JP2000248110A - Method for dehalogenating organic halogen-containing plastic - Google Patents

Method for dehalogenating organic halogen-containing plastic

Info

Publication number
JP2000248110A
JP2000248110A JP5045199A JP5045199A JP2000248110A JP 2000248110 A JP2000248110 A JP 2000248110A JP 5045199 A JP5045199 A JP 5045199A JP 5045199 A JP5045199 A JP 5045199A JP 2000248110 A JP2000248110 A JP 2000248110A
Authority
JP
Japan
Prior art keywords
plasticizer
plastic
organic halogen
metal oxide
containing plastic
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Pending
Application number
JP5045199A
Other languages
Japanese (ja)
Inventor
Seiichi Masuda
誠一 増田
Kaoru Masame
薫 眞目
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.)
Nippon Steel Corp
Original Assignee
Sumitomo Metal Industries 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 Sumitomo Metal Industries Ltd filed Critical Sumitomo Metal Industries Ltd
Priority to JP5045199A priority Critical patent/JP2000248110A/en
Publication of JP2000248110A publication Critical patent/JP2000248110A/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

  • Separation, Recovery Or Treatment Of Waste Materials Containing Plastics (AREA)

Abstract

PROBLEM TO BE SOLVED: To dehalogenate an organic halogen-containing plastic at good efficiency by removing the plasticizer from the plastic by extraction with an organic solvent, mixing the plasticizer-free residue with a metal oxide and/or a metal hydroxide, and mechanochemically treating the mixture. SOLUTION: A plastic is broken to a size of about 5 mm or below with a cutter or shredder, and the cut pieces are immersed in an organic solvent under agitation. The solvent containing the plasticizer is separated by filtration. The plasticizer-free residue is mixed with a metal oxide and/or a metal hydroxide, and the mixture is ground with e.g. a ball mill. The treated product is withdrawn and subjected to a treatment for eluting chlorine for 1-2 hr under agitation in an at least about 10-fold amount of water and filtered and dehydrated to accomplish dechlorination. The metal oxide and/or metal hydroxide used are desirably oxides and/or hydroxides of calcium and/or strontium and are desirably used in an amount at least twice the reaction molar equivalents of the halogen atoms contained in the material to be dehalogenated.

Description

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

【0001】[0001]

【発明の属する技術分野】本発明は、ポリ塩化ビニル樹
脂、フッ素樹脂等の燃焼処理時に有害ガスを発生する有
機ハロゲン含有プラスチックからの脱ハロゲン方法に関
する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method for dehalogenating an organic halogen-containing plastic which generates a harmful gas when a polyvinyl chloride resin, a fluororesin or the like is burned.

【0002】[0002]

【従来の技術】ポリ塩化ビニル樹脂は耐熱性、耐食性、
成形加工性等に優れていることから、各種方面で広く使
用されている。従って、廃棄されるポリ塩化ビニルが年
々増加しており、そのまま他の生ゴミと共に焼却処理さ
れて、焼却施設からの有害ガスの発生が社会問題化して
いる。
2. Description of the Related Art Polyvinyl chloride resin has heat resistance, corrosion resistance,
Because of its excellent moldability, it is widely used in various fields. Therefore, the amount of polyvinyl chloride to be discarded is increasing year by year, and it is incinerated with other garbage as it is, and the generation of harmful gas from the incineration facility has become a social problem.

【0003】試験的には脱塩素処理として250〜30
0℃に加熱分解し塩酸として塩素が回収されているが、
高温処理であるため処理設備の安全性の問題から普及に
は至っていない。
As a test, 250 to 30 dechlorination treatments are used.
It is decomposed by heating to 0 ° C and chlorine is recovered as hydrochloric acid.
Due to the high temperature treatment, it has not been widely used due to the safety of the processing equipment.

【0004】ポリ弗化エチレン等のフッ素樹脂は耐熱性
や耐薬品性に優れておりバルブやライニングの材料に使
用されているが、焼却処理により弗化水素等の有毒ガス
を発生するという問題がある。
[0004] Fluororesins such as polyfluorinated ethylene are excellent in heat resistance and chemical resistance and are used as materials for valves and linings. However, there is a problem that toxic gases such as hydrogen fluoride are generated by incineration. is there.

