JP2753669B2 - Separation and recovery method of waste plastic - Google Patents
Separation and recovery method of waste plasticInfo
- Publication number
- JP2753669B2 JP2753669B2 JP22043192A JP22043192A JP2753669B2 JP 2753669 B2 JP2753669 B2 JP 2753669B2 JP 22043192 A JP22043192 A JP 22043192A JP 22043192 A JP22043192 A JP 22043192A JP 2753669 B2 JP2753669 B2 JP 2753669B2
- Authority
- JP
- Japan
- Prior art keywords
- specific gravity
- waste plastic
- separation
- plastic
- waste
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Expired - Fee Related
Links
Classifications
-
- 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
- Separation, Recovery Or Treatment Of Waste Materials Containing Plastics (AREA)
- Processing Of Solid Wastes (AREA)
- Separation Of Solids By Using Liquids Or Pneumatic Power (AREA)
- Processing And Handling Of Plastics And Other Materials For Molding In General (AREA)
Description
【0001】[0001]
【産業上の利用分野】本発明は、種々の廃プラスチック
の混合物を液体中での比重差を利用して高比重物と低比
重物とに分離し、これらを別々に回収する廃プラスチッ
クの分離回収方法に関し、より詳細にはその前処理に関
するものである。BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to the separation of waste plastics in which a mixture of various waste plastics is separated into a high specific gravity substance and a low specific gravity substance by utilizing a specific gravity difference in a liquid, and these are separately collected. The present invention relates to a recovery method, and more particularly to a pretreatment thereof.
【0002】[0002]
【従来の技術】ポリ塩化ビニルを含むプラスチック廃棄
物を一括処理すると、回収プラスチックをリサイクルす
る場合、多種類の廃プラスチックが混在するため、リサ
イクルプラスチックの質が低下し、また、回収プラスチ
ックを焼却処理する場合は、混在するポリ塩化ビニルの
焼却に伴って塩化水素ガスが発生し、これが焼却炉を損
傷し、さらには公害の発生原因にもなる。2. Description of the Related Art When plastic waste containing polyvinyl chloride is collectively treated, when recycled plastic is recycled, various types of waste plastics are mixed, so that the quality of the recycled plastic deteriorates and the collected plastic is incinerated. In such a case, hydrogen chloride gas is generated along with incineration of the mixed polyvinyl chloride, which damages the incinerator and further causes pollution.
【0003】本発明者らは図2に示すような廃プラスチ
ックの分離回収装置を開発した。これは、投入された廃
プラスチック混合物を循環させる投入槽(1) と、廃プラ
スチック混合物を比重差により低比重物と高比重物に区
分する分離槽(2) からなり、投入槽(1) には、スクリュ
ー(3) を備えた垂直筒体(4) が液中に沈むように配設さ
れている。スクリュー(3) の回転によって垂直筒体(4)
内に下降流が発生され、この下降流によって廃プラスチ
ック片は垂直筒体(4) 内に引き込まれ、強制的に分散さ
せられると共に、分散片が短時間で分離槽へ移行させら
れる。The present inventors have developed an apparatus for separating and recovering waste plastic as shown in FIG. This consists of a charging tank (1) for circulating the waste plastic mixture and a separation tank (2) for separating the waste plastic mixture into low specific gravity substances and high specific gravity substances based on the specific gravity difference. Is disposed such that a vertical cylinder (4) having a screw (3) sinks in the liquid. Vertical cylinder (4) by rotating screw (3)
A downward flow is generated therein, and by this downward flow, the waste plastic pieces are drawn into the vertical cylinder (4) and are forcibly dispersed, and the dispersed pieces are transferred to the separation tank in a short time.
