JP2002003860A - Melting and oilifying apparatus for waste plastics - Google Patents
Melting and oilifying apparatus for waste plasticsInfo
- Publication number
- JP2002003860A JP2002003860A JP2000182746A JP2000182746A JP2002003860A JP 2002003860 A JP2002003860 A JP 2002003860A JP 2000182746 A JP2000182746 A JP 2000182746A JP 2000182746 A JP2000182746 A JP 2000182746A JP 2002003860 A JP2002003860 A JP 2002003860A
- Authority
- JP
- Japan
- Prior art keywords
- waste plastics
- solvent oil
- melting
- oil
- solvent
- 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
Links
- 239000002699 waste material Substances 0.000 title claims abstract description 97
- 239000004033 plastic Substances 0.000 title claims abstract description 89
- 229920003023 plastic Polymers 0.000 title claims abstract description 89
- 238000002844 melting Methods 0.000 title claims abstract description 33
- 230000008018 melting Effects 0.000 title claims abstract description 33
- 239000002904 solvent Substances 0.000 claims abstract description 69
- 238000010438 heat treatment Methods 0.000 claims abstract description 25
- 239000007788 liquid Substances 0.000 claims abstract description 22
- 238000000926 separation method Methods 0.000 claims abstract description 18
- 239000007789 gas Substances 0.000 claims description 35
- 238000002485 combustion reaction Methods 0.000 claims description 25
- 239000000356 contaminant Substances 0.000 claims description 22
- 238000001816 cooling Methods 0.000 claims description 11
- 239000004014 plasticizer Substances 0.000 claims description 7
- 239000000112 cooling gas Substances 0.000 claims 1
- 239000000446 fuel Substances 0.000 abstract description 10
- 239000003921 oil Substances 0.000 description 84
- 235000019198 oils Nutrition 0.000 description 84
- VEXZGXHMUGYJMC-UHFFFAOYSA-N Hydrochloric acid Chemical compound Cl VEXZGXHMUGYJMC-UHFFFAOYSA-N 0.000 description 11
- 239000002994 raw material Substances 0.000 description 9
- 238000004090 dissolution Methods 0.000 description 8
- 238000001514 detection method Methods 0.000 description 6
- 239000000295 fuel oil Substances 0.000 description 6
- KZBUYRJDOAKODT-UHFFFAOYSA-N Chlorine Chemical compound ClCl KZBUYRJDOAKODT-UHFFFAOYSA-N 0.000 description 5
- 238000001914 filtration Methods 0.000 description 5
- DKAGJZJALZXOOV-UHFFFAOYSA-N hydrate;hydrochloride Chemical compound O.Cl DKAGJZJALZXOOV-UHFFFAOYSA-N 0.000 description 5
- CURLTUGMZLYLDI-UHFFFAOYSA-N Carbon dioxide Chemical compound O=C=O CURLTUGMZLYLDI-UHFFFAOYSA-N 0.000 description 4
- 239000000155 melt Substances 0.000 description 4
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 4
- 238000004821 distillation Methods 0.000 description 3
- 239000000463 material Substances 0.000 description 3
- 239000002480 mineral oil Substances 0.000 description 3
- -1 polypropylene Polymers 0.000 description 3
- 238000004064 recycling Methods 0.000 description 3
- 239000000126 substance Substances 0.000 description 3
- 235000015112 vegetable and seed oil Nutrition 0.000 description 3
- 239000008158 vegetable oil Substances 0.000 description 3
- 239000001569 carbon dioxide Substances 0.000 description 2
- 229910002092 carbon dioxide Inorganic materials 0.000 description 2
- 239000000460 chlorine Substances 0.000 description 2
- 238000010411 cooking Methods 0.000 description 2
- 238000002309 gasification Methods 0.000 description 2
- 238000005470 impregnation Methods 0.000 description 2
- 238000000034 method Methods 0.000 description 2
- 239000010813 municipal solid waste Substances 0.000 description 2
- 230000002265 prevention Effects 0.000 description 2
- 238000000197 pyrolysis Methods 0.000 description 2
- 239000007787 solid Substances 0.000 description 2
- 102100033040 Carbonic anhydrase 12 Human genes 0.000 description 1
- 102100033041 Carbonic anhydrase 13 Human genes 0.000 description 1
- ZAMOUSCENKQFHK-UHFFFAOYSA-N Chlorine atom Chemical compound [Cl] ZAMOUSCENKQFHK-UHFFFAOYSA-N 0.000 description 1
- 101000867855 Homo sapiens Carbonic anhydrase 12 Proteins 0.000 description 1
- 101000867860 Homo sapiens Carbonic anhydrase 13 Proteins 0.000 description 1
- 101100219325 Phaseolus vulgaris BA13 gene Proteins 0.000 description 1
- 239000004698 Polyethylene Substances 0.000 description 1
- 239000004743 Polypropylene Substances 0.000 description 1
- 239000004793 Polystyrene Substances 0.000 description 1
- 238000009835 boiling Methods 0.000 description 1
- 229910052801 chlorine Inorganic materials 0.000 description 1
- 230000006835 compression Effects 0.000 description 1
- 238000007906 compression Methods 0.000 description 1
- 238000011109 contamination Methods 0.000 description 1
- 230000000382 dechlorinating effect Effects 0.000 description 1
- 238000006298 dechlorination reaction Methods 0.000 description 1
- 230000018044 dehydration Effects 0.000 description 1
- 238000006297 dehydration reaction Methods 0.000 description 1
- 230000001877 deodorizing effect Effects 0.000 description 1
- 230000029087 digestion Effects 0.000 description 1
- 150000002013 dioxins Chemical class 0.000 description 1
- 239000008157 edible vegetable oil Substances 0.000 description 1
- 230000000694 effects Effects 0.000 description 1
