JPH10259273A - Chlorine removal from chlorine-containing polymeric resin - Google Patents

Chlorine removal from chlorine-containing polymeric resin

Info

Publication number
JPH10259273A
JPH10259273A JP27962297A JP27962297A JPH10259273A JP H10259273 A JPH10259273 A JP H10259273A JP 27962297 A JP27962297 A JP 27962297A JP 27962297 A JP27962297 A JP 27962297A JP H10259273 A JPH10259273 A JP H10259273A
Authority
JP
Japan
Prior art keywords
chlorine
heat medium
resin
containing polymer
polymer resin
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
JP27962297A
Other languages
Japanese (ja)
Inventor
Minoru Asanuma
稔 浅沼
Tatsuro Ariyama
達郎 有山
Yukihiko Asakawa
幸彦 浅川
Koichi Tomioka
浩一 冨岡
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.)
JFE Engineering Corp
Original Assignee
NKK Corp
Nippon Kokan 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 NKK Corp, Nippon Kokan Ltd filed Critical NKK Corp
Priority to JP27962297A priority Critical patent/JPH10259273A/en
Publication of JPH10259273A publication Critical patent/JPH10259273A/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

Abstract

PROBLEM TO BE SOLVED: To obtain high treatment efficiency in chlorine removal from chlorine- containing resin by means of a rotary kiln by using the thermal medium continuously after dechlorination treatment without separation from the waste resin as a feedstock for the kiln, as the heat medium is prevented from segregation. SOLUTION: The material to be treated comprising partially or wholly a chlorine-containing polymer resin material is fed to a path 4 inside the rotary kiln together with the heat medium and hot gas is blown in the same path 4 to effect the dechlorination from the chlorine-containing polymer resin. At this time, as a heat medium to be fed together with the material to be treated, iron source for the furnace, an iron source reducing agent, one or more kinds of powder particles that can be used as a fuel or auxiliary feedstock, particularly powdery coke and/or granular thermosetting resin are used. Since the heat medium is the particles used in the furnace, it can be used as an iron source reduction agent or as a fuel in no need of separation into the treated resin material and the heat medium. Thus, the segregation of the heat medium is inhibited to attain high treatment efficiency.

Description

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

【0001】[0001]

【発明が属する技術分野】本発明は、塩化ビニル等の含
塩素高分子樹脂から塩素を除去するための塩素除去方法
に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method for removing chlorine from a chlorine-containing polymer resin such as vinyl chloride.

【0002】[0002]

【従来の技術】近年、産業廃棄物や一般廃棄物としてプ
ラスチック等の合成樹脂類が急増しており、その処理が
社会的に大きな問題となっている。なかでも高分子系の
炭化水素化合物であるプラスチックは燃焼時に発生する
発熱量が高く、一般焼却炉で焼却処理した場合に炉壁等
を傷めることから大量処理が困難であり、その多くはご
み埋立て地等に投棄されているのが現状である。しか
し、プラスチック等の投棄は環境対策上好ましくなく、
また、昨今では埋立用の用地不足が社会問題となりつつ
あり、このため投棄によらない合成樹脂類の大量処理方
法の開発が切望されている。
2. Description of the Related Art In recent years, synthetic resins such as plastics have been rapidly increasing as industrial wastes and general wastes, and their disposal has become a serious social problem. Among them, plastics, which are high-molecular hydrocarbon compounds, generate a large amount of heat when they are burned, and when incinerated in a general incinerator, damage the furnace walls etc., making mass treatment difficult, and most of them are landfills. It is currently dumped on land. However, dumping of plastics etc. is not preferable for environmental measures,
Further, recently, shortage of land for landfill is becoming a social problem, and therefore, development of a method for mass processing of synthetic resins that does not rely on dumping is keenly desired.