【0004】ほとんど流れがない分離槽(2) では、廃プ
ラスチックの比重差によってポリエチレンなどの低比重
物(5) とポリ塩化ビニルなどの高比重物(6) とに分離さ
れる。低比重物(5) は分離槽(2) の表面に浮上し、高比
重物(6) は分離槽(2) 底部に沈積する。高比重物(6) の
沈積物はエアーリフト(7) と回収装置(8) を備えた循環
路(9) へ送られ、回収装置(8) で回収される。[0004] In the separation tank (2) where there is almost no flow, waste plastic is separated into a low specific gravity substance (5) such as polyethylene and a high specific gravity substance (6) such as polyvinyl chloride due to a difference in specific gravity. The low specific gravity (5) floats on the surface of the separation tank (2), and the high specific gravity (6) deposits on the bottom of the separation tank (2). The deposit of the high specific gravity (6) is sent to the circulation path (9) equipped with the air lift (7) and the recovery device (8), and is recovered by the recovery device (8).
【0005】この廃プラスチック分離回収方法によれ
ば、装置は投入槽と分離槽からなるので、投入槽と中間
槽と分離槽とからなる装置を用いる従来の方法に比べ、
廃プラスチックの分離回収処理に必要な時間を短縮で
き、廃プラスチックの分離回収装置を小型化でき、処理
に必要な液量を少くできる。スクリューによって筒体内
に廃プラスチック片を強制的に分散させる水流を発生す
ると共に、分散片を分離槽へ移行させるので、槽底から
の空気の吹き込みによって水または塩水に循環流を発生
させる従来の方法のように、ポリ塩化ビニルのような疎
水性プラスチックの表面には空気が付着しやすく、その
ためこの種のプラスチックが分離槽内で浮上してしまう
ことがほとんどなく、廃プラスチックの分離回収率を向
上させることができる。According to this waste plastic separation / recovery method, the apparatus is composed of a charging tank and a separation tank, and therefore, compared to a conventional method using a device including a charging tank, an intermediate tank and a separation tank.
The time required for waste plastic separation and recovery processing can be reduced, the size of the waste plastic separation and recovery device can be reduced, and the amount of liquid required for the processing can be reduced. A conventional method of generating a water flow for forcibly dispersing waste plastic pieces in a cylinder by a screw and transferring the dispersion pieces to a separation tank, so that a circulating flow is generated in water or salt water by blowing air from the bottom of the tank. As described above, air easily adheres to the surface of hydrophobic plastics such as polyvinyl chloride, so that this type of plastic hardly floats in the separation tank, improving the separation and recovery rate of waste plastics. Can be done.
【0006】[0006]
【発明が解決しようとする課題】しかし、上述した従来
の方法では、投入する廃プラスチックが偏平状のものや
いびつなもの、凹凸状の形状を成す場合には、垂直筒体
内のスクリューの回転により当該プラスチックを同筒体
内に引き込む際に、プラスチック表面に空気が付着し、
高比重のプラスチックでも分離槽内で浮上してしまうも
のが多くある。However, in the above-mentioned conventional method, when the waste plastic to be charged has a flat shape, a distorted shape, or an uneven shape, the rotation of the screw in the vertical cylinder causes the waste plastic to rotate. When the plastic is pulled into the cylinder, air adheres to the plastic surface,
Many high-density plastics also float in the separation tank.
【0007】本発明は、上記の点に鑑み、廃プラスチッ
クがいかなる形状をなしていても、これを液体中で比重
差によって高比重物と低比重物とに完全に区分して、こ
れらを効率的かつ高収率に分離回収できる方法を提供す
ることを目的とする。SUMMARY OF THE INVENTION In view of the above, the present invention provides a method for completely separating waste plastic into high specific gravity substances and low specific gravity substances in liquid according to the specific gravity difference, regardless of the shape. It is an object of the present invention to provide a method capable of separating and recovering the target in a high yield.
【0008】[0008]
【課題を解決するための手段】本発明による廃プラスチ
ックの分離回収方法は、上記目的を達成すべく工夫され
たものであって、廃プラスチックの混合物を液体中で比
重差により高比重物と低比重物とに分離するに当たり、
処理すべき廃プラスチックに水蒸気をあてることによっ
て、廃プラスチックを予め濡れ性付与処理しておくこと
を特徴とするものである。The method of separating and recovering waste plastic according to the present invention has been devised to achieve the above-mentioned object, and comprises mixing a mixture of waste plastics with a high specific gravity material and a low specific gravity material in a liquid by a specific gravity difference. In separating into specific gravity,
By exposing the waste plastic to be treated to steam
The waste plastic is subjected to a wettability-imparting treatment in advance .
