JPH0691649A - Method and device for processing waste plastic - Google Patents

Method and device for processing waste plastic

Info

Publication number
JPH0691649A
JPH0691649A JP24756392A JP24756392A JPH0691649A JP H0691649 A JPH0691649 A JP H0691649A JP 24756392 A JP24756392 A JP 24756392A JP 24756392 A JP24756392 A JP 24756392A JP H0691649 A JPH0691649 A JP H0691649A
Authority
JP
Japan
Prior art keywords
waste plastic
oil
plastic
waste
gas
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Pending
Application number
JP24756392A
Other languages
Japanese (ja)
Inventor
Masayoshi Kubota
昌良 久保田
Ryokichi Yamada
良吉 山田
Harumi Matsuzaki
晴美 松崎
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.)
Hitachi Ltd
Original Assignee
Hitachi Ltd
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Hitachi Ltd filed Critical Hitachi Ltd
Priority to JP24756392A priority Critical patent/JPH0691649A/en
Publication of JPH0691649A publication Critical patent/JPH0691649A/en
Pending 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
    • 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

Landscapes

  • Processing Of Solid Wastes (AREA)
  • Manufacture Of Porous Articles, And Recovery And Treatment Of Waste Products (AREA)
  • Processing And Handling Of Plastics And Other Materials For Molding In General (AREA)
  • Separation, Recovery Or Treatment Of Waste Materials Containing Plastics (AREA)

Abstract

PURPOSE:To recycle light oil of high quality as a fuel by a method and device wherein cracked gas is suitably retrieved by supplying intake pressure and negative pressure to the inside of a heating furnace under a condition of melting temperature of waste plastic and the retrieve is performed by classifying into waste plastic of molten residue and kneaded matter generated due to caking of incinerated ashes. CONSTITUTION:Cracked gas is sucked, filtered by a gas-liquid separating filter pot 9a, cooled by a cooler 10 so as to change to oil, and returned to an oil separating tank 11 as oil. As for sucking and retrieving quantity of the cracked gas, constant sucking time is detected by a timer or oil quantity in the oil separating tank 11 is detected, and a suction fan 12 is controlled. The cracked gas which can not be changed to oil burns as a fuel at a heating furnace 16a so as to be a heating source. Separated oil is stored in an oil product tank as occasion demands as a replenishing fuel in the heating furnace. Molten residue of retrieved optional cracked gas opens a shielding damper 7, it is discharged being kneaded by a recovery screw feeder 8, retrieved into a cooling tank 18, crushed into optional size by a crusher so as to make soil.

Description

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

【0001】[0001]

【産業上の利用分野】本発明は廃棄物を処理して再利用
する方法に係り、特に、処理困難性廃棄物である廃棄プ
ラスチックのうち、ポリオレフィン系プラスチックから
有用な軽質油を適宜回収して再資源化するとともに、最
終処分として埋め立てされる焼却灰と前記廃棄プラスチ
ックの溶融残渣を粘結固化し、土壌として無公害化処理
する方法及び装置に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method for treating and reusing wastes, and in particular, it collects useful light oil from polyolefin plastics among waste plastics that are difficult to dispose of as appropriate. The present invention relates to a method and an apparatus for recycling and incinerating ash to be landfilled as final disposal and a molten residue of the waste plastic to be solidified and solidified to be pollution-free as soil.

【0002】[0002]

【従来の技術】近年、我国は経済の発展に従い生活が豊
かになり生活様式及び産業構造の多様化に伴い、ごみの
排出量が増大していると同時に、一般都市廃棄物及び産
業廃棄物の量,質が大きく変化してごみ処理問題を複雑
にしている。特に、プラスチックは食品パッケージ、各
種容器から家電品等に用途が急速に拡大して廃棄物とし
て多量に排出されるようになった。プラスチックは埋立
てしても腐らず、埋立て地の地盤が安定しない、焼却す
れば高温になり焼却炉を傷め有害ガスを排出するなど多
くの問題が指摘されている。このため、プラスチックの
処理に種々の処理技術が開発されている。例えば、溶融
固化再生利用,熱分解油化,高温溶融,溶融固化減容
化,焼却余熱回収利用などプラスチック単独あるいは混
合ごみを対象とした処理技術が研究及び開発されてい
る。これらの技術については(社)プラスチック処理促
進協会発行の「廃プラスチックの処理・資源化技術シス
テムガイドブック」(平成元年3月刊)に詳細に記載さ
れている。
2. Description of the Related Art In recent years, Japan has become more affluent with economic development and the diversification of lifestyles and industrial structures has led to an increase in the amount of waste generated. The quantity and quality change greatly, complicating the waste management problem. In particular, the use of plastics has expanded rapidly from food packages and various containers to home electric appliances, etc., and a large amount of plastics have been discharged as waste. Many problems have been pointed out, such as the fact that plastic does not rot even when it is landfilled, the ground in the landfill is not stable, and when incinerated it becomes hot and damages the incinerator and discharges harmful gases. Therefore, various processing techniques have been developed for processing plastics. For example, processing techniques for plastics alone or mixed wastes such as melt solidification recycling, pyrolysis oilification, high temperature melting, melt solidification volume reduction, incineration residual heat recovery utilization have been studied and developed. These technologies are described in detail in the "Technology Guidebook for Waste Plastic Processing and Resource Recycling Technology" published by Japan Plastics Processing Promotion Association (March 1989).