【0005】以上述べたごとく有機ハロゲン化合物含有
プラスチックは化学的安定性と種々の良好な特性から、
多方面で用いられているが、その化学的安定性から処理
が困難で、処理に苦慮しているのが現状である。
[0005] As described above, plastics containing an organic halogen compound have high chemical stability and various good properties.
Although it is used in various fields, it is difficult to treat because of its chemical stability, and at present it is difficult to treat.

【0006】[0006]

【発明が解決しようとする課題】このように、Cl・F
等の除去が問題であり、Cl・F等の除去方法としてメ
カノケミカル処理に着目した。
As described above, Cl.F.
Removal is a problem, and attention was paid to mechanochemical treatment as a method for removing Cl and F.

【0007】メカノケミカル処理とは、ボールミル等の
衝撃粉砕装置で反応物を粉砕する処理である。粉砕によ
り反応物が物理的に分子レベルで引きちぎられ、活性の
高い分子面ができる。このことにより常温では起こり得
ない反応を進行させることができる。
[0007] The mechanochemical treatment is a treatment in which a reaction product is pulverized by an impact pulverizer such as a ball mill. The milling physically tears off the reactants at the molecular level, creating a highly active molecular surface. This allows a reaction that cannot take place at normal temperature to proceed.

【0008】ところで、ポリ塩化ビニルをはじめとする
有機ハロゲン含有プラスチックは、そのままで使用され
ることもあるが、常温で固く、衝撃に弱いため10〜5
0%程度の可塑剤を混練して使用する製品が多い。この
可塑剤により変形能を向上させることにより、農業用シ
ート、長靴、ホース、電線被服材等、多くの用途を生み
出している。
Incidentally, organic halogen-containing plastics such as polyvinyl chloride are sometimes used as they are.
Many products use about 0% of a plasticizer kneaded. By improving the deformability with this plasticizer, many uses are created, such as agricultural sheets, boots, hoses, and wire covering materials.

【0009】しかしながら、この可塑剤の存在がボール
ミル等による粉砕に支障を生じさせ、メカノケミカル処
理の反応効率を著しく低下させるという問題があった。
However, there is a problem that the presence of the plasticizer hinders the pulverization by a ball mill or the like, and significantly reduces the reaction efficiency of the mechanochemical treatment.

【0010】本発明の目的は、有機ハロゲン含有プラス
チック中に存在する可塑剤を事前に分離し、メカノケミ
カル処理を効率よくおこなう有機ハロゲン含有プラスチ
ックからの脱ハロゲン方法を提供することにある。
An object of the present invention is to provide a method for dehalogenating an organic halogen-containing plastic in which a plasticizer present in the organic halogen-containing plastic is separated in advance and a mechanochemical treatment is efficiently performed.

【0011】[0011]

【課題を解決するための手段】本発明者等は、試験を重
ねた結果以下の知見を得た。 (1)有機ハロゲン含有プラスチック中の可塑剤を有機
溶剤で抽出除去すると、残留するプラスチックはポーラ
ス状になる。
Means for Solving the Problems The present inventors have obtained the following findings as a result of repeated tests. (1) When the plasticizer in the organic halogen-containing plastic is extracted and removed with an organic solvent, the remaining plastic becomes porous.

【0012】(2)ポーラス状のプラスチックのため、
ボールミル等で粉砕し易く、メカノケミカル処理時の脱
塩素効率が向上する。
(2) Because of the porous plastic,
It is easy to pulverize with a ball mill or the like, and the dechlorination efficiency during mechanochemical treatment is improved.

【0013】本発明は、以上の知見に基づいてなされた
もので、その要旨は、下記のとおりである。
The present invention has been made based on the above findings, and the gist thereof is as follows.