【0009】上記水蒸気による濡れ性付与前処理として
は、次のような態様が可能である。As the pretreatment for imparting wettability with water vapor , the following embodiments are possible.
【0010】a)処理すべき廃プラスチックに水蒸気を
あてる。これによってプラスチックの細孔内の空気を脱
気する。 A) Steam is added to the waste plastic to be treated.
Dedicate This removes air in the plastic pores.
I care.
【0011】好ましくは、この後、さらに細孔内に水を
しみ込ませておく。 Preferably, thereafter, water is further added to the pores.
Let it soak.
【0012】b)上記と同様に、処理すべき廃プラスチ
ックに水蒸気をあて、プラスチックの細孔内の空気を脱
気した後、さらに雰囲気を冷却して水蒸気を液化させ細
孔内に液化水をしみ込ませておく。 B) Waste plastic to be treated as described above
Water vapor to remove air in the plastic pores.
After that, the atmosphere is further cooled to liquefy water vapor and
Let the liquefied water soak in the holes.
【0013】b)の方法が好ましい。 The method of b) is preferred.
【0014】[0014]
【作用】本発明による廃プラスチックの分離回収方法で
は、廃プラスチックの混合物を液体中で比重差により高
比重物と低比重物とに分離するに当たり、処理すべき廃
プラスチックに水蒸気をあてることによって、廃プラス
チックを予め濡れ性付与処理しておくので、廃プラスチ
ックと、分離回収装置内の水または水に塩類等を溶解さ
せ比重を大きくした液体との親和性を増加させることが
できる。その結果、廃プラスチックの表面に空気が付着
することはほとんどなくなり、高比重プラスチックの沈
降速度を増すことができる。したがって、廃プラスチッ
クの形状に関係なくこれを液体中で比重差によって高比
重物と低比重物とに完全に区分して、これらを効率的か
つ高収率に分離回収することができる。According to the method for separating and recovering waste plastic according to the present invention, when a mixture of waste plastics is separated into a high specific gravity substance and a low specific gravity substance by a specific gravity difference in a liquid, the waste to be treated is removed.
Exposing waste to water by applying steam to plastics
Since the tic is pre-treated for imparting wettability , the affinity between the waste plastic and water in the separation / recovery device or a liquid in which salts or the like are dissolved in water to increase the specific gravity can be increased. As a result, air hardly adheres to the surface of the waste plastic, and the sedimentation speed of the high-density plastic can be increased. Therefore, regardless of the shape of the waste plastic, it can be completely separated into a high specific gravity substance and a low specific gravity substance in the liquid by a specific gravity difference, and these can be separated and recovered efficiently and with high yield.
【0015】[0015]
【実施例】つぎに、本発明による廃プラスチックの分離
回収方法を実施例により具体的に説明する。Next, the method for separating and recovering waste plastic according to the present invention will be described in detail with reference to examples.
【0016】実施例1(参考として) まず、非イオン界面活性剤の水溶液として、250pp
mのポリオキシエチレンオクチルフェニルエーテル水溶
液を調製し、これを薬液タンク(10)に貯えた。処理すべ
き廃プラスチックとして、厚さ1mmのポリ塩化ビニル
板を15×15mm程度に破砕したもの100gを用意
し、この破砕片を攪拌機(15)付きの薬液タンク(10)内の
非イオン界面活性剤水溶液中に10秒間浸した。その
後、プラスチック破砕片を回収して脱水機(11)で軽く水
気を切り、プラスチック破砕片の表面に界面活性剤の薄
膜を形成させた。Example 1 (for reference) First, as an aqueous solution of a nonionic surfactant, 250 pp
m of an aqueous solution of polyoxyethylene octyl phenyl ether was prepared and stored in a chemical solution tank (10). As a waste plastic to be treated, 100 g of a 1 mm thick polyvinyl chloride plate crushed to about 15 × 15 mm is prepared, and the crushed pieces are subjected to nonionic surface activity in a chemical solution tank (10) with a stirrer (15). It was immersed in the agent aqueous solution for 10 seconds. Thereafter, the plastic crushed pieces were collected and lightly drained with a dehydrator (11) to form a surfactant thin film on the surface of the plastic crushed pieces.
【0017】脱水機(11)から出た濾液は濾液タンク(12)
に貯えられ、同タンク(12)の底部からポンプ(13)によっ
てフィルター装置(14)に通され、スラッジを除去された
後、薬液タンク(10)へ戻された。The filtrate discharged from the dehydrator (11) is supplied to a filtrate tank (12).
The sludge was removed from the bottom of the tank (12) by a pump (13) through a filter device (14), and then returned to a chemical solution tank (10).
【0018】このような前処理の後、図2に示す分離回
収装置の投入槽(1) 内の水中に処理済みプラスチック破
砕片を投入した。廃プラスチックの分離回収装置は、投
入された廃プラスチック混合物を循環させる投入槽(1)
と、廃プラスチック混合物を比重差により低比重物と高
比重物に区分する分離槽(2) からなり、投入槽(1) に
は、スクリュー(3) を備えた垂直筒体(4) が液中に沈む
ように配設されている。スクリュー(3) の回転によって
垂直筒体(4) 内に下降流が発生され、この下降流によっ
てプラスチック片は垂直筒体(4) 内に引き込まれ、強制
的に分散させられると共に、分散片が短時間で分離槽へ
移行させられる。After such pretreatment, the treated plastic crushed pieces were put into water in the charging tank (1) of the separation and recovery apparatus shown in FIG. The waste plastic separation and recovery device is a charging tank (1) for circulating the waste plastic mixture
And a separation tank (2) that separates the waste plastic mixture into low-specific gravity substances and high-specific gravity substances based on the specific gravity difference.In the charging tank (1), a vertical cylinder (4) equipped with a screw (3) is equipped with a liquid. It is arranged to sink in. A downward flow is generated in the vertical cylinder (4) by the rotation of the screw (3), and the plastic flow is drawn into the vertical cylinder (4) by this downward flow and is forcibly dispersed, and the dispersion pieces are dispersed. Transfer to the separation tank in a short time.
【0019】ほとんど流れがない分離槽(2) では、廃プ
ラスチックの比重差によってポリエチレンなどの低比重
物(5) とポリ塩化ビニルなどの高比重物(6) とに分離さ
れる。低比重物(5) は分離槽(2) の表面に浮上し、高比
重物(6) は分離槽(2) 底部に沈積する。高比重物(6) の
沈積物はエアーリフト(7) と回収装置(8) を備えた循環
路(9) へ送られ、回収装置(8) で回収される。In the separation tank (2) where there is little flow, waste plastic is separated into a low specific gravity substance (5) such as polyethylene and a high specific gravity substance (6) such as polyvinyl chloride due to a difference in specific gravity. The low specific gravity (5) floats on the surface of the separation tank (2), and the high specific gravity (6) deposits on the bottom of the separation tank (2). The deposit of the high specific gravity (6) is sent to the circulation path (9) equipped with the air lift (7) and the recovery device (8), and is recovered by the recovery device (8).
【0020】実施例2 実施例1の非イオン界面活性剤水溶液による前処理の代
わりに、処理すべき廃プラスチックに予め水蒸気をあ
て、廃プラスチックの細孔内の空気を脱気した後、さら
に細孔内に水をしみ込ませた。Example 2 Instead of the pretreatment with the nonionic surfactant aqueous solution of Example 1, steam was previously applied to the waste plastic to be treated, and the air in the pores of the waste plastic was degassed. Water was soaked in the holes.