【0003】一方、我国のごみ処理の主流は焼却であ
り、自治体が収集する一般廃棄物のほとんどが焼却され
ている。埋立て地が少ないことから焼却により最大限に
減容化しているのが実情である。しかし、焼却すれば排
ガス,排水の処理あるいは焼却残渣の焼却灰は埋立てさ
れるが風による灰の飛散,雨水による流出及び灰に含ま
れる有害物質,重金属類等の溶出による二次公害等の危
険が懸念されている。
On the other hand, the mainstream of waste treatment in Japan is incineration, and most of the general waste collected by local governments is incinerated. Since there are few landfills, the actual situation is that the volume is reduced to the maximum by incineration. However, if incinerated, exhaust gas, wastewater treatment, or incinerated ash of the incineration residue is landfilled, but ash scattering by wind, runoff by rainwater and secondary pollution due to elution of harmful substances and heavy metals contained in ash, etc. There is concern about the danger.

【0004】いずれも最終処分は埋立てであるが、種々
の問題がある。加えるに、産業廃棄物の増大により埋立
て用地が逼迫し、しばしば不法投棄がされるなど社会問
題になっている。この様な状況のため、廃棄プラスチッ
ク処理に関する発明も多数公開されている。例えば、
「ごみ焼却灰固形物及びその製造方法」(特公平1− 2
54285号)、「廃棄物溶融処理方法」(特公昭57−74513
号公報)、「プラスチック廃棄物の処理方法」(特公
昭61−78847 号公報)など廃棄プラスチックと焼却灰と
の溶融処理、廃棄プラスチックからの油化に関する発明
もいくつか公開されている。しかし、これらの発明は油
化かプラスチックと焼却灰を溶融して成形固化物を製造
する方法に関するもので、両者を兼ね備えた視点での言
及はない。
Although the final disposal is landfill, there are various problems. In addition, the increasing amount of industrial waste has led to a tight landfill site, which often causes illegal dumping, which is a social problem. Due to this situation, many inventions relating to waste plastic processing have been published. For example,
"Waste Incinerated Ash Solids and Their Manufacturing Method" (Japanese Patent Publication No. 1-2
54285), "Waste melting treatment method" (Japanese Patent Publication No. 57-74513)
No.), “Plastic waste treatment method” (Japanese Patent Publication No. 61-78847), and several inventions relating to melting treatment of waste plastic and incineration ash and oilification from waste plastic have been disclosed. However, these inventions relate to a method for producing a molded solidified product by melting oil or plastic and incineration ash, and there is no reference from the viewpoint of having both of them.

【0005】[0005]

【発明が解決しようとする課題】上記廃棄プラスチック
及び焼却灰の処理には次のような課題がある。
The treatment of the waste plastic and incineration ash has the following problems.

【0006】処理困難性廃棄物としてのプラスチックの
排出量が近年増大し、種々の処理技術が開発されてい
る。処理技術は、加熱溶融し、減容化成型固形物として
再利用する方法があるが、技術傾向は溶融,分解ガスか
らの油化技術が主流のようである。
Difficulty in processing The amount of plastics discharged as waste has increased in recent years, and various processing techniques have been developed. As for the treatment technology, there is a method in which it is heated and melted and reused as a volume-reduced molded solid matter, but the technical trend seems to be the mainstream is oiling technology from melting and decomposition gas.

【0007】自治体では廃棄プラスチックを燃えるご
みと燃えないごみとするかは焼却炉及び埋立て地の状況
により対応しなければならず、課題となっている。
[0007] In municipalities, whether to dispose of waste plastic as burnable waste or non-burnable waste must be dealt with depending on the conditions of the incinerator and the landfill site, which is a problem.