- 230000007613 environmental effect Effects 0.000 description 1
- 238000003912 environmental pollution Methods 0.000 description 1
- 238000001704 evaporation Methods 0.000 description 1
- 230000008020 evaporation Effects 0.000 description 1
- 239000012530 fluid Substances 0.000 description 1
- 239000002737 fuel gas Substances 0.000 description 1
- 239000010687 lubricating oil Substances 0.000 description 1
- 150000001247 metal acetylides Chemical class 0.000 description 1
- 235000010446 mineral oil Nutrition 0.000 description 1
- 239000010811 mineral waste Substances 0.000 description 1
- 230000001590 oxidative effect Effects 0.000 description 1
- 238000004806 packaging method and process Methods 0.000 description 1
- 229920000728 polyester Polymers 0.000 description 1
- 229920000573 polyethylene Polymers 0.000 description 1
- 229920001155 polypropylene Polymers 0.000 description 1
- 229920002223 polystyrene Polymers 0.000 description 1
- 238000004537 pulping Methods 0.000 description 1
- 238000000746 purification Methods 0.000 description 1
- 238000007670 refining Methods 0.000 description 1
- 238000002407 reforming Methods 0.000 description 1
- 231100000331 toxic Toxicity 0.000 description 1
- 230000002588 toxic effect Effects 0.000 description 1
- 239000002918 waste heat Substances 0.000 description 1
- 239000013585 weight reducing agent Substances 0.000 description 1
Classifications
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B29—WORKING OF PLASTICS; WORKING OF SUBSTANCES IN A PLASTIC STATE IN GENERAL
- B29B—PREPARATION OR PRETREATMENT OF THE MATERIAL TO BE SHAPED; MAKING GRANULES OR PREFORMS; RECOVERY OF PLASTICS OR OTHER CONSTITUENTS OF WASTE MATERIAL CONTAINING PLASTICS
- B29B17/00—Recovery of plastics or other constituents of waste material containing plastics
- B29B17/04—Disintegrating plastics, e.g. by milling
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B29—WORKING OF PLASTICS; WORKING OF SUBSTANCES IN A PLASTIC STATE IN GENERAL
- B29B—PREPARATION OR PRETREATMENT OF THE MATERIAL TO BE SHAPED; MAKING GRANULES OR PREFORMS; RECOVERY OF PLASTICS OR OTHER CONSTITUENTS OF WASTE MATERIAL CONTAINING PLASTICS
- B29B17/00—Recovery of plastics or other constituents of waste material containing plastics
- B29B17/04—Disintegrating plastics, e.g. by milling
- B29B2017/0424—Specific disintegrating techniques; devices therefor
- B29B2017/0496—Pyrolysing the materials
-
- Y—GENERAL 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
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02E—REDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
- Y02E50/00—Technologies for the production of fuel of non-fossil origin
- Y02E50/30—Fuel from waste, e.g. synthetic alcohol or diesel
-
- Y—GENERAL 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
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W30/00—Technologies for solid waste management
- Y02W30/50—Reuse, recycling or recovery technologies
- Y02W30/62—Plastics recycling; Rubber recycling
Landscapes
- Engineering & Computer Science (AREA)
- Environmental & Geological Engineering (AREA)
- Mechanical Engineering (AREA)
- Separation, Recovery Or Treatment Of Waste Materials Containing Plastics (AREA)
- Production Of Liquid Hydrocarbon Mixture For Refining Petroleum (AREA)
- Gasification And Melting Of Waste (AREA)
- Treating Waste Gases (AREA)
- Processing Of Solid Wastes (AREA)
Abstract
Description
【0001】[0001]
【発明の属する技術分野】本発明は、廃プラスチック類
や、都市塵芥等の廃棄物に含まれる不溶性挟雑物が混入
した廃プラスチック類(本明細書において、「廃プラス
チック類」という。)を効率よく溶解させるとともに、
可燃性の不溶性挟雑物の脱水・脱塩素や発熱量の増進を
行い、燃料化するようにした廃プラスチック類の溶融油
化装置に関するものである。BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to waste plastics and waste plastics mixed with insoluble contaminants contained in wastes such as municipal waste (hereinafter referred to as "waste plastics"). While dissolving efficiently,
The present invention relates to a melting and oiling apparatus for waste plastics, which decomposes combustible insoluble contaminants by dehydrating / dechlorinating them and increasing the calorific value to convert them into fuel.
【0002】[0002]
【従来の技術】近年、環境の保全と資源の保護を目的と
して、再生資源利用促進法の制定に引き続き、容器包装
リサイクル法の制定と法整備がなされ、資源の循環型リ
サイクル社会が進行している。このような状況の中で、
都市塵芥の焼却処理においては、廃プラスチック類の分
別や、高い湿性による焼却物の発熱量低下を原因とした
燃焼困難が問題化している。リサイクルができない廃プ
ラスチック類を焼却処理すれば、有害ガスの発生のみな
らず、猛毒性を有するダイオキシン類の生成と飛散によ
る環境の汚染原因となり、また、埋め立て処分すれば分
解や減量が行われず、埋め立て処分場の狭窄化の原因と
なる等、廃プラスチック類の処理・処分には難問が山積
している。2. Description of the Related Art In recent years, the Containers and Packaging Recycling Law has been enacted and enacted following the enactment of the Recycling Resource Utilization Act for the purpose of environmental protection and resource protection. I have. In such a situation,
In the incineration treatment of municipal garbage, the difficulty of separating waste plastics and the difficulty of burning due to a decrease in the calorific value of incinerated materials due to high humidity have become problems. Incineration of waste plastics, which cannot be recycled, not only generates harmful gases, but also causes environmental pollution due to the generation and scattering of highly toxic dioxins. There are many difficulties in the treatment and disposal of waste plastics, such as the narrowing of landfills.