【0021】この前処理の後、実施例1と同様に、図2
に示す分離回収装置の投入槽(1) 内の水中に処理済みプ
ラスチック破砕片を投入し、実施例1と同様の操作を行
った。After this pre-processing, as in the first embodiment, FIG.
The treated plastic crushed pieces were charged into water in the charging tank (1) of the separation and recovery apparatus shown in (1), and the same operation as in Example 1 was performed.
【0022】実施例3 実施例1の非イオン界面活性剤水溶液による前処理の代
わりに、処理すべき廃プラスチックに予め水蒸気(温
度:150℃、圧力:5kgf/cm 2 G)をあて、廃
プラスチックの細孔内の空気を脱気した後、雰囲気を冷
却して水蒸気を液化させ細孔内に液化水をしみ込ませて
おいた。Example 3 Instead of the pretreatment with a nonionic surfactant aqueous solution of Example 1, water vapor (temperature
After applying air at a temperature of 150 ° C. and a pressure of 5 kgf / cm 2 G) to evacuate the air in the pores of the waste plastic, the atmosphere is cooled to liquefy water vapor and impregnate liquefied water into the pores. Was.
【0023】この前処理の後、実施例1と同様に、図2
に示す分離回収装置の投入槽(1) 内の水中に処理済みプ
ラスチック破砕片を投入し、実施例1と同様の操作を行
った。After this preprocessing, as in the first embodiment, FIG.
The treated plastic crushed pieces were charged into water in the charging tank (1) of the separation and recovery apparatus shown in (1), and the same operation as in Example 1 was performed.
【0024】比較例1 厚さ1mmのポリ塩化ビニル板を15×15mm程度に
破砕したプラスチック破砕片100gを、上記前処理な
しで、図2に示す分離回収装置の投入槽(1) 内の水中に
投入し、実施例1と同様の操作を行った。COMPARATIVE EXAMPLE 1 100 g of plastic crushed pieces obtained by crushing a polyvinyl chloride plate having a thickness of 1 mm into a size of about 15 × 15 mm were not subjected to the above-mentioned pretreatment, and the water in the charging tank (1) of the separation and recovery apparatus shown in FIG. And the same operation as in Example 1 was performed.
【0025】比較試験 実施例3による前処理品と、比較例1による非前処理品
とについて、廃プラスチックの分離回収実験を行った。
この実験結果を表1に示す。Comparative Test Separation and recovery experiments of waste plastic were performed on the pretreated product according to Example 3 and the non-pretreated product according to Comparative Example 1.
Table 1 shows the experimental results.
【0026】[0026]
【表1】 表1から、本発明による廃プラスチックの分離回収方法
では、移動時間、回収率共に大幅な改良が認められる。[Table 1] From Table 1, it can be seen that the method for separating and recovering waste plastic according to the present invention significantly improves both the transfer time and the recovery rate.
【0027】[0027]
【発明の効果】本発明による廃プラスチックの分離回収
方法は、上記の如く構成されているので、次の利点を有
する。The method for separating and recovering waste plastic according to the present invention has the following advantages since it is configured as described above.
【0028】1) 廃プラスチックの分離回収率を向上さ
せることができる。1) The separation and recovery rate of waste plastic can be improved.
【0029】2) 廃プラスチックの分離回収処理に必要
な時間を短縮できる。2) The time required for the separation and recovery of waste plastic can be reduced.
【0030】3) 廃プラスチックを前処理することによ
り廃プラスチック表面の汚れを分離回収装置投入前に除
去できる。3) By pre-treating the waste plastic, the dirt on the surface of the waste plastic can be removed before the waste plastic is introduced.
【0031】こうして、本発明の装置によれば、廃プラ
スチックの混合物を比重差によって低比重物と高比重物
に完全に区分して、これらを効率的かつ高収率に分離回
収することができる。Thus, according to the apparatus of the present invention, the mixture of waste plastics can be completely separated into low specific gravity substances and high specific gravity substances according to the specific gravity difference, and these can be separated and recovered efficiently and with high yield. .
【図1】廃プラスチックの分離回収装置を示す垂直充断
面図である。FIG. 1 is a vertical sectional view showing a device for separating and recovering waste plastic.
【図2】本発明方法を示すフローシートである。FIG. 2 is a flow sheet showing the method of the present invention.
(1) …投入槽 (2) …分離槽 (3) …スクリュー (4) …垂直筒体 (5) …低比重物 (6) …高比重物 (9) …循環路 (10)…薬液タンク (11)…脱水機 (1)… Input tank (2)… Separation tank (3)… Screw (4)… Vertical cylinder (5)… Low specific gravity (6)… High specific gravity (9)… Circulation path (10)… Chemical tank (11) Dehydrator
───────────────────────────────────────────────────── フロントページの続き (72)発明者 高倉 千登世 大阪市此花区西九条5丁目3番28号 日 立造船株式会社内 (56)参考文献 特開 昭48−97155(JP,A) 特開 昭50−37465(JP,A) 特開 昭50−97673(JP,A) 特公 昭52−5065(JP,B2) ──────────────────────────────────────────────────続 き Continuation of the front page (72) Inventor Chitose Takakura 5-28 Nishikujo, Konohana-ku, Osaka-shi Inside Tachibashi Shipbuilding Co., Ltd. (56) References JP-A-48-97155 (JP, A) 50-5037465 (JP, A) JP-A-50-96773 (JP, A) JP-B 52-5065 (JP, B2)
Claims (1)
差により高比重物と低比重物とに分離するに当たり、処
理すべき廃プラスチックに水蒸気をあてることによっ
て、廃プラスチックを予め濡れ性付与処理しておくこと
を特徴とする廃プラスチックの分離回収方法。The method according to claim 1 mixture of waste plastics Upon separated into a high density product and low specific gravity thereof by a difference in specific gravity in the liquid processing
By applying steam to the waste plastics
And separating and collecting the waste plastic in advance by subjecting the waste plastic to a wettability imparting treatment .
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP22043192A JP2753669B2 (en) | 1992-08-19 | 1992-08-19 | Separation and recovery method of waste plastic |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP22043192A JP2753669B2 (en) | 1992-08-19 | 1992-08-19 | Separation and recovery method of waste plastic |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPH0663944A JPH0663944A (en) | 1994-03-08 |
| JP2753669B2 true JP2753669B2 (en) | 1998-05-20 |
Family
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Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP22043192A Expired - Fee Related JP2753669B2 (en) | 1992-08-19 | 1992-08-19 | Separation and recovery method of waste plastic |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JP2753669B2 (en) |
Families Citing this family (4)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP2796934B2 (en) * | 1994-04-14 | 1998-09-10 | 中小企業事業団 | Waste plastic separation method |
| JP2006175740A (en) * | 2004-12-22 | 2006-07-06 | Sharp Corp | Plastic waste recycling method, plastic raw material manufacturing method, plastic molding manufacturing method, plastic raw material, plastic molding |
| JP2007015340A (en) * | 2005-07-11 | 2007-01-25 | Sharp Corp | Recycling method of plastic mixture, plastic raw material and plastic molded body |
| DE112019001817B4 (en) | 2018-04-06 | 2025-01-30 | Federal-Mogul Motorparts Llc | BRAKE PAD |
Family Cites Families (4)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS525066B2 (en) * | 1972-03-24 | 1977-02-09 | ||
| JPS5037465A (en) * | 1973-08-03 | 1975-04-08 | ||
| JPS5097673A (en) * | 1973-12-27 | 1975-08-02 | ||
| JPS525065A (en) * | 1975-06-30 | 1977-01-14 | Kubota Ltd | Leakage preventing unit of dust collector by-pass duct |
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1992
- 1992-08-19 JP JP22043192A patent/JP2753669B2/en not_active Expired - Fee Related
Also Published As
| Publication number | Publication date |
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| JPH0663944A (en) | 1994-03-08 |
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