【0008】廃棄プラスチックのまま埋立てると腐ら
ず、地盤が安定しない、嵩高のため埋立て地の不足を加
速させる。
Landfilling waste plastic as it is will not rot and the ground will not be stable, and the bulkiness will accelerate the shortage of landfill.

【0009】減容,成型固形物の処理はコスト高であ
り、再利用としての市場は小さく、最終的には焼却,埋
立てされる。
[0009] Volume reduction and processing of molded solids are expensive, the market for reuse is small, and they are finally incinerated or landfilled.

【0010】油化技術は回収した油がタール状とか油
質に問題があり、触媒による改質が開発されているが、
触媒の寿命などの開発課題がある。
[0010] In the oil technology, the recovered oil has problems such as tar and oil quality, and reforming with a catalyst has been developed.
There are development issues such as catalyst life.

【0011】プラスチック専焼はプラスチックが高カ
ロリのため燃やすと千数百度の高温になることから炉の
耐熱性が問題となる。
[0011] In the plastic baking, the heat resistance of the furnace becomes a problem because the temperature of the furnace becomes a few hundreds of degrees when burned because the plastic has a high calorie.

【0012】前述のようにごみ処理の主流は焼却である
が、処理量の増大に伴い、当然のことながら焼却灰も増
加する。その処分は主に埋立てであるが、 風により飛散,雨水で流出。
As described above, the mainstream of waste treatment is incineration, but as the amount of treatment increases, naturally, incineration ash also increases. The disposal is mainly landfill, but it is scattered by the wind and is discharged as rainwater.

【0013】焼却灰に含まれる有害物質や重金属類の
溶出による土壌及び地下水の汚染、 燃焼排ガスや排水に含まれる種々の無機,有機汚染物
による環境汚染。
Pollution of soil and groundwater by elution of harmful substances and heavy metals contained in incineration ash, environmental pollution by various inorganic and organic pollutants contained in combustion exhaust gas and wastewater.

【0014】の問題がある。そのため、処理技術は (a)コンクリート固化:水銀,シアン等の有害物質を埋
立てる固化技術として実用化されているが、セメントの
種類,混合比,混練方法、さらには成型方法等最適化が
必要であり、用途としてあまり多いと言えない。
There is a problem of. Therefore, the treatment technology is (a) solidification of concrete: it has been put to practical use as a solidification technology for burying harmful substances such as mercury and cyan, but it is necessary to optimize the type of cement, mixing ratio, kneading method, and molding method. Therefore, it cannot be said that there are many uses.

【0015】(b)灰溶融化:焼却灰を高温で溶融し、冷
却固化するもので有害物質なども固化物中に閉じ込めら
れ、セメントなど建築資材,道路建設の砂の代用など用
途は広い。溶融方法としては電気抵抗,電気アーク,電
気マイクロ波溶融法等があるが、灰を高温で溶融するた
め、例えば、消費電力が700〜1,000KWh/T
灰が必要となるなど、かなりコスト高となる。
(B) Ash melting: The incineration ash is melted at high temperature and cooled and solidified. Hazardous substances and the like are also trapped in the solidified material, and have a wide range of applications such as construction materials such as cement and substitution of sand for road construction. As a melting method, there are electric resistance, electric arc, electric microwave melting method, etc., but since ash is melted at a high temperature, for example, power consumption is 700 to 1,000 KWh / T.
The cost is considerably high, for example, ash is required.

【0016】本発明の目的は、処理困難性のプラスチッ
クと焼却灰を同時に処理し、プラスチックからは良質の
軽質油を回収し、プラスチック溶融残渣と焼却灰は粘結
固化させ、二次公害を抑制した土壌化にする方法及び装
置を提供することにある。
The object of the present invention is to treat difficult-to-treat plastic and incineration ash at the same time, recover good quality light oil from the plastic, and solidify the plastic melting residue and incineration ash to suppress secondary pollution. It is intended to provide a method and an apparatus for converting into soil.

【0017】[0017]

【課題を解決するための手段】本発明は、上記目的を達
成するため、プラスチックの溶融温度において、減圧・
強制吸気するとプラスチックからは軽質分の分解ガスが
発生することに着目することにより、公知の処理技術の
油化及び溶融処理の両技術の組合わせを可能とし、プラ
スチックからは良質の軽質油を適宜回収するとともに、
プラスチックの溶融残渣と焼却灰が混練した粘結固化物
を土壌として得るための方法及び装置を提供するもので
ある。
In order to achieve the above object, the present invention is to reduce the pressure at the melting temperature of plastics.
By paying attention to the fact that light decomposition gas is generated from plastic when forced intake is performed, it is possible to combine both known oil processing and melting processing technologies. With collecting
It is intended to provide a method and an apparatus for obtaining a solidified and solidified material obtained by kneading a molten residue of plastic and incinerated ash as soil.