【0003】一方、廃プラスチック類を油化して燃料油
としたり、再蒸留精製して工業原料化するリサイクル手
法が脚光を浴びるようになった。この廃プラスチック類
の溶融油化装置としては、都市塵芥等の廃棄物を廃プラ
スチック類と不溶解性夾雑物とに分別し、分別した廃プ
ラスチック類のみを溶融・蒸解釜に充填して密閉した
後、この溶融・蒸解釜を外部から熱し、内部に充填した
廃プラスチック類を加熱して溶融・蒸解し、発生した蒸
解ガスを冷却器に導き、冷却して液化させ分解油を得
る、いわゆる加熱溶融・蒸解装置が多く用いられてい
る。また、希にではあるが、ガス化炉内燃料の下部燃焼
熱で、上部堆積燃料を熱分解させて可燃性分解ガスを得
る自燃式乾溜ガス化焼焼炉を用い、この自燃式乾溜ガス
化焼焼炉で発生した可燃性ガスを冷却器に導いて冷却
し、液化して分解油を得る自燃式乾溜ガス化燃焼方式の
油化装置も用いられている。[0003] On the other hand, a recycling technique for converting waste plastics into fuel oil by converting the waste plastics into fuel oil or re-distilling and refining to make industrial raw materials has come into the spotlight. This waste plastics melting and oiling device separates waste such as municipal waste into waste plastics and insoluble contaminants, and only the separated waste plastics are filled into a melting and digester and sealed. After that, the melting and digesting furnace is heated from the outside, the waste plastics filled inside are heated and melted and digested, and the generated cooking gas is guided to a cooler, cooled and liquefied to obtain cracked oil, so-called heating. Melting / pulping equipment is often used. In addition, although rare, the lower combustion heat of the fuel in the gasifier causes the upper deposited fuel to be thermally decomposed to obtain a flammable cracked gas. A self-combustion dry-distillation gasification type oil liquefaction apparatus in which combustible gas generated in a baking furnace is guided to a cooler to be cooled and liquefied to obtain cracked oil is also used.
【0004】[0004]
【発明が解決しようとする課題】しかしながら、上記従
来の溶融油化装置においては、第1には、溶融・蒸解釜
の壁面が外部よりバーナー等の燃焼火炎で加熱されるこ
とから、蒸解釜壁面が過熱し、蒸解釜内の接液面に炭化
物が生成して付着する焦げ付き現象が起り、この付着物
が壁面の伝熱を阻害し、運用の時間経過と共に溶融・蒸
解の効率が悪くなるという問題があった。また、第2に
は、上記炭化物の付着による保温効果により、溶融・蒸
解釜の壁面が過熱し、釜を構成する材質の劣化が進行す
るという問題がある。However, in the above-mentioned conventional melter / oiler, firstly, the wall surface of the melting and digesting furnace is heated from outside by a combustion flame such as a burner, so that the wall surface of the digester is Is overheated, causing charring to occur and stick to the liquid contact surface in the digester, and this deposit impedes the heat transfer to the wall, and the efficiency of melting and digestion deteriorates with the lapse of operation. There was a problem. Secondly, there is a problem that the wall surface of the melting and digesting vessel is overheated due to the heat retention effect due to the adhesion of the carbide, and the material constituting the cooking vessel is deteriorated.
【0005】さらに、第3には、不溶性挟雑物が混入す
る場合は、これらが溶融・蒸解釜の壁面を保温・断熱す
ることから、上記第1、第2の問題点の原因となり、蒸
解原料として採用できないという問題があった。また、
減量のみを目的に溶融を行った場合、溶融物を溶融釜か
ら取り出して、溶融物に含れる挟雑物を分離しようとし
ても、取り出した溶融物の粘性が高く、しかも温度が降
下するとさらに粘性が高くなることから、固液の分離が
困難であり、最悪の場合には固液分離装置に凝固・固着
して装置の破損原因となるため、このような不溶性挟雑
物を含む廃プラスチック類を原料として使用することが
できないという問題があった。Third, when insoluble contaminants are mixed, they insulate and insulate the walls of the melting and digesting furnace, causing the first and second problems described above. There was a problem that it could not be used as a raw material. Also,
When melting is performed for the purpose of weight reduction only, the melt is taken out of the melter and the contaminants contained in the melt are separated. Is high, so solid-liquid separation is difficult. In the worst case, waste plastics containing such insoluble contaminants may coagulate and stick to the solid-liquid separation device, causing damage to the device. There is a problem that cannot be used as a raw material.
【0006】また、自燃式乾溜ガス化燃焼方式の油化装
置は、原料の一部を燃焼させて消費するために、回収す
る生成油の歩留まりが悪いという欠点を有している。[0006] Further, the self-combustion type dry distillation gasification combustion type liquefaction apparatus has a disadvantage that the yield of recovered product oil is low because a part of the raw material is burned and consumed.
【0007】本発明は、上記従来の廃プラスチック類の
油化装置が有する問題点に鑑み、分別された廃プラスチ
ック類のみならず、廃プラスチック類と不溶解性夾雑物
の分別が困難で、かつ高い湿性がある都市塵芥等の廃棄
物に含まれるような廃プラスチック類でも、効率よく溶
解して固液分離することができ、さらに、可燃性挟雑物
の脱水・脱塩素と発熱量の増進を行い、燃料化できるよ
うにした廃プラスチック類の溶融油化装置を提供するこ
とを目的とする。The present invention has been made in view of the above problems of the conventional waste plastic oiling apparatus, and it is difficult to separate not only waste plastics but also waste plastics and insoluble contaminants. Waste plastics, such as those contained in high-moisture municipal waste, can be efficiently dissolved and separated into solids and liquids. It is intended to provide a molten plasticizer for waste plastics which can be converted to fuel.
【0008】[0008]
【課題を解決するための手段】上記目的を達成するた
め、本発明の廃プラスチック類の溶融油化装置は、廃プ
ラスチック類を溶融することにより油化する廃プラスチ
ック類の溶融油化装置において、廃プラスチック類と溶
媒油とを収容する溶解槽と、該溶解槽の溶媒油を加温し
て廃プラスチック類を溶解させる溶媒油加温装置と、廃
プラスチック類が溶解した溶媒油から不溶性挟雑物を分
離する固液分離装置とを備えたことを特徴とする。Means for Solving the Problems In order to achieve the above object, a molten plasticizer for waste plastics according to the present invention is a molten plasticizer for waste plastics, which is made by melting waste plastics. A dissolving tank containing waste plastics and solvent oil, a solvent oil heating device for heating the solvent oil in the dissolving tank to dissolve waste plastics, and an insoluble contaminant from the solvent oil in which the waste plastics are dissolved A solid-liquid separation device for separating an object.
