロへ供給された後で上記固形化装
置へ供給される請求項1記載の再生処理プラント。
3. The oversized garbage and waste wood contained in the waste are crushed by a crusher, and the crushed material is separated from the crushed material by a magnetic separator using a magnetic separator, and valuable metals, bottles, and hazardous materials are separated by hand. The remaining crushed material is removed by a sorting device to remove fine matter such as earth and sand, and the remaining large and medium crushed material is crushed by a secondary crushing device and then aluminum is removed by an aluminum separator.The wood chips and waste plastic are separated by a separating device. 2. The regeneration treatment plant according to claim 1, wherein each of the fractions is separated and then supplied once to a silo with a fixed-quantity feeder, and then supplied to the solidifying device.
【請求項4】 上記廃棄物に含まれる廃プラスチック、
故紙及び若しくは紙屑は、破砕装置で破砕され、磁選機
で磁性物を選別後に二次破砕装置で粉砕され、風力選別
装置でダストが除去されてから廃プラ・紙屑用定量供給
機付きサイロへ一旦供給された後で上記固形化装置へ供
給される請求項1記載の再生処理プラント。
4. A waste plastic contained in the waste,
Waste paper and / or paper debris is crushed by a crusher, the magnetic material is separated by a magnetic separator, then crushed by a secondary crusher, dust is removed by a wind separator, and then once into a silo with a quantitative feeder for waste plastic and paper waste. The regeneration processing plant according to claim 1, wherein the supply is supplied to the solidifying device after the supply.
【請求項5】 上記廃棄物に含まれる下水汚泥やし尿汚
泥糞尿汚泥は、脱水装置で脱水後に破砕済み紙屑や廃タ
イヤ等から生成された廃活性炭と混合後に上記固形化装
置へ供給される請求項1記載の再生処理プラント。
5. The sewage sludge and night soil sludge and manure sludge contained in the waste are supplied to the solidifying device after being mixed with crushed paper waste or waste activated carbon generated from waste tires or the like after being dewatered by a dewatering device. Item 2. A regeneration plant according to Item 1.
【請求項6】 上記廃棄物に含まれる廃ゴムタイヤは、
破砕装置で破砕後に脱酸素材と共に上記炭化装置に供給
されて、乾留炭化され、破砕装置で破砕後に磁選機で磁
性物が除去される請求項1記載の再生処理プラント。
6. The waste rubber tire contained in the waste,
2. The regeneration treatment plant according to claim 1, wherein the crushing device is supplied to the carbonization device together with the deoxidized material after the crushing, and carbonized by dry distillation, and after the crushing device, the magnetic material is removed by a magnetic separator.
JP24098797A 1997-09-05 1997-09-05 Pollution-free regeneration treatment plant for waste Expired - Fee Related JP3278384B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
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Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
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JPH1177013A true JPH1177013A (en) 1999-03-23
JP3278384B2 JP3278384B2 (en) 2002-04-30

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JP2009540097A (en) * 2006-06-14 2009-11-19 トル−コール テクノロジー べー ヴェー Method of preparing solid fuel by roasting, solid fuel thus obtained and use of those fuels
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