【0018】これにより、良質の軽質油は燃料とするこ
とができ、再資源化が達成できる。また、プラスチック
の溶融残渣と無機質の焼却灰との粘結固化物は焼却灰中
の有害物質の溶出を大幅に抑制すると共に、プラスチッ
ク溶融残渣が一部炭化することから保水性に優れた土壌
として再利用できる。
As a result, good quality light oil can be used as a fuel, and recycling can be achieved. In addition, the caking solidified product of the molten residue of the plastic and the incinerated ash of the inorganic substance greatly suppresses the elution of harmful substances in the incinerated ash, and since the plastic molten residue partially carbonizes, it becomes a soil with excellent water retention. Can be reused.

【0019】[0019]

【作用】現状の廃棄プラスチックの油化システムは28
0〜340℃に加熱した溶融槽において、プラスチック
を溶融し、次いで熱分解槽に供給して400℃前後で熱
分解し、分解ガスを冷却・油化して油を回収する方式が
主流である。しかし、得られた油はワックスあるいはタ
ール状であるなど燃料として再使用するには問題があ
る。そのため、分解ガスを触媒により改質して軽質油に
する方法が提案されている(特公昭63−178195号,平2
−29492号)。
[Function] The current oil recycling system for waste plastic is 28
In a melting tank heated to 0 to 340 ° C., a method in which plastic is melted, then supplied to a thermal decomposition tank and thermally decomposed at around 400 ° C., and the decomposed gas is cooled and oiled to recover oil is the mainstream. However, the obtained oil is in the form of wax or tar, and there is a problem in reusing it as a fuel. Therefore, a method has been proposed in which cracked gas is reformed with a catalyst to produce light oil (Japanese Patent Publication No. 178195/1988).
-29492).

【0020】本発明は、廃棄プラスチックの熱分解油化
の基礎実験においてプラスチックを溶融し、容器内を吸
気,減圧すると分解ガスの発生が溶融温度で容易に起こ
ることに着目してなされたものである。実験では、廃冷
蔵庫の使用材(ポリスチレン:PS)を10〜20mm片
に破砕して供試した。PSは250〜280℃で溶融し
液状となり、300℃前後で分解ガスの発生が起こる
が、容器内を吸気・減圧すると同温度条件下で分解ガス
の発生が活発となる。また、吸気した分解ガスを冷却器
を介して油化する経時変化を観察すると、吸気初期の発
生ガスを油化した時の油性状は淡褐色で流動性が高い。
吸気をさらに継続すると得られる油は次第に色が褐色か
ら黒色になると同時に粘性が高くなる。これは、吸気に
より軽質分が優先的にガス化するものと考えられ、油化
初期の油は良質の軽質油であり、触媒による改質を必要
としない。一方、プラスチックと焼却灰を混合した時の
プラスチック溶融残渣と焼却灰との混練物は、焼却灰が
溶融プラスチックにより粘結されているため、冷却後任
意のサイズに破砕して土壌として利用できる。ここで、
注意すべきは過剰に分解ガスを発生させると溶融残渣は
粘性が高くなると同時に焼却灰の粘結度が落ちる。実験
では、プラスチックと焼却灰の重量割合1:0.3 で供
試プラスチック重量に対して油化回収量は30〜50w
t%程度が適当であった。このようにして得られた土壌
の模式図を図3に示すが、粒径2〜3mmに破砕すると埋
立てしてもプラスチック及び焼却灰それぞれ単独では問
題であった雨風による流出,飛散さらには埋立て地の地
盤安定の問題が解消できる。特に、焼却灰から溶出する
有害物質等がプラスチック溶融残渣で粘結されることに
より大幅に抑制される。さらに、溶融分解を適宜制御す
ることで溶融残渣の大部分が炭化し、ポーラスな保水性
及び焼却灰の親水性を併せ持つ良質の土壌として利用で
きる。すなわち、本発明は廃プラスチックからは良質の
軽質油のみを回収して再資源化し、溶融残渣と焼却灰の
混練物を改良土壌として利用するところにある。
The present invention has been made in the basic experiment of thermal decomposition and oilification of waste plastics by paying attention to the fact that when plastics are melted and the inside of the container is sucked and decompressed, decomposition gas is easily generated at the melting temperature. is there. In the experiment, the material (polystyrene: PS) used in the waste refrigerator was crushed into 10 to 20 mm pieces for use. PS melts at 250 to 280 ° C. and becomes liquid, and decomposition gas is generated at around 300 ° C. However, when suction and decompression are performed in the container, generation of decomposition gas becomes active under the same temperature condition. Further, observing the change over time in which the inhaled decomposed gas is liquefied through the cooler, the oily property when the generated gas in the early stage of inhalation is oiled is light brown and has high fluidity.
When the intake is further continued, the oil obtained gradually changes from brown to black in color and becomes more viscous. It is considered that the light fraction is preferentially gasified by intake air, and the oil in the early stage of oiling is a good quality light oil and does not require reforming by a catalyst. On the other hand, the kneaded product of the molten plastic residue and the incinerated ash when the plastic and the incinerated ash are mixed, since the incinerated ash is bound by the molten plastic, it can be crushed to an arbitrary size after cooling and used as soil. here,
It should be noted that when the decomposition gas is excessively generated, the viscosity of the molten residue becomes high, and at the same time, the caking degree of the incineration ash decreases. In the experiment, the weight ratio of plastic to incinerated ash was 1: 0.3, and the recovery amount of oil was 30 to 50w based on the weight of the plastic sample.
About t% was suitable. A schematic diagram of the soil obtained in this way is shown in Fig. 3. When crushed to a particle size of 2 to 3 mm, plastic and incineration ash were problems when they were used alone, but runoff, scattering, and landfill The problem of ground stability of the ground can be solved. In particular, harmful substances and the like eluted from the incineration ash are significantly suppressed by being bound by the plastic melting residue. Furthermore, by controlling melt decomposition appropriately, most of the melt residue is carbonized, and it can be used as a high-quality soil having both porous water retention and hydrophilicity of incineration ash. That is, the present invention is to recover only high-quality light oil from waste plastic and recycle it, and use the kneaded product of the molten residue and incinerated ash as the improved soil.