【0009】この廃プラスチック類の溶融油化装置で
は、溶媒油を介して廃プラスチック類を加熱することに
より、廃プラスチック類を溶媒油に溶解させることか
ら、炭化物による溶解槽の内壁面への焦げ付き現象やこ
の焦げ付き現象による伝熱障害もなく、廃プラスチック
類の溶解を効率よく進行させることができる。そして、
廃プラスチック類が溶解した溶媒油は、粘性が低くて流
動性がよく、温度が降下しても流動性が保持されること
から、固液分離装置での不溶性挟雑物の分離・脱油を良
好に行うことができる。さらに、分離された不溶性挟雑
物は、加温された溶媒油によって脱塩素と脱水が行われ
るとともに、廃プラスチック類が溶解した溶媒油の含浸
によって改質されることから、発熱量の高い無害な燃料
として使用することができる。また、分離した廃プラス
チック類が溶解した溶媒油は、そのまま燃料油として使
用できるとともに、さらに蒸留精製することにより、工
業原料油として再利用することができる。In this apparatus for melting waste plastics, the waste plastics are dissolved in the solvent oil by heating the waste plastics through the solvent oil. The dissolution of the waste plastics can proceed efficiently without any phenomenon or heat transfer obstruction due to this scorching phenomenon. And
Solvent oil in which waste plastics are dissolved has low viscosity and good fluidity, and since the fluidity is maintained even when the temperature drops, separation and deoiling of insoluble contaminants in a solid-liquid separation device is required. Can be performed well. Furthermore, the separated insoluble contaminants are dechlorinated and dehydrated by the heated solvent oil, and are reformed by impregnation with the solvent oil in which the waste plastics are dissolved. It can be used as a fuel. Further, the solvent oil in which the separated waste plastics are dissolved can be used as a fuel oil as it is, and can be reused as an industrial raw material oil by further purifying it by distillation.
【0010】この場合において、溶媒油加温装置に、溶
解槽の溶媒油を外部で循環させて加温する方式のものを
使用することができる。In this case, a system in which the solvent oil in the dissolving tank is circulated outside and heated may be used for the solvent oil heating device.
【0011】これにより、炭化物による溶解槽の内壁面
への焦げ付きをさらに効果的に防止し、廃プラスチック
類の溶解をより効率的に進行させることができる。[0011] This makes it possible to more effectively prevent charring from sticking to the inner wall surface of the dissolving tank, and to dissolve waste plastics more efficiently.
【0012】また、廃プラスチック類の溶解時に生成す
るガスを導入する燃焼炉と、該燃焼炉から排出されたガ
スを冷却する冷却装置とを設けることができる。Further, a combustion furnace for introducing gas generated when the waste plastics are melted, and a cooling device for cooling the gas discharged from the combustion furnace can be provided.
【0013】これにより、廃プラスチック類の溶解時に
生成する有機性ガスを燃焼させて酸化・脱臭を行うとと
もに、ガス中に含まれる塩素ガスを、冷却装置で復水と
なる水蒸気と化合・結合させ、塩酸水として回収するこ
とができる。[0013] Thus, the organic gas generated when the waste plastics are dissolved is burned to oxidize and deodorize, and the chlorine gas contained in the gas is combined and combined with the steam which is condensed by the cooling device. Can be recovered as aqueous hydrochloric acid.
【0014】[0014]
【発明の実施の形態】以下、本発明の廃プラスチック類
の溶融油化装置の実施の形態を図面に基づいて説明す
る。DETAILED DESCRIPTION OF THE PREFERRED EMBODIMENTS An embodiment of a waste plasticizer for melting and oiling waste plastics according to the present invention will be described below with reference to the drawings.
【0015】図1に、本発明の廃プラスチック類の溶融
油化装置の一実施例を示す。本実施例の溶融油化装置
は、廃プラスチック類と溶媒油とを収容する溶解槽7
と、溶解槽7の溶媒油を外部で循環させて加温すること
により、該溶解槽7で廃プラスチック類を溶解させる溶
媒油加温装置19と、廃プラスチック類が溶解した溶媒
油から不溶性挟雑物を分離する固液分離装置8とを備え
ている。FIG. 1 shows an embodiment of the apparatus for melt-oiling waste plastics according to the present invention. The melting and oiling apparatus of the present embodiment has a melting tank 7 for storing waste plastics and solvent oil.
By circulating the solvent oil in the dissolving tank 7 outside and heating it, a solvent oil heating device 19 for dissolving the waste plastics in the dissolving tank 7 and an insoluble sandwich from the solvent oil in which the waste plastics are dissolved. A solid-liquid separator 8 for separating miscellaneous substances.
【0016】溶媒油としては、食用油等の植物油や機械
用潤滑油等の鉱物油、又はこれら植物油や鉱物油の廃油
等の、常温で液体の油を使用することができる。そし
て、この溶媒油を溶媒油加温装置によって180〜28
0℃に加温することにより、例えば、1〜2時間で廃プ
ラスチック類を溶媒油に溶解させる。溶解槽7に収容す
る溶媒油と廃プラスチック類の比率は、溶媒油60〜7
0重量%に対し、廃プラスチック類30〜40重量%以
下となるように制御することが適当である。なお、廃プ
ラスチック類としては、例えば、ポリプロピレン、ポリ
エチレン、ポリスチレン、ポリエステル等があり、これ
を溶媒油に溶解させて油化を行うことができる。As the solvent oil, vegetable oils such as edible oils, mineral oils such as mechanical lubricating oils, and oils which are liquid at normal temperature such as waste oils of these vegetable oils and mineral oils can be used. Then, the solvent oil is heated to 180 to 28 by a solvent oil heating device.
By heating to 0 ° C., for example, the waste plastics are dissolved in the solvent oil in 1 to 2 hours. The ratio of solvent oil to waste plastics contained in the dissolution tank 7 is 60 to 7
It is appropriate to control waste plastics to be 30 to 40% by weight or less with respect to 0% by weight. The waste plastics include, for example, polypropylene, polyethylene, polystyrene, polyester, and the like, which can be dissolved in a solvent oil to make oil.
【0017】すなわち、本実施例の廃プラスチック類の
溶融油化装置では、先ず、廃プラスチック類を溶解槽7
に適量投入し、原料投入口1を密閉した後、別設した溶
媒油貯槽13に貯留する溶媒油を、溶媒油供給口2から
溶解槽7に移送して溶解槽7を満たす。この場合、溶解
槽7内の溶媒油面の高さは、溶解槽7に設けたレベル検
出器15の信号により、溶媒油の移送ポンプ14を駆動
又は停止させることによって制御される。なお、溶媒油
は、溶媒油貯槽13側で予め予熱したものも使用するこ
とができる。That is, in the waste plastics melting and oiling apparatus of this embodiment, first, waste plastics are melted in the melting tank 7.
After the raw material introduction port 1 is closed, the solvent oil stored in the separately provided solvent oil storage tank 13 is transferred from the solvent oil supply port 2 to the dissolution tank 7 to fill the dissolution tank 7. In this case, the height of the solvent oil level in the dissolution tank 7 is controlled by driving or stopping the solvent oil transfer pump 14 based on a signal from the level detector 15 provided in the dissolution tank 7. The solvent oil may be preheated on the solvent oil storage tank 13 side.
【0018】溶解槽7内の溶媒油は、この溶解槽7に設
けた温油戻り口4から取り出して、温油戻り口4の下流
側に設けた濾過装置17で異物を除去した後、さらに下
流側に設けた循環ポンプ18を経由し、溶媒油加温装置
19に移送されて加温され、溶解槽7に設けた温油送り
口5から溶解槽7内に送り込まれる。この場合、溶融槽
7内の溶媒油は、廃プラスチック類の溶融が完了するま
で、溶解槽7、濾過装置17、循環ポンプ18、溶媒油
加温装置19、溶解槽7の循環ラインで循環させる。The solvent oil in the dissolving tank 7 is taken out from the hot oil return port 4 provided in the dissolving tank 7, and after the foreign matter is removed by a filtering device 17 provided downstream of the hot oil return port 4, the solvent oil is further removed. The solvent is transferred to a solvent oil heating device 19 via a circulation pump 18 provided on the downstream side, heated and sent into the dissolving tank 7 from the hot oil feed port 5 provided in the dissolving tank 7. In this case, the solvent oil in the melting tank 7 is circulated through the melting tank 7, the filtering device 17, the circulation pump 18, the solvent oil heating device 19, and the circulation line of the melting tank 7 until the melting of the waste plastics is completed. .
【0019】溶解槽7内の溶媒油の温度は、溶解槽7に
設けた温度検出調節器16で検出する信号により、溶媒
油加温装置19での溶媒油の加温状況が制御され、温度
検出調節器16に予め設定した温度に保たれる。溶媒油
加温装置19の熱源としては、燃料油又は燃料ガスの燃
焼熱、電熱、廃熱ガス、臨界ガス(超臨界流体)等、任
意の熱源を使用することができる。The temperature of the solvent oil in the dissolving tank 7 is controlled by a signal detected by a temperature detection controller 16 provided in the dissolving tank 7 to control the heating state of the solvent oil in the solvent oil heating device 19. The temperature is kept at a preset value in the detection controller 16. As a heat source of the solvent oil heating device 19, any heat source such as combustion heat of fuel oil or fuel gas, electric heat, waste heat gas, and critical gas (supercritical fluid) can be used.
【0020】溶解槽7内の廃プラスチック類は、加温さ
れた溶媒油に溶解して溶媒油との合成油となるが、この
場合、廃プラスチック類を溶媒油を介して加熱し、特
に、本実施例では溶解槽7の壁面を直接加熱しない循環
加熱方式であるため、炭化物による溶解槽7の内壁面へ
の焦げ付き現象やこの焦げ付き現象による伝熱障害もな
く、効率よく廃プラスチック類の溶解が進行する。The waste plastics in the dissolving tank 7 are dissolved in the heated solvent oil to become a synthetic oil with the solvent oil. In this case, the waste plastics are heated through the solvent oil, In this embodiment, since the circulation heating method does not directly heat the wall surface of the melting tank 7, there is no scorching phenomenon on the inner wall surface of the melting tank 7 due to carbides and no heat transfer obstruction due to the scorching phenomenon, and the waste plastics can be efficiently dissolved. Progresses.
【0021】一方、廃プラスチック類が溶解する際に
は、塩素や低沸点物質が気化して有機性ガスとなり、ま
た、不溶性挟雑物中の水分は、加温された溶媒油で加熱
され、蒸発して水蒸気となり、その結果、有機性ガスと
水蒸気の混合ガスが生成される。この有機性ガスと水蒸
気の混合ガスは、溶解槽7上部の蒸発ガス出口3から取
り出され、蒸発ガス出口3の下流に設けた逆火防止装置
20を経由して、バーナー22を設けたさらに下流の燃
焼炉21に導かれる。燃焼炉21に導かれた混合ガス
は、800.℃以上の高温で有機性ガスが燃焼され、酸化・
脱臭される。この場合、燃焼炉21内の温度は、燃焼炉
21の出口に設けられた温度検出調節器23で検出する
信号でバーナー22の燃焼を制御することにより、温度
検出調節器23に予め設定した800.℃以上の温度に保た
れる。On the other hand, when the waste plastics are dissolved, chlorine and low-boiling substances are vaporized to become an organic gas, and the water in the insoluble contaminants is heated by a heated solvent oil, It evaporates to steam, and as a result, a mixed gas of organic gas and steam is generated. The mixed gas of the organic gas and the steam is taken out from the evaporative gas outlet 3 at the upper part of the dissolving tank 7, passes through the flashback prevention device 20 provided downstream of the evaporative gas outlet 3, and further downstream with the burner 22. To the combustion furnace 21. The mixed gas led to the combustion furnace 21 is burned at a high temperature of 800.degree.
It is deodorized. In this case, the temperature in the combustion furnace 21 is controlled by the signal detected by the temperature detection controller 23 provided at the outlet of the combustion furnace 21 to control the combustion of the burner 22, and the temperature in the temperature detection controller 23 is set in advance. Maintained at a temperature of.