【0003】このような背景の下、プラスチック等の合
成樹脂類を高炉等の補助燃料あるいは鉄源の還元剤とし
て用いる方法が、例えば欧州特許公開公報第06224
65A1号及び特公昭51−33493号公報に示され
ている。しかし、廃棄合成樹脂類中には塩化ビニル等の
含塩素高分子樹脂が平均して約15%も含まれると言わ
れており、このような合成樹脂類を高炉等に供給した場
合には、含塩素高分子樹脂の熱分解や燃焼により多量の
有害ガス(HCl)が発生し、著しい環境汚染を生じさ
せる。したがって、このような有害ガスの発生を防止す
るためには、事前に合成樹脂類から含塩素高分子樹脂を
分離し、この含塩素高分子樹脂から塩素分を除去(脱塩
素処理)する必要がある。
Against this background, a method using synthetic resins such as plastics as an auxiliary fuel for a blast furnace or the like or a reducing agent for an iron source is disclosed in, for example, European Patent Publication No. 06224.
65A1 and JP-B-51-33493. However, it is said that about 15% of chlorine-containing polymer resin such as vinyl chloride is contained in waste synthetic resin on average, and when such synthetic resin is supplied to a blast furnace or the like, A large amount of harmful gas (HCl) is generated by thermal decomposition and combustion of the chlorine-containing polymer resin, causing significant environmental pollution. Therefore, in order to prevent the generation of such harmful gases, it is necessary to separate the chlorine-containing polymer resin from the synthetic resins in advance and remove chlorine (dechlorination treatment) from the chlorine-containing polymer resin. is there.

【0004】従来、含塩素高分子樹脂を脱塩素処理する
ための方法として、ロータリーキルンを用いる方法が知
られている。この方法はロータリーキルンの内部に含塩
素高分子樹脂材と熱媒体である砂を供給するとともに、
熱源として加熱ガスを供給するもので、含塩素高分子樹
脂はキルンの回転により砂と混合されつつ約250〜3
50℃程度に加熱され、この加熱によって樹脂中の塩素
分が塩化水素として脱離する脱離反応が生じ、塩化水素
ガスが発生する。この塩化水素ガスは加熱ガスとともに
キルン外に排出され、また、脱塩素処理が完了した含塩
素高分子樹脂の残渣(樹脂の残留固形物)も熱媒体であ
る砂とともにキルン外に排出される。
Conventionally, a method using a rotary kiln is known as a method for dechlorinating a chlorine-containing polymer resin. This method supplies chlorine-containing polymer resin material and sand as a heat carrier inside the rotary kiln,
Heating gas is supplied as a heat source, and the chlorine-containing polymer resin is mixed with sand by rotation of the kiln for about 250 to 3 hours.
The resin is heated to about 50 ° C., and this heating causes a elimination reaction in which chlorine in the resin is eliminated as hydrogen chloride, and hydrogen chloride gas is generated. The hydrogen chloride gas is discharged to the outside of the kiln together with the heating gas, and the residue of the chlorine-containing polymer resin (residual solid matter of the resin) after the dechlorination treatment is also discharged to the outside of the kiln together with the sand as the heat medium.

【0005】[0005]

【発明が解決しようとする課題】しかし、脱塩素処理さ
れた樹脂材の残渣を高炉等の溶解炉の吹き込み若しくは
装入原料(主として、鉄源の還元剤や燃料)等として用
いる場合、熱媒体として砂を用いる上記従来技術では脱
塩素処理が完了した樹脂材の残渣から砂を分離する必要
があり、この処理のために設備コストや処理コストの増
大を招いてしまう。
However, when the residue of the dechlorinated resin material is blown into a melting furnace such as a blast furnace or used as a raw material (mainly, a reducing agent or fuel for an iron source), a heat medium is required. In the above-described conventional technique using sand as the material, it is necessary to separate the sand from the residue of the resin material after the dechlorination treatment is completed, and this treatment causes an increase in equipment cost and treatment cost.