【0021】[0021]

【実施例】以下、図を用いて説明する。Embodiments will be described below with reference to the drawings.

【0022】図1は本発明の一実施例の装置構成を示
す。プラスチック片1と焼却灰2を混合して予熱する混
合ホッパ3,混合物3aを供給する供給スクリューフィ
ーダ4と密閉炉6及び混練物6aを排出するための回収
スクリューフィーダ8が主な装置構成で、それぞれのス
クリューフィーダ入口側に遮蔽ダンパ5,7及び油化装
置,排ガス処理装置が付設する。
FIG. 1 shows a device configuration of an embodiment of the present invention. The mixing hopper 3 for mixing and preheating the plastic piece 1 and the incineration ash 2, the supply screw feeder 4 for supplying the mixture 3a, the closed furnace 6 and the recovery screw feeder 8 for discharging the kneaded material 6a are the main device configurations. Shielding dampers 5 and 7, an oiling device, and an exhaust gas treatment device are attached to the inlet side of each screw feeder.

【0023】図示していないが破砕工程で任意サイズに
破砕された熱可塑性プラスチック片1と焼却灰2(同図
示せず)の混合重量割合を1:0.1〜0.7、好ましく
は1:0.2〜0.3の割合でホッパ3に投入し、200
〜250℃で予熱しながら撹拌羽根3aで撹拌・混合す
るとプラスチックが軟化し、表面が溶解し焼却灰2が付
着しただんご状態になる。供給原料のプラスチックに塩
化ビニール系樹脂(PVC)が混入した場合、PVCは
溶融点が低く、250℃の予熱による撹拌・混合の段階
でほとんどが分解・ガス化し、そのガスは混合ホッパ3
上部から気液分離フィルタ9aで同伴する不純物を分離
し、塩素を含むガスをオフガス洗浄装置17に導入し
て、水洗浄により塩素を溶解吸収させたのち排気する。
その後、遮蔽ダンパ5を開にし、だんご状プラスチック
を供給スクリューフィーダ4により混練しながら密閉炉
6に供給する。したがって、フィーダ,密閉炉での焼却
灰の飛散は少ない。密閉炉6は250〜400℃、好ま
しくは300℃前後に加熱し、溶融したプラスチックが
焼却灰とよく混合するように撹拌し、該密閉炉内を吸引
ファン12で吸引して負圧にする。これにより、発生し
た分解ガスは吸引され気液分離用フィルタポット9aで
濾過され、クーラ10で冷却・油化され油として油水分
離槽11に回収される。分解ガスの吸引・回収量は一定
の吸引時間をタイマで、あるいは油水分離槽11での油
量を検出し吸引ファン12を制御する。油化しない分解
ガスは加熱炉16aで燃料として燃焼し、加熱源にす
る。分離された油は加熱炉の補充燃料の他、適宜油製品
タンクにストックする。一方、任意の分解ガスが回収さ
れた溶融残渣は遮蔽ダンパ7を開にし、回収スクリュー
フィーダ8により混練しながら排出し、冷却水槽18に
回収して、破砕機で任意サイズに破砕し土壌とする。図
示しないが回収スクリューフィーダ終端部に成形金具を
設けて成形固形物にすることも可能である。本発明は、
バッチ処理を前提に述べたが、ホッパ3での撹拌混合及
びフィーダ4での供給状態より連続運転も可能である
が、減圧・吸引していることを考慮すれば、一定量ずつ
処理する間欠連続運転が好ましい。
Although not shown, the mixing weight ratio of the thermoplastic plastic pieces 1 and the incineration ash 2 (not shown) crushed to an arbitrary size in the crushing step is 1: 0.1 to 0.7, preferably 1 : 200 to 200 in the hopper 3 at a ratio of 0.2 to 0.3
When the mixture is stirred and mixed by the stirring blade 3a while preheating at ˜250 ° C., the plastic is softened, the surface is melted, and the incinerated ash 2 is attached to the dumpling. When vinyl chloride resin (PVC) is mixed in the plastic as the feedstock, PVC has a low melting point, and most of it decomposes and gasifies at the stage of stirring and mixing by preheating at 250 ° C, and the gas is mixed in the hopper 3
Impurities entrained by the gas-liquid separation filter 9a are separated from the upper part, a gas containing chlorine is introduced into the off-gas cleaning device 17, and chlorine is dissolved and absorbed by water cleaning and then exhausted.
After that, the shielding damper 5 is opened, and the dumpling-shaped plastic is supplied to the closed furnace 6 while being kneaded by the supply screw feeder 4. Therefore, scattering of incinerated ash in the feeder and closed furnace is small. The closed furnace 6 is heated to 250 to 400 ° C., preferably around 300 ° C., stirred so that the molten plastic mixes well with the incinerated ash, and the inside of the closed furnace is sucked by the suction fan 12 to a negative pressure. As a result, the generated decomposition gas is sucked, filtered by the gas-liquid separation filter pot 9a, cooled and oiled by the cooler 10, and collected as oil in the oil / water separation tank 11. The amount of suction / recovery of the decomposed gas is controlled by a timer for a certain suction time or by detecting the amount of oil in the oil / water separation tank 11 to control the suction fan 12. The decomposed gas that is not liquefied burns as fuel in the heating furnace 16a and is used as a heating source. The separated oil is stocked in the oil product tank as well as the refueling fuel for the heating furnace. On the other hand, the melted residue in which any decomposed gas is collected is opened by opening the shielding damper 7, discharged while being kneaded by the collecting screw feeder 8, collected in the cooling water tank 18, and crushed to an arbitrary size by a crusher to be soil. . Although not shown, it is also possible to provide a molded metal piece at the end of the recovery screw feeder to form a molded solid material. The present invention is
Although it was described on the premise of batch processing, continuous operation is possible depending on the agitating and mixing in the hopper 3 and the supply state in the feeder 4, but in consideration of the fact that the pressure is reduced and suctioned, intermittent continuous processing is performed by a fixed amount. Driving is preferred.