【0022】また、混合ガス中に含まれる塩酸及び塩素
ガスは、燃焼炉21の燃焼熱で高温の塩素ガスとなり、
燃焼排ガスと混合して燃焼炉21より排出される。この
排ガスは、燃焼炉21の下流側の冷却装置24に導か
れ、冷却された後液化されるが、燃焼排ガス中の塩素ガ
スは、冷却により復水となる水蒸気と化合・結合し、液
化して塩酸水となる。また、炭酸ガスを主成分とする燃
焼排ガスは、冷却されても液化することなく気体のまま
となる。Hydrochloric acid and chlorine gas contained in the mixed gas are converted into high-temperature chlorine gas by the heat of combustion in the combustion furnace 21.
It is mixed with the combustion exhaust gas and discharged from the combustion furnace 21. This exhaust gas is guided to a cooling device 24 on the downstream side of the combustion furnace 21 and is cooled and liquefied. The chlorine gas in the combustion exhaust gas is combined and combined with water vapor which is condensed by cooling, and is liquefied. Into hydrochloric acid. Further, the combustion exhaust gas containing carbon dioxide as a main component remains as a gas without being liquefied even when cooled.
【0023】液化した塩酸水と炭酸ガスを主成分とする
気体は、冷却装置24の下流側に設けた汽水分離器25
に導かれて塩酸水と気体とに分離され、塩酸水は、塩酸
水貯槽28に収容され、また、分離された気体は、無害
な排ガスとして排風機26を経由して排気塔27から大
気中に排出される。The liquefied hydrochloric acid and the gas mainly composed of carbon dioxide gas are supplied to a brackish water separator 25 provided downstream of the cooling device 24.
The hydrochloric acid is separated into hydrochloric acid water and gas by the air, and the hydrochloric acid water is stored in a hydrochloric acid water storage tank 28, and the separated gas is discharged as harmless exhaust gas from the exhaust tower 27 via the exhaust fan 26 into the atmosphere. Is discharged.
【0024】他方、溶解槽7での廃プラスチック類の溶
解が完了した時点で、溶媒油の加温と循環ラインを停止
させ、溶解槽7の底部に設けた溶解物排出弁6を開く。
そして、溶解物排出弁6の下流側の固液分離装置8に、
廃プラスチック類が溶解した合成油と不溶性挟雑物とが
混合した溶解物を移送する。固液分離装置8に移送され
た溶解物は、合成油と不溶性挟雑物とに分離され、合成
油は、固液分離装置8の下流側の濾過装置9で濾過され
た後、濾過装置9の下流側に設けたポンプ10を経由し
て、合成油貯槽11に収容される。On the other hand, when the dissolving of the waste plastics in the dissolving tank 7 is completed, the heating of the solvent oil and the circulation line are stopped, and the melt discharge valve 6 provided at the bottom of the dissolving tank 7 is opened.
Then, the solid-liquid separation device 8 downstream of the melt discharge valve 6
The dissolved material in which the synthetic oil in which the waste plastics are dissolved and the insoluble contaminants are mixed is transferred. The dissolved matter transferred to the solid-liquid separation device 8 is separated into synthetic oil and insoluble contaminants. The synthetic oil is filtered by a filtration device 9 downstream of the solid-liquid separation device 8 and then filtered. Is stored in a synthetic oil storage tank 11 via a pump 10 provided on the downstream side.
【0025】また、固液分離装置で合成油から分離・脱
油された不溶性挟雑物は、固液分離装置8の下流側の夾
雑物箱12に収容される。この場合、合成油は、植物油
又は鉱物油と廃プラスチック類とで合成されたものであ
るため、粘性が低くて流動性がよく、なおかつ温度が降
下しても流動性が保持されることから、固液分離装置8
での合成油と不溶性挟雑物の分離・脱油を良好に行うこ
とができる。なお、固液分離装置8には、遠心力式分離
器や圧縮脱油式分離器、あるいは真空式脱油器を使用す
ることができる。The insoluble contaminants separated and deoiled from the synthetic oil in the solid-liquid separation device are stored in a contaminant box 12 on the downstream side of the solid-liquid separation device 8. In this case, since the synthetic oil is synthesized from vegetable oil or mineral oil and waste plastics, it has low viscosity and good fluidity, and since the fluidity is maintained even when the temperature drops, Solid-liquid separator 8
Separation and deoiling of synthetic oils and insoluble contaminants can be performed satisfactorily. The solid-liquid separator 8 may be a centrifugal separator, a compression deoiler, or a vacuum deoiler.
【0026】固液分離装置8で分離された可燃性の不溶
性挟雑物は、溶解槽7での廃プラスチック類の溶解の際
に、脱塩素と脱水が行われ、さらに合成油の含浸があり
改質されている結果、発熱量も高く燃料として燃焼させ
ても有害成分が発生する心配もなく、分離形状のまま、
又は成形加工して無害で良好な燃料として使用すること
ができる。また、分離・回収した合成油はそのまま燃料
油として使用できるのみならず、再蒸留精製することに
より、工業原料油として再利用することが可能である。The flammable insoluble contaminants separated by the solid-liquid separation device 8 are dechlorinated and dehydrated when the waste plastics are dissolved in the dissolving tank 7, and further impregnated with synthetic oil. As a result of reforming, the calorific value is high and there is no risk of generating harmful components even if burned as fuel,
Alternatively, it can be molded and used as a harmless and good fuel. Further, the separated and recovered synthetic oil can be used not only as a fuel oil as it is, but also can be reused as an industrial raw material oil by re-distillation and purification.
【0027】以上、本実施例では、溶媒油加温装置19
を、溶解槽7の溶媒油を外部で循環させて加温するよう
に構成したが、この溶媒油加温装置19を、溶解槽7を
直接加温するように構成することも可能である。As described above, in the present embodiment, the solvent oil heating device 19
Is heated by circulating the solvent oil in the dissolving tank 7 outside, but the solvent oil heating device 19 may be configured to directly heat the dissolving tank 7.
【0028】[0028]
【発明の効果】本発明の廃プラスチック類の溶融油化装
置によれば、溶媒油を介して廃プラスチック類を加熱す
ることにより、廃プラスチック類を溶媒油に溶解させる
ことから、炭化物による溶解槽の内壁面への焦げ付き現
象やこの焦げ付き現象による伝熱障害もなく、廃プラス
チック類の溶解を効率よく進行させることができる。そ
して、廃プラスチック類が溶解した溶媒油は、粘性が低
くて流動性がよく、温度が降下しても流動性が保持され
ることから、固液分離装置での不溶性挟雑物の分離・脱
油を良好に行うことができる。さらに、分離された不溶
性挟雑物は、加温された溶媒油によって脱塩素と脱水が
行われるとともに、廃プラスチック類が溶解した溶媒油
の含浸によって改質されることから、発熱量の高い無害
な燃料として使用することができる。また、分離した廃
プラスチック類が溶解した溶媒油は、そのまま燃料油と
して使用できるとともに、さらに蒸留精製することによ
り、工業原料油として再利用することができる。そし
て、これにより、分別された廃プラスチック類のみなら
ず、廃プラスチック類と不溶解性夾雑物の分別が困難
で、かつ高い湿性がある都市塵芥等の廃棄物に含まれる
ような廃プラスチック類でも、効率よく溶解して固液分
離することができ、さらに、可燃性挟雑物の脱水・脱塩
素と発熱量の増進を行い、燃料化及び廃プラスチック類
の再利用を効率的に促進することができる。According to the molten plasticizer for waste plastics of the present invention, the waste plastics are dissolved in the solvent oil by heating the waste plastics through the solvent oil. There is no scorching phenomenon on the inner wall surface and no heat transfer obstruction due to this scoring phenomenon, so that the dissolution of waste plastics can proceed efficiently. The solvent oil in which the waste plastics are dissolved has low viscosity and good fluidity, and since the fluidity is maintained even when the temperature drops, the separation and removal of insoluble contaminants in the solid-liquid separation device is performed. Oil can be performed well. Furthermore, the separated insoluble contaminants are dechlorinated and dehydrated by the heated solvent oil, and are reformed by impregnation with the solvent oil in which the waste plastics are dissolved. It can be used as a fuel. Further, the solvent oil in which the separated waste plastics are dissolved can be used as a fuel oil as it is, and can be reused as an industrial raw material oil by further purifying it by distillation. And by this, not only the separated waste plastics but also the waste plastics which are difficult to separate from the waste plastics and the insoluble contaminants and are included in the waste such as the highly humid municipal garbage. To efficiently dissolve and separate solids and liquids, and to promote dehydration and dechlorination of combustible contaminants and increase the calorific value to promote efficient use of fuel and reuse of waste plastics. Can be.
【0029】また、溶媒油加温装置に、溶解槽の溶媒油
を外部で循環させて加温する方式のものを使用すること
により、炭化物による溶解槽の内壁面への焦げ付きをさ
らに効果的に防止し、廃プラスチック類の溶解をより効
率的に進行させることができる。Further, by using a solvent oil heating device which circulates the solvent oil of the dissolving tank outside and heats it, the charring on the inner wall surface of the dissolving tank by the carbide can be more effectively achieved. It is possible to prevent waste plastics from dissolving more efficiently.
【0030】さらに、廃プラスチック類の溶解時に生成
するガスを導入する燃焼炉と、該燃焼炉から排出された
ガスを冷却する冷却装置とを設けることにより、廃プラ
スチック類の溶解時に生成する有機性ガスを燃焼させて
酸化・脱臭を行うとともに、ガス中に含まれる塩素ガス
を、冷却装置で復水となる水蒸気と化合・結合させ、塩
酸水として回収することができる。Further, by providing a combustion furnace for introducing a gas generated when the waste plastics are melted, and a cooling device for cooling the gas discharged from the combustion furnace, the organic furnace generated when the waste plastics are melted is provided. In addition to burning and oxidizing and deodorizing the gas, chlorine gas contained in the gas is combined and combined with water vapor to be condensed by a cooling device, and can be recovered as hydrochloric acid water.
【図1】本発明の廃プラスチック類の溶融油化装置の一
実施例を示す説明図である。FIG. 1 is an explanatory view showing one embodiment of a molten plasticizer for waste plastics of the present invention.
1 原料投入口 2 溶媒油供給口 3 蒸発ガス出口 4 温油戻り口 5 温油送り口 6 溶解物排出弁 7 溶解槽 8 固液分離装置 9 濾過装置 10 ポンプ 11 合成油貯槽 12 挟雑物箱 13 溶媒油貯槽 14 移送ポンプ 15 レベル検出器 16 温度検出調節器 17 濾過装置 18 循環ポンプ 19 溶媒油加温装置 20 逆火防止装置 21 燃焼炉 22 バーナー 23 温度検出調節器 24 冷却装置 25 汽水分離器 26 排風機 27 排気塔 28 塩酸水貯槽 DESCRIPTION OF SYMBOLS 1 Raw material input port 2 Solvent oil supply port 3 Evaporation gas outlet 4 Hot oil return port 5 Hot oil feed port 6 Dissolved substance discharge valve 7 Dissolution tank 8 Solid-liquid separation device 9 Filtration device 10 Pump 11 Synthetic oil storage tank 12 Contamination box DESCRIPTION OF SYMBOLS 13 Solvent oil storage tank 14 Transfer pump 15 Level detector 16 Temperature detection controller 17 Filtration device 18 Circulation pump 19 Solvent oil heating device 20 Flashback prevention device 21 Combustion furnace 22 Burner 23 Temperature detection controller 24 Cooling device 25 Steam separator 26 exhaust fan 27 exhaust tower 28 hydrochloric acid water storage tank
───────────────────────────────────────────────────── フロントページの続き (51)Int.Cl.7 識別記号 FI テーマコート゛(参考) C08J 11/20 B01D 53/34 134B F23G 5/00 ZAB B09B 3/00 ZAB 115 303E 7/12 ZAB Fターム(参考) 3K061 AA18 AB02 AC13 BA06 DA01 DA17 4D002 AA19 AA40 AC10 BA02 BA05 BA13 DA35 EA05 4D004 AA07 AA46 AC04 BA03 CA13 CA29 CA47 CA48 CB04 CC04 4F301 AA13 AA14 AA15 AA25 CA09 CA12 CA24 CA43 CA53 CA64 CA65 4H029 CA05 CA12 CA16 ──────────────────────────────────────────────────続 き Continued on the front page (51) Int.Cl. 7 Identification symbol FI Theme coat ゛ (Reference) C08J 11/20 B01D 53/34 134B F23G 5/00 ZAB B09B 3/00 ZAB 115 303E 7/12 ZAB F term (Reference) 3K061 AA18 AB02 AC13 BA06 DA01 DA17 4D002 AA19 AA40 AC10 BA02 BA05 BA13 DA35 EA05 4D004 AA07 AA46 AC04 BA03 CA13 CA29 CA47 CA48 CB04 CC04 4F301 AA13 AA14 AA15 AA25 CA09 CA12 CA24 CA05 4
Claims (3)
油化する廃プラスチック類の溶融油化装置において、廃
プラスチック類と溶媒油とを収容する溶解槽と、該溶解
槽の溶媒油を加温して廃プラスチック類を溶解させる溶
媒油加温装置と、廃プラスチック類が溶解した溶媒油か
ら不溶性挟雑物を分離する固液分離装置とを備えたこと
を特徴とする廃プラスチック類の溶融油化装置。1. A waste plastics melting and oiling apparatus for converting waste plastics into oil by melting the waste plastics, comprising: a melting tank containing waste plastics and a solvent oil; and heating the solvent oil in the melting tank. -Oil melting of waste plastics, comprising: a solvent oil heating device for dissolving waste plastics by heating; and a solid-liquid separation device for separating insoluble contaminants from the solvent oil in which the waste plastics are dissolved. apparatus.