【0006】また、含塩素高分子樹脂材の形態は塊状や
フィルム状等、種々雑多であるとともに、合成樹脂の密
度が1前後であるのに対して砂の密度は2〜3程度であ
り、両者には著しい比重差があることから、砂がロータ
リーキルン内で偏析し易く、このため砂が熱媒体として
有効に機能せず、処理効率が低いという問題がある。ま
た、含塩素高分子樹脂材と砂との比率(含塩素高分子樹
脂材/砂)が1以下の場合には樹脂材の低級炭化水素へ
の熱分解が起こり易く、この結果、排ガスに塩化水素ガ
スとともに低級炭化水素ガスが含まれることになるた
め、排ガスの処理コストも増大してしまう。
Further, the form of the chlorine-containing polymer resin material is various, such as a lump or a film, and the density of the synthetic resin is about 1, while the density of the sand is about 2-3, Since there is a remarkable difference in specific gravity between the two, the sand tends to segregate in the rotary kiln, so that the sand does not function effectively as a heat carrier and the processing efficiency is low. When the ratio of the chlorine-containing polymer resin material to the sand (chlorine-containing polymer resin material / sand) is 1 or less, thermal decomposition of the resin material to lower hydrocarbons easily occurs. Since the lower hydrocarbon gas is contained together with the hydrogen gas, the processing cost of the exhaust gas also increases.

【0007】したがって本発明の目的は、このような従
来技術の問題点を解決し、ロータリーキルン方式による
含塩素高分子樹脂の塩素除去において、脱塩素処理後の
樹脂材の残渣から熱媒体を分離することなく、そのまま
炉用の原料(燃料または銑源還元剤等)として用いるこ
とを可能とする含塩素高分子樹脂の塩素除去方法を提供
することにある。また、本発明の他の目的は、熱媒体の
偏析が防止され、熱媒体が効果的に機能して高い処理効
率が得られるとともに、樹脂材の低級炭化水素への熱分
解も効果的に抑制される含塩素高分子樹脂の塩素除去方
法を提供することにある。
SUMMARY OF THE INVENTION Accordingly, an object of the present invention is to solve such problems of the prior art, and to separate a heat medium from a residue of a resin material after dechlorination treatment in removing chlorine from a chlorine-containing polymer resin by a rotary kiln method. An object of the present invention is to provide a method for removing chlorine from a chlorine-containing polymer resin, which can be used as a raw material for a furnace (such as a fuel or an iron source reducing agent) without any modification. Another object of the present invention is to prevent the segregation of the heat medium, effectively function the heat medium to obtain high treatment efficiency, and also effectively suppress the thermal decomposition of the resin material into lower hydrocarbons. To provide a method for removing chlorine from a chlorine-containing polymer resin.

【0008】[0008]

【課題を解決するための手段】このような課題を解決す
るための本発明の特徴は以下の通りである。 (1) ロータリキルン方式の塩素除去装置を用い、ロータ
リーキルンの通路内に一部または全部が含塩素高分子樹
脂材からなる被処理材を熱媒体とともに供給し、且つ同
じ通路内に加熱ガスを流して含塩素高分子樹脂材の脱塩
素処理を行う含塩素高分子樹脂の塩素除去方法におい
て、被処理材とともに供給すべき熱媒体として、炉の鉄
源、鉄源還元剤、燃料または副原料として使用できる粉
粒物の中から選ばれる1種以上の粉粒物を用いることを
特徴とする含塩素高分子樹脂の塩素除去方法。
The features of the present invention for solving such a problem are as follows. (1) Using a rotary kiln-type chlorine removing device, supply the material to be treated, which is partially or entirely made of a chlorine-containing polymer resin material, together with the heat medium into the passage of the rotary kiln, and flow the heating gas through the same passage. In the method for removing chlorine from chlorine-containing polymer resin by dechlorination of chlorine-containing polymer resin material, as a heat medium to be supplied together with the material to be treated, as a furnace iron source, iron source reducing agent, fuel or auxiliary material A method for removing chlorine from a chlorine-containing polymer resin, comprising using one or more kinds of particles selected from usable particles.