【0024】図2はスクリューフィーダに温度勾配をつ
け混練・土壌化を主目的とした装置構成図を示す。ホッ
パ16aにプラスチック片1と焼却灰2を定量供給し、
混合する。遮断ダンパ5,7を開放し、混合物をスクリ
ューフィーダ4でホッパ16b供給するが、スクリューフ
ィーダ4は加熱器20で200〜250℃に加熱制御
し、供給する過程で加熱・混練する。この時、スクリュ
ーフィーダ4の排出口において、実施例のように塩化ビ
ニール系樹脂混入により発生する塩素ガスの除去をフィ
ルタポット9b及びガス洗浄装置15を介して行い、排
気する。一定量を加熱供給すると、次いで遮断ダンパ7
を閉じ、吸引ファン12で吸気を行い、加熱器21,2
2で280〜320℃に加熱してスクリューフィーダ8
により混練物を供給し、ここで発生する分解ガスを吸気
してフィルタポット9aで濾過後、クーラ10で冷却・
油化する。混練物はホッパ16cに貯留され、適宜遮断
ダンパ7aを開き、冷却・破砕して土壌とする。
FIG. 2 is a diagram showing the construction of an apparatus whose main purpose is to knead and soil the screw feeder with a temperature gradient. A fixed amount of plastic pieces 1 and incinerated ash 2 are supplied to the hopper 16a,
Mix. The shut-off dampers 5 and 7 are opened, and the mixture is fed by the screw feeder 4 to the hopper 16b. The screw feeder 4 is heated and controlled at 200 to 250 ° C. by the heater 20, and is heated and kneaded in the feeding process. At this time, at the discharge port of the screw feeder 4, the chlorine gas generated by mixing the vinyl chloride resin is removed through the filter pot 9b and the gas cleaning device 15 and exhausted as in the embodiment. When a certain amount of heat is supplied, then the shut-off damper 7
Closed, suction air is taken in by the suction fan 12, and the heaters 21, 2 are closed.
2 and heat to 280-320 ℃, screw feeder 8
To supply a kneaded product, suck the decomposed gas generated here, filter through the filter pot 9a, and cool with the cooler 10.
Liquefy. The kneaded material is stored in the hopper 16c, and the shut-off damper 7a is appropriately opened to cool and crush it to obtain soil.

【0025】[0025]

【発明の効果】本発明によれば、以下の効果がある。The present invention has the following effects.

【0026】(1)産業廃棄物のなかの処理困難性である
プラスチック及び焼却灰を同時に処理できる。
(1) Plastics and incinerated ash, which are difficult to dispose of in industrial waste, can be treated at the same time.

【0027】(2)プラスチックからは良質の軽質油を回
収して、燃料として再資源化できる。 (3)溶融残渣の混練物は土壌として利用でき、埋立てし
た場合には有害物質の溶出が少なく二次公害などの環境
汚染が抑制できる。
(2) Good quality light oil can be recovered from plastics and recycled as fuel. (3) The kneaded product of the molten residue can be used as soil, and when it is landfilled, toxic substances are less eluted, and environmental pollution such as secondary pollution can be suppressed.

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

【図1】本発明の一実施例である装置の系統図。FIG. 1 is a system diagram of an apparatus that is an embodiment of the present invention.

【図2】本発明の他の実施例である装置の系統図。FIG. 2 is a system diagram of an apparatus that is another embodiment of the present invention.

【図3】炭化土壌の説明図。FIG. 3 is an explanatory view of carbonized soil.

【符号の説明】[Explanation of symbols]

1…廃棄プラスチック、2…焼却灰、3…混合ホッパ、
4…供給フィーダ、5,7…遮断ダンパ、6…密閉炉、
8…回収フィーダ、9a,9b…フィルタポット、10
…クーラ、11…油水分離槽、12…吸引ファン、13
…油タンク、14…加熱炉、15…オフガス洗浄装置。
1 ... Waste plastic, 2 ... Incinerated ash, 3 ... Mixing hopper,
4 ... Supply feeder, 5, 7 ... Shutoff damper, 6 ... Closed furnace,
8 ... Collection feeder, 9a, 9b ... Filter pot, 10
... Cooler, 11 ... Oil-water separation tank, 12 ... Suction fan, 13
... oil tank, 14 ... heating furnace, 15 ... off-gas cleaning device.

Claims (8)

【特許請求の範囲】[Claims] 【請求項1】廃棄プラスチックと焼却灰を混合して加熱
炉中で加熱し、前記廃棄プラスチックを溶融処理する方
法において、前記加熱炉内を前記廃棄プラスチックの溶
融温度条件下で吸気・負圧下にして適宜分解ガスを回収
し、溶融残渣の前記廃棄プラスチックと前記焼却灰が粘
結した混練物とに分離して回収することを特徴とする廃
棄プラスチックの処理方法。
1. A method of melting waste plastic by mixing waste plastic and incinerated ash and heating the mixture in a heating furnace, wherein the inside of the heating furnace is subjected to suction / negative pressure under the melting temperature condition of the waste plastic. A method for treating waste plastics, characterized in that the decomposed gas is appropriately recovered by means of the method, and the waste plastics as a molten residue and the kneaded material in which the incinerated ash are caking are separated and recovered.
【請求項2】請求項1において、前記加熱炉は密閉式と
し、分解ガスは炉外に吸気して冷却・液化し、油として
回収する廃棄プラスチックの処理装置。
2. The processing apparatus for waste plastic according to claim 1, wherein the heating furnace is a closed type, and the decomposed gas is sucked outside the furnace to be cooled / liquefied and recovered as oil.
【請求項3】請求項1において、前記溶融プラスチック
と前記焼却灰が粘結固化した混練物は、密閉炉からスク
リューフィーダによる搬送装置で混練して排出・回収
し、適宜冷却・破砕し土壌として再利用する廃棄プラス
チックの処理装置。
3. The kneaded material obtained by caking and solidifying the molten plastic and the incinerated ash according to claim 1, is kneaded from a closed furnace by a conveying device using a screw feeder, discharged and collected, and appropriately cooled and crushed to obtain soil. Equipment for processing waste plastic for reuse.
【請求項4】請求項1において、混合ホッパで廃棄プラ
スチックと焼却灰を予熱し、スクリューフィーダにより
密閉炉に供給する工程と混合物を加熱し、前記廃棄プラ
スチックを溶融して前記焼却灰と混練する工程及び前記
廃棄プラスチックの分解ガスを強制的に吸気し、冷却し
て油化する工程及び残留溶融プラスチックと前記焼却灰
との粘結混練物を前記スクリューフィーダにより前記密
閉炉から排出する工程から構成されるプラスチックの処
理システム。
4. The process according to claim 1, wherein waste plastic and incineration ash are preheated by a mixing hopper, and a step of supplying the mixture to a closed furnace by a screw feeder and heating the mixture, the waste plastic is melted and kneaded with the incineration ash. Steps and steps of forcibly inhaling the decomposition gas of the waste plastic, cooling and oiling, and discharging the caking kneaded product of the residual molten plastic and the incinerated ash from the closed furnace by the screw feeder Plastic processing system.
【請求項5】請求項1において、前記加熱炉から減圧,
負圧下における前記分解ガスの回収を、一定の吸気時間
もしくは冷却した油化量から検出することにより制御す
る廃棄プラスチックの処理システム。
5. The reduced pressure from the heating furnace according to claim 1,
A treatment system for waste plastics, which controls recovery of the decomposed gas under negative pressure by detecting from a fixed intake time or a cooled oilification amount.
【請求項6】請求項1において、前記密閉炉における加
熱溶融温度が250〜400℃である廃棄プラスチック
の処理方法。
6. The method for treating waste plastic according to claim 1, wherein the heating and melting temperature in the closed furnace is 250 to 400 ° C.
【請求項7】請求項1または3において、前記廃棄プラ
スチックと焼却灰の混合重量割合を1:0.1〜0.7と
する廃棄プラスチックの処理方法。
7. The method for treating waste plastic according to claim 1, wherein the mixing weight ratio of the waste plastic and incineration ash is 1: 0.1 to 0.7.
【請求項8】請求項1において、前記加熱炉内を不活性
ガスで一定圧力の加圧下にし、前記廃棄プラスチック溶
融温度条件で分解ガスの発生による過剰ガスを適宜回収
し、溶融残渣の前記廃棄プラスチックと前記焼却灰が粘
結した前記混練物とに分離して回収する廃棄プラスチッ
クの処理方法。
8. The method according to claim 1, wherein the inside of the heating furnace is pressurized with an inert gas at a constant pressure, and excess gas due to generation of decomposition gas under the melting temperature condition of the waste plastic is appropriately recovered, and the waste residue is discarded. A method for treating waste plastic, in which the plastic and the kneaded material in which the incinerated ash is caking are separated and collected.
JP24756392A 1992-09-17 1992-09-17 Method and device for processing waste plastic Pending JPH0691649A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP24756392A JPH0691649A (en) 1992-09-17 1992-09-17 Method and device for processing waste plastic

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP24756392A JPH0691649A (en) 1992-09-17 1992-09-17 Method and device for processing waste plastic

Publications (1)

Publication Number Publication Date
JPH0691649A true JPH0691649A (en) 1994-04-05

Family

ID=17165360

Family Applications (1)

Application Number Title Priority Date Filing Date
JP24756392A Pending JPH0691649A (en) 1992-09-17 1992-09-17 Method and device for processing waste plastic

Country Status (1)

Country Link
JP (1) JPH0691649A (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN114131786A (en) * 2021-10-29 2022-03-04 深圳万宏业科技有限公司 Recovery and extraction system for waste composite material

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN114131786A (en) * 2021-10-29 2022-03-04 深圳万宏业科技有限公司 Recovery and extraction system for waste composite material

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