部で循環させて加温することを特徴とする請求項1記載
の廃プラスチック類の溶融油化装置。2. The molten plasticizer for waste plastics according to claim 1, wherein the solvent oil heater circulates the solvent oil in the dissolving tank externally to heat the solvent.
スを導入する燃焼炉と、該燃焼炉から排出されたガスを
冷却する冷却装置とを設けたことを特徴とする請求項1
又は2記載の廃プラスチック類の溶融油化装置。3. A combustion furnace for introducing gas generated when waste plastics are melted, and a cooling device for cooling gas discharged from the combustion furnace are provided.
Or a melting and oiling apparatus for waste plastics according to 2.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP2000182746A JP2002003860A (en) | 2000-06-19 | 2000-06-19 | Melting and oilifying apparatus for waste plastics |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP2000182746A JP2002003860A (en) | 2000-06-19 | 2000-06-19 | Melting and oilifying apparatus for waste plastics |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| JP2002003860A true JP2002003860A (en) | 2002-01-09 |
Family
ID=18683447
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP2000182746A Pending JP2002003860A (en) | 2000-06-19 | 2000-06-19 | Melting and oilifying apparatus for waste plastics |
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| Country | Link |
|---|---|
| JP (1) | JP2002003860A (en) |
Cited By (7)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP2003112153A (en) * | 2001-07-31 | 2003-04-15 | Tokyo Erutekku Kk | Method for recycling waste |
| JP2007252986A (en) * | 2006-03-20 | 2007-10-04 | Minoru Sasaki | Moving body for treating discharged material |
| JP2007302039A (en) * | 2006-05-09 | 2007-11-22 | Minoru Sasaki | Vehicle for processing waste |
| CN106287733A (en) * | 2016-08-11 | 2017-01-04 | 赛能杰高新技术股份有限公司 | One way of life waste disposal method |
| JP2017165967A (en) * | 2016-03-17 | 2017-09-21 | エッジオイルエナジー株式会社 | Method for generating recycled fuel oil from waste synthetic resin |
| WO2022032858A1 (en) * | 2020-08-14 | 2022-02-17 | 中国华能集团清洁能源技术研究院有限公司 | System and process for cleaning flue gas with low-temperature pentane and simultaneously performing desulfurization and decarbonization |
| WO2023211390A1 (en) | 2022-04-26 | 2023-11-02 | Sabanci Universitesi | A method of recovery of polyolefins from waste materials, and polyolefin product so recovered |
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| JPH05345894A (en) * | 1992-06-16 | 1993-12-27 | Toyo Seikan Kaisha Ltd | Method for chemically reusing plastics |
| JPH07233373A (en) * | 1994-02-24 | 1995-09-05 | Hitachi Zosen Corp | Waste plastic processing equipment |
| JPH1160796A (en) * | 1997-08-14 | 1999-03-05 | Chiyoda Corp | Waste plastic processing method and equipment |
| JP2000153522A (en) * | 1998-11-21 | 2000-06-06 | Nkk Corp | Treatment of chlorine-containing resins |
Cited By (8)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP2003112153A (en) * | 2001-07-31 | 2003-04-15 | Tokyo Erutekku Kk | Method for recycling waste |
| JP2007252986A (en) * | 2006-03-20 | 2007-10-04 | Minoru Sasaki | Moving body for treating discharged material |
| JP2007302039A (en) * | 2006-05-09 | 2007-11-22 | Minoru Sasaki | Vehicle for processing waste |
| JP2017165967A (en) * | 2016-03-17 | 2017-09-21 | エッジオイルエナジー株式会社 | Method for generating recycled fuel oil from waste synthetic resin |
| CN106287733A (en) * | 2016-08-11 | 2017-01-04 | 赛能杰高新技术股份有限公司 | One way of life waste disposal method |
| WO2022032858A1 (en) * | 2020-08-14 | 2022-02-17 | 中国华能集团清洁能源技术研究院有限公司 | System and process for cleaning flue gas with low-temperature pentane and simultaneously performing desulfurization and decarbonization |
| WO2023211390A1 (en) | 2022-04-26 | 2023-11-02 | Sabanci Universitesi | A method of recovery of polyolefins from waste materials, and polyolefin product so recovered |
| JP2025518629A (en) * | 2022-04-26 | 2025-06-18 | サバンチ ウニベルシテシ | Process for recovering polyolefins from waste materials and polyolefin products so recovered - Patents.com |
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