【0014】有機溶剤を用いて有機ハロゲン含有プラス
チックに練り込まれている可塑剤を抽出除去した後に、
可塑剤を除去した有機ハロゲン含有プラスチックと酸化
物および/または水酸化物とを混合してメカノケミカル
処理を行うことを特徴とする有機ハロゲン含有プラスチ
ックからの脱ハロゲン方法。
After extracting and removing the plasticizer kneaded into the organic halogen-containing plastic using an organic solvent,
A method for dehalogenating organic halogen-containing plastics, comprising mixing an organic halogen-containing plastic from which a plasticizer has been removed with an oxide and / or a hydroxide and performing a mechanochemical treatment.

【0015】[0015]

【発明の実施の形態】有機溶剤を用いて有機ハロゲン含
有プラスチックに練り込まれている可塑剤を抽出除去す
る方法は、以下のとおりである。
DETAILED DESCRIPTION OF THE PREFERRED EMBODIMENTS A method for extracting and removing a plasticizer kneaded in an organic halogen-containing plastic by using an organic solvent is as follows.

【0016】プラスチックを裁断機やシュレッダーを用
いて5mm以下程度に破砕し、有機溶剤中に浸漬・攪拌
する。その後、フィルターを用いて可塑剤を含む溶剤を
分離し、可塑剤を抽出除去することができる。
The plastic is crushed to about 5 mm or less using a cutter or a shredder, immersed in an organic solvent and stirred. Thereafter, the solvent containing the plasticizer is separated using a filter, and the plasticizer can be extracted and removed.

【0017】可塑剤の除去に用いる有機溶剤はアセト
ン、トルエン、ジエチルエーテル、灯油等の有機溶剤で
あればよく、特に限定されるものではない。
The organic solvent used for removing the plasticizer may be any organic solvent such as acetone, toluene, diethyl ether and kerosene, and is not particularly limited.

【0018】可塑剤を除去した残渣と金属酸化物および
/または水酸化物とを混合してボールミル等で粉砕す
る。粉砕容器および粉砕用のボールの材質は特に限定す
るものではないが、ステンレス鋼、タングステンカーバ
イト、メノウ等が望ましい。
The residue from which the plasticizer has been removed and the metal oxide and / or hydroxide are mixed and ground with a ball mill or the like. The material of the crushing container and the crushing ball is not particularly limited, but stainless steel, tungsten carbide, agate and the like are preferable.

【0019】混合粉砕終了後、前記混合処理物を取り出
し、重量で約10倍量以上の水中で攪拌しながら1〜2
時間塩素を溶出させる処理を行い、濾過脱水し脱塩素化
処理が終了する。
After the completion of the mixing and pulverization, the mixed product is taken out and stirred in water of about 10 times or more by weight while stirring.
A process for eluting chlorine is performed for a period of time, followed by filtration and dehydration to complete the dechlorination process.

【0020】添加混合する酸化物、水酸化物は、カルシ
ウムおよび/またはストロンチウムの酸化物、水酸化物
が望ましい。
The oxides and hydroxides to be added and mixed are preferably calcium and / or strontium oxides and hydroxides.

【0021】ストロンチウム、カルシウム分の合計は少
なくとも処理物のハロゲン含有量と反応モル当量(以
下、単に反応当量ともいう)が必要であり、反応当量の
2倍以上が望ましい。当量の場合でもハロゲンの除去は
可能であるが除去率が70〜80%に止まり、反応当量
の約2倍で90%の除去率が得られ、99%以上の除去
率を得るには、反応当量の3〜5倍量を必要とする。
The total content of strontium and calcium requires at least the halogen content of the treated product and the reaction molar equivalent (hereinafter, also simply referred to as the reaction equivalent), and is preferably at least twice the reaction equivalent. Even in the case of an equivalent, the removal of halogen is possible, but the removal rate is limited to 70 to 80%, and a removal rate of 90% is obtained at about twice the reaction equivalent. It requires 3 to 5 times the equivalent amount.

【0022】添加量が多いほど短時間で除去率は上昇で
きるが、反応当量の10倍以上添加すると反応系全体に
おけるハロゲン濃度が低下し、除去速度は低下する傾向
がある。
The removal rate can be increased in a short time as the amount of addition increases, but when added 10 times or more the reaction equivalent, the halogen concentration in the whole reaction system decreases, and the removal rate tends to decrease.

【0023】[0023]

【実施例】(比較例1)可塑剤としてジオクチルフタレ
ート(DOP)を約50%含有するポリ塩化ビニル製品
を10gの試料に27gの生石灰(CaO)を混合し1
〜3時間ボールミルにてメカノケミカル処理を行い、そ
の混合試料を取りだし、約1時間攪拌水中(500cc
の容量)で水洗し、濾過した残渣中の塩素分析を行い脱
塩素率を求めた。この生石灰(CaO)の添加量は反応
当量の3倍に相当する。
(Comparative Example 1) 27 g of quicklime (CaO) was mixed with 10 g of a polyvinyl chloride product containing about 50% of dioctyl phthalate (DOP) as a plasticizer.
Perform a mechanochemical treatment in a ball mill for ~ 3 hours, take out the mixed sample, and stir in stirring water (500cc
Was washed with water, and the chlorine residue in the filtered residue was analyzed to determine the dechlorination rate. The added amount of quicklime (CaO) is equivalent to three times the reaction equivalent.

【0024】(本発明例1)比較例1で使用した可塑剤
としてジオクチルフタレート(DOP)を約50%含有
するポリ塩化ビニルシート製品(厚み約1.5mm)を
5×5mm以下に裁断し、20gの試料をステンレス容
器中でジエチルエーテルに浸して約2時間室温で放置し
たのち、可塑剤を含む溶剤をフィルターろ過して、残渣
を取り出し乾燥したものを計量したところ10.5gで
あった。この可塑剤を除去した試料に27gの生石灰
(CaO)を混合し1〜3時間ボールミルにてメカノケ
ミカル処理を行い、その混合試料を取りだし、約1時間
攪拌水中(500ccの容量)で水洗し、濾過した残渣
中の塩素分析を行い脱塩素率を求めた。この生石灰(C
aO)の添加量は反応当量の3倍に相当する。
(Invention Example 1) A polyvinyl chloride sheet product (about 1.5 mm thick) containing about 50% of dioctyl phthalate (DOP) as a plasticizer used in Comparative Example 1 was cut into 5 × 5 mm or less. After a sample of 20 g was immersed in diethyl ether in a stainless steel container and allowed to stand at room temperature for about 2 hours, a solvent containing a plasticizer was filtered with a filter, and the residue was taken out and dried. 27 g of quicklime (CaO) was mixed with the sample from which the plasticizer had been removed, subjected to a mechanochemical treatment with a ball mill for 1 to 3 hours, and the mixed sample was taken out and washed with stirring water (500 cc capacity) for about 1 hour. Chlorine in the filtered residue was analyzed to determine the dechlorination rate. This quicklime (C
The amount of aO) added corresponds to three times the reaction equivalent.

【0025】(比較例2)可塑剤を含有しない純粋なポ
リ塩化ビニル10gの試料に27gの生石灰(CaO)
を混合し1〜3時間ボールミルにてメカノケミカル処理
を行い、その混合試料を取りだし、約1時間攪拌水中
(500ccの容量)で水洗し、濾過した残渣中の塩素
分析を行い脱塩素率を求めた。この生石灰(CaO)の
添加量は反応当量の3倍に相当する。
Comparative Example 2 27 g of quicklime (CaO) was added to a 10 g sample of pure polyvinyl chloride containing no plasticizer.
Are mixed and subjected to a mechanochemical treatment in a ball mill for 1 to 3 hours, a mixed sample is taken out, washed for about 1 hour with stirring water (500 cc capacity), and the chlorine residue in the filtered residue is analyzed to determine the dechlorination rate. Was. The added amount of quicklime (CaO) is equivalent to three times the reaction equivalent.

【0026】表1は、上記各条件下における脱塩素率
(%)の値を示す。表1に示すように、可塑剤を事前に
除去後にメカノケミカル処理をおこなった本発明例1
は、可塑剤を事前に除去しない比較例1よりも、さらに
可塑剤が入っていない比較例2よりも、脱塩素率(%)
が高かった。
Table 1 shows the values of the dechlorination rate (%) under the above conditions. As shown in Table 1, Example 1 of the present invention in which a mechanochemical treatment was performed after removing the plasticizer in advance.
Dechlorination rate (%) than Comparative Example 1 in which the plasticizer was not removed in advance, and Comparative Example 2 in which the plasticizer was not added.
Was high.

【0027】[0027]

【表1】 [Table 1]

【0028】[0028]

【発明の効果】本発明により、有機ハロゲン含有プラス
チックからの脱ハロゲンをメカノケミカル処理により効
率よくおこなうことができる。
According to the present invention, dehalogenation from an organic halogen-containing plastic can be efficiently performed by mechanochemical treatment.

Claims (1)

【特許請求の範囲】[Claims] 【請求項1】 有機溶剤を用いて有機ハロゲン含有プラ
スチックに練り込まれている可塑剤を抽出除去した後
に、可塑剤を除去した有機ハロゲン含有プラスチックと
金属酸化物および/または水酸化物とを混合してメカノ
ケミカル処理を行うことを特徴とする有機ハロゲン含有
プラスチックからの脱ハロゲン方法。
After extracting and removing a plasticizer kneaded in an organic halogen-containing plastic using an organic solvent, the organic halogen-containing plastic from which the plasticizer has been removed is mixed with a metal oxide and / or a hydroxide. A method for dehalogenating an organic halogen-containing plastic, comprising performing a mechanochemical treatment.
JP5045199A 1999-02-26 1999-02-26 Method for dehalogenating organic halogen-containing plastic Pending JP2000248110A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP5045199A JP2000248110A (en) 1999-02-26 1999-02-26 Method for dehalogenating organic halogen-containing plastic

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP5045199A JP2000248110A (en) 1999-02-26 1999-02-26 Method for dehalogenating organic halogen-containing plastic

Publications (1)

Publication Number Publication Date
JP2000248110A true JP2000248110A (en) 2000-09-12

Family

ID=12859237

Family Applications (1)

Application Number Title Priority Date Filing Date
JP5045199A Pending JP2000248110A (en) 1999-02-26 1999-02-26 Method for dehalogenating organic halogen-containing plastic

Country Status (1)

Country Link
JP (1) JP2000248110A (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2001253969A (en) * 2000-03-09 2001-09-18 Dowa Mining Co Ltd Method for cold defluorination of fluororesin
WO2019141504A1 (en) 2018-01-20 2019-07-25 Bürkle Consulting Gmbh Mechanochemical process for producing valuable products free from persistent organic pollutants and other organohalogen compounds from waste comprising plastics and plastic laminates

Cited By (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2001253969A (en) * 2000-03-09 2001-09-18 Dowa Mining Co Ltd Method for cold defluorination of fluororesin
WO2019141504A1 (en) 2018-01-20 2019-07-25 Bürkle Consulting Gmbh Mechanochemical process for producing valuable products free from persistent organic pollutants and other organohalogen compounds from waste comprising plastics and plastic laminates
DE102018000418A1 (en) * 2018-01-20 2019-07-25 Bürkle Consulting Gmbh Mechanochemical process for the production of persistent organic pollutants and other organohalogen compounds free value products from wastes of plastics and plastic laminates
US11807724B2 (en) 2018-01-20 2023-11-07 Gregor Luthe Mechanochemical process for producing valuable products free from persistent organic pollutants and other organohalogen compounds from waste comprising plastics and plastic laminates
EP4293072A2 (en) 2018-01-20 2023-12-20 Smart Material Printing B.V. Mechanochemical process for the production of persistent organic pollutants and other organohalogen compounds free valuables from waste of plastics and plastic laminates
EP4293072A3 (en) * 2018-01-20 2024-03-13 Smart Material Printing B.V. Mechanochemical process for the production of persistent organic pollutants and other organohalogen compounds free valuables from waste of plastics and plastic laminates

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