【0009】(2) 上記(1)の塩素除去方法において、熱
媒体として用いる粉粒物が、粉コークス、粉鉱石、焼結
粉および粉粒状熱硬化性樹脂の中から選ばれる1種以上
の粉粒物であることを特徴とする含塩素高分子樹脂の塩
素除去方法。 (3) 上記(1)の塩素除去方法において、熱媒体として用
いる粉粒物が、粉コークスおよび粉粒状熱硬化性樹脂の
中から選ばれる1種以上の粉粒物であることを特徴とす
る含塩素高分子樹脂の塩素除去方法。本発明では、被処
理材に塩素含有樹脂以外の樹脂類、塩素含有樹脂と他の
素材との複合材、樹脂以外の素材が含まれることを妨げ
ない。
(2) In the method for removing chlorine according to the above (1), the powdery or granular material used as the heat medium is at least one selected from coke breeze, ore, ore powder, sintered powder and particulate thermosetting resin. A method for removing chlorine from a chlorine-containing polymer resin, which is a granular material. (3) The method for removing chlorine according to the above (1), wherein the granular material used as the heat medium is at least one type of granular material selected from coke breeze and granular thermosetting resin. Method for removing chlorine from chlorine-containing polymer resin. In the present invention, the material to be treated does not prevent the inclusion of resins other than the chlorine-containing resin, composite materials of the chlorine-containing resin and other materials, and materials other than the resin.

【0010】[0010]

【発明の実施の形態】以下、本発明の実施の形態を図1
及び図2を例に説明すると、図において1はロータリー
キルン本体であり、このロータリーキルン本体1は耐火
物2と鉄皮3とからなり、内部が被処理樹脂材を移送し
つつ脱塩素処理するための通路4を構成している。
FIG. 1 is a block diagram showing an embodiment of the present invention.
And FIG. 2 as an example, 1 is a rotary kiln main body in the figure, and this rotary kiln main body 1 is composed of a refractory 2 and a steel shell 3, and the inside of the rotary kiln main body 1 is used for dechlorination while transferring a resin material to be processed. The passage 4 is constituted.

【0011】このロータリーキルン本体1の通路4に
は、その一端側から一部または全部が含塩素高分子樹脂
材である被処理材(以下、被処理材が実質的に樹脂材の
みからなる場合を例に述べる)と熱媒体が供給されると
ともに、熱源として加熱ガスが供給される。この加熱ガ
スはキルン全体を加熱するとともに、被処理樹脂材と熱
媒体を加熱する。また、固体熱媒体は被処理樹脂材を加
熱するだけでなく、被処理樹脂材中に分散して被処理樹
脂材どうしの融着、塊状化を抑制し、これらにより脱塩
素効率を向上させる。被処理樹脂材はキルンの回転によ
り熱媒体と混合されつつ加熱され、この加熱によって含
塩素高分子樹脂材中の塩素分が塩化水素として脱離する
反応が生じ、塩化水素ガスが発生する。
In the passage 4 of the rotary kiln main body 1, a material to be treated, which is partially or entirely a chlorine-containing polymer resin material from one end side thereof (hereinafter, a case where the material to be treated is substantially composed of only a resin material). (Described in the example), a heating medium is supplied, and a heating gas is supplied as a heat source. The heating gas heats the entire kiln and heats the resin material to be processed and the heat medium. Further, the solid heat medium not only heats the resin material to be treated, but also disperses in the resin material to be treated, thereby suppressing fusion and agglomeration of the resin materials to be treated, thereby improving the dechlorination efficiency. The resin material to be treated is heated while being mixed with the heat medium by the rotation of the kiln, and this heating causes a reaction in which chlorine in the chlorine-containing polymer resin material is desorbed as hydrogen chloride, and hydrogen chloride gas is generated.

【0012】本発明では、このような脱塩素処理におい
て被処理樹脂材とともに通路4内に供給する熱媒体とし
て、炉の鉄源、鉄源還元剤、燃料または副原料として使
用できる1種以上の粉粒物を用いる。これによって、脱
塩素処理を終えた樹脂材の残渣を熱媒体と分離すること
なく、そのまま溶解炉等に鉄源の還元剤や燃料等として
供給することができる。そのような熱媒体に適した粉粒
物としては、粉コークス、粉鉱石、焼結粉(焼結鉱の粉
粒物)、粉粒状熱硬化性樹脂(例えば、フェノール樹
脂、ユリア樹脂、ウレタン樹脂等)等が挙げられ、これ
らのうちの1種以上を熱媒体として用いることが好まし
い。
In the present invention, as a heat medium supplied into the passage 4 together with the resin material to be treated in such a dechlorination treatment, at least one kind of iron source, iron source reducing agent, fuel or auxiliary material of the furnace that can be used. Use granules. Thus, the residue of the resin material after the dechlorination treatment can be supplied as it is to the melting furnace or the like as a reducing agent of the iron source, fuel, or the like without being separated from the heat medium. Powders and granules suitable for such a heat medium include coke breeze, fine ore, sintered powder (granules of sintered ore), and particulate thermosetting resins (eg, phenolic resin, urea resin, urethane resin). And the like, and it is preferable to use one or more of these as a heat medium.

【0013】また、通路4内での熱媒体の偏析を防止し
て加熱効率を向上させるためには、熱媒体の粒径や比重
が樹脂材になるべく近い方が好ましく、このような観点
からは熱媒体として粉コークスおよび/または粉粒状熱
硬化性樹脂を使用することが最も好ましい。また、熱媒
体として粉コークス、粉粒状熱硬化性樹脂を用いること
により熱媒体の偏析が防止される結果、樹脂材の低級炭
化水素への分解も抑制される。
In order to prevent the segregation of the heat medium in the passage 4 and improve the heating efficiency, it is preferable that the heat medium has a particle diameter and specific gravity as close as possible to the resin material. Most preferably, coke breeze and / or particulate thermosetting resin is used as the heating medium. In addition, the use of coke breeze or a particulate thermosetting resin as a heat medium prevents segregation of the heat medium, thereby suppressing decomposition of the resin material into lower hydrocarbons.

【0014】通路4内における被処理樹脂材の加熱温度
は250〜350℃、望ましくは300℃前後とするこ
とが好ましい。加熱温度が250℃未満では塩化水素の
脱離反応が効率的に行われず、一方、350℃を超える
と樹脂材のガス状および液状炭化水素への熱分解が起こ
り始める。
The heating temperature of the resin material to be treated in the passage 4 is preferably set at 250 to 350.degree. C., more preferably around 300.degree. If the heating temperature is lower than 250 ° C., the elimination reaction of hydrogen chloride is not efficiently performed, while if it exceeds 350 ° C., thermal decomposition of the resin material into gaseous and liquid hydrocarbons starts to occur.

【0015】通路4を流れた加熱ガスと被処理樹脂材か
ら脱離した塩化水素ガスは通路4の他端側から排出さ
れ、この排出ガス中の塩化水素ガスは塩化水素吸収棟等
で回収される。また、脱塩素処理が完了した被処理樹脂
材の残渣(熱分解した樹脂の残留固形物)は熱媒体(炉
の鉄源還元剤、燃料または副原料として使用できる1種
以上の粉粒物)とともにキルン外に排出され、熱媒体を
分離されることなく、そのまま溶解炉等の炉において鉄
源の還元剤や燃料等として用いられる。
The heated gas flowing through the passage 4 and the hydrogen chloride gas desorbed from the resin material to be treated are discharged from the other end of the passage 4, and the hydrogen chloride gas in the discharged gas is recovered in a hydrogen chloride absorption building or the like. You. In addition, the residue of the resin material to be treated after the dechlorination treatment has been completed (residual solid matter of the thermally decomposed resin) is a heating medium (an iron source reducing agent for a furnace, at least one kind of powder or granules usable as a fuel or an auxiliary material). Is discharged out of the kiln together with the heat medium, and is used as it is as a reducing agent of an iron source, a fuel, etc. in a furnace such as a melting furnace without being separated.

【0016】図3は、本発明の実施に供される塩素除去
装置の一構成例を示すもので、通路4を有するロータリ
ーキルン本体1の一端側には、供給口6を備えた材料供
給用のスクリューフィーダー5と加熱ガス(熱風)を供
給するための熱風導管7が接続されている。また、ロー
タリーキルン本体1の他端側には処理済み樹脂材および
排ガスの排出装置8が設けられている。この排出装置8
は、その下部に樹脂残渣の排出口9を、また上部に排ガ
ス排出口10を有している。その他図面において、11
は熱風発生機、12はスクリューフィーダー5の駆動モ
ータである。
FIG. 3 shows an example of the structure of a chlorine removing apparatus used for carrying out the present invention. One end of a rotary kiln body 1 having a passage 4 is provided with a supply port 6 for supplying a material. A screw feeder 5 and a hot air conduit 7 for supplying a heating gas (hot air) are connected. On the other end side of the rotary kiln body 1, a discharge device 8 for the treated resin material and the exhaust gas is provided. This discharging device 8
Has a resin residue outlet 9 at its lower part and an exhaust gas outlet 10 at its upper part. In other drawings, 11
, A hot air generator; and 12, a drive motor for the screw feeder 5.

【0017】このような塩素除去装置によれば、スクリ
ューフィーダー5を通じて被処理樹脂材と熱媒体がロー
タリーキルン本体1の一端側から通路4内に供給される
とともに、熱風導管7から加熱ガスが供給される。通路
4内では上述したようにして被処理樹脂材の脱塩素処理
がなされ、排ガス(加熱ガス+塩化水素ガス)と脱塩素
処理が完了した被処理樹脂材の残渣および熱媒体の混合
体は、ロータリーキルン本体1の他端側の排出装置8に
排出され、排ガスは上部の排ガス排出口10から、また
被処理樹脂材の残渣および熱媒体の混合体は下部の排出
口9から、それぞれ排出される。なお、被処理樹脂材と
熱媒体のロータリーキルン本体1への供給は、それぞれ
別々の供給装置を用いて行ってもよい。
According to such a chlorine removing apparatus, the resin material to be treated and the heat medium are supplied into the passage 4 from one end of the rotary kiln body 1 through the screw feeder 5, and the heating gas is supplied from the hot air conduit 7. You. In the passage 4, as described above, the resin material to be treated is dechlorinated, and a mixture of the exhaust gas (heating gas + hydrogen chloride gas), the residue of the resin material to be treated and the heat medium, which has been dechlorinated, The exhaust gas is discharged to the discharge device 8 at the other end of the rotary kiln main body 1, and the exhaust gas is discharged from the upper exhaust gas discharge port 10, and the mixture of the residue of the resin material to be treated and the heat medium is discharged from the lower discharge port 9. . The supply of the resin material to be processed and the heat medium to the rotary kiln main body 1 may be performed using separate supply devices.

【0018】[0018]

【実施例】図3に示す構造の塩素除去装置を用い、塩化
ビニル樹脂材の脱塩化水素処理を行った。使用した塩素
除去装置の構造及び試験条件は以下の通りである。 ・装置構成 キルン寸法:内径600mmφ×長さ3000mm ロータリーキルン本体の傾斜角:5° ・試験条件 熱風温度:320℃ 熱風供給量:3500Nm3/hr キルン回転数:1rpm
EXAMPLE A vinyl chloride resin material was subjected to dehydrochlorination using a chlorine removing apparatus having the structure shown in FIG. The structure of the chlorine removal apparatus used and the test conditions are as follows. -Equipment configuration Kiln dimensions: 600mm inner diameter x 3000mm length Tilt angle of rotary kiln body: 5 °-Test conditions Hot air temperature: 320 ° C Hot air supply: 3500Nm 3 / hr Kiln rotation speed: 1rpm

【0019】本実施例では被処理樹脂材として、塩素含
有率:35wt%、灰分含有率:2.5wt%、炭素含
有率:56.53wt%、水素含有率:5.96wt
%、粒径10〜20mmの塩化ビニル樹脂を用いた。熱
媒体としては、本発明例では粒径10mm以下粉コーク
スを、また比較例では砂を用いた。
In this embodiment, as the resin material to be treated, chlorine content: 35 wt%, ash content: 2.5 wt%, carbon content: 56.53 wt%, hydrogen content: 5.96 wt
%, A vinyl chloride resin having a particle size of 10 to 20 mm was used. As the heat medium, coke breeze having a particle size of 10 mm or less was used in the present invention, and sand was used in the comparative example.

【0020】○ 本発明例1及び比較例1 樹脂材供給量と熱媒体供給量の重量比を1/1で一定と
した上で、樹脂材供給量を変えて脱塩素処理を行い、樹
脂材の脱塩素率を調べた。その結果を図4に示す。 ○ 本発明例2及び比較例2 樹脂材供給量を100kg/hrで一定とした上で、熱
媒体供給量を変えて脱塩素処理を行い、樹脂材の脱塩素
率および低級炭化水素への分解率を調べた。その結果を
図5に示す。
Inventive Example 1 and Comparative Example 1 After the weight ratio between the resin material supply amount and the heat medium supply amount was kept constant at 1/1, the resin material supply amount was changed to perform dechlorination treatment. Was examined for the dechlorination rate. FIG. 4 shows the results. ○ Inventive Example 2 and Comparative Example 2 After the resin material supply was fixed at 100 kg / hr, dechlorination was performed by changing the heating medium supply, and the resin material was dechlorinated and decomposed into lower hydrocarbons. The rate was checked. The result is shown in FIG.

【0021】図4および図5によれば、熱媒体に粉コー
クスを用いた本発明例ではロータリーキルン内での熱媒
体の偏析が防止されるため、熱媒体に砂を用いた比較例
に較べ高効率に脱塩素処理を行うことができ、また、樹
脂材の低級炭化水素への分解率(ガス化率)も比較例に
較べ低く抑えられている。
According to FIG. 4 and FIG. 5, the segregation of the heating medium in the rotary kiln is prevented in the example of the present invention using coke breeze as the heating medium. The dechlorination treatment can be performed efficiently, and the decomposition rate (gasification rate) of the resin material into lower hydrocarbons is suppressed to be lower than the comparative example.

【0022】[0022]

【発明の効果】以上述べたように本発明の塩素除去方法
によれば、炉装入材料として使用することができる粉粒
物を熱媒体として用いるため、脱塩素処理完了後の樹脂
の残渣を熱媒体と分離することなく、そのまま高炉等を
はじめとする各種の炉(特に溶解炉)に燃料や鉄源の還
元剤等として供給することができる。また、特に熱媒体
として粉コークスを用いることにより熱媒体の偏析等が
防止され、このため脱塩素処理の高い処理効率を確保す
ることができ、且つ樹脂材の低級炭化水素への熱分解も
効果的に抑制することができる。
As described above, according to the chlorine removing method of the present invention, since the powdery granules that can be used as a furnace charging material are used as a heat medium, the resin residue after the completion of the dechlorination treatment is removed. Without being separated from the heat medium, it can be directly supplied to various furnaces (especially melting furnaces) such as a blast furnace as a fuel or a reducing agent for an iron source. In particular, the use of coke breeze as a heating medium prevents segregation of the heating medium, thereby ensuring a high processing efficiency of the dechlorination treatment, and also has an effect of thermally decomposing the resin material into lower hydrocarbons. Can be suppressed.

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

【図1】本発明法の一実施形態を示すもので、ロータリ
ーキルン本体を縦断面した状態で示す説明図
FIG. 1 shows an embodiment of the method of the present invention, and is an explanatory view showing a rotary kiln main body in a longitudinal sectional state.

【図2】本発明法の一実施形態を示すもので、ロータリ
ーキルン本体を横断面した状態で示す説明図
FIG. 2 shows an embodiment of the method of the present invention, and is an explanatory diagram showing a rotary kiln main body in a cross-sectional state.

【図3】本発明の実施に供される塩素除去装置の一構成
例を示す説明図
FIG. 3 is an explanatory diagram showing an example of a configuration of a chlorine removing apparatus provided for carrying out the present invention.

【図4】実施例の本発明例1と比較例1について、樹脂
材供給量と樹脂材の脱塩素率との関係を示すグラフ
FIG. 4 is a graph showing a relationship between a supply amount of a resin material and a dechlorination ratio of the resin material for Example 1 of the present invention and Comparative Example 1 of the embodiment.

【図5】実施例の本発明例2と比較例2について、樹脂
材供給量/熱媒体供給量の重量比と樹脂材の脱塩素率お
よび低級炭化水素への分解率(ガス化率)との関係を示
すグラフ
FIG. 5 shows the weight ratio of the supply amount of the resin material / the supply amount of the heating medium, the dechlorination rate of the resin material, and the decomposition rate (gasification rate) of the resin material to lower hydrocarbons in Example 2 of the present invention and Comparative Example 2. Graph showing the relationship

【符号の説明】[Explanation of symbols]

1…ロータリーキルン本体、2…耐火物、3…鉄皮、4
…通路、5…スクリューフィーダー、6…供給口、7…
熱風導管、8…排出装置、9…排出口、10…排ガス排
出口、11…熱風発生機、12…駆動モータ
1: rotary kiln body, 2: refractory, 3: iron skin, 4
... passage, 5 ... screw feeder, 6 ... supply port, 7 ...
Hot air conduit, 8 ... exhaust device, 9 ... outlet, 10 ... exhaust gas outlet, 11 ... hot air generator, 12 ... drive motor

───────────────────────────────────────────────────── フロントページの続き (72)発明者 冨岡 浩一 東京都千代田区丸の内一丁目1番2号 日 本鋼管株式会社内 ────────────────────────────────────────────────── ─── Continued on the front page (72) Inventor Koichi Tomioka 1-2-1 Marunouchi, Chiyoda-ku, Tokyo Inside Nihon Kokan Co., Ltd.

Claims (3)

【特許請求の範囲】[Claims] 【請求項1】 ロータリキルン方式の塩素除去装置を用
い、ロータリーキルンの通路内に一部または全部が含塩
素高分子樹脂材からなる被処理材を熱媒体とともに供給
し、且つ同じ通路内に加熱ガスを流して含塩素高分子樹
脂材の脱塩素処理を行う含塩素高分子樹脂の塩素除去方
法において、被処理材とともに供給すべき熱媒体とし
て、炉の鉄源、鉄源還元剤、燃料または副原料として使
用できる粉粒物の中から選ばれる1種以上の粉粒物を用
いることを特徴とする含塩素高分子樹脂の塩素除去方
法。
1. A rotary kiln-type chlorine removing apparatus is used to supply a material to be processed, which is partially or entirely made of a chlorine-containing polymer resin material, together with a heat medium into a passage of a rotary kiln, and to supply a heating gas into the same passage. In the method for removing chlorine from a chlorine-containing polymer resin in which the chlorine-containing polymer resin material is dechlorinated by flowing water, the iron source of the furnace, the iron source reducing agent, the fuel or the auxiliary A method for removing chlorine from a chlorine-containing polymer resin, comprising using one or more kinds of powders selected from powders that can be used as a raw material.
【請求項2】 熱媒体として用いる粉粒物が、粉コーク
ス、粉鉱石、焼結粉および粉粒状熱硬化性樹脂の中から
選ばれる1種以上の粉粒物であることを特徴とする請求
項1に記載の含塩素高分子樹脂の塩素除去方法。
2. The powdery material used as the heat medium is at least one kind of powdery material selected from coke breeze, fine ore, sintered powder, and powdery thermosetting resin. Item 6. The method for removing chlorine from a chlorine-containing polymer resin according to Item 1.
【請求項3】 熱媒体として用いる粉粒物が、粉コーク
スおよび粉粒状熱硬化性樹脂の中から選ばれる1種以上
の粉粒物であることを特徴とする請求項1に記載の含塩
素高分子樹脂の塩素除去方法。
3. The chlorine-containing substance according to claim 1, wherein the powdery substance used as the heat medium is at least one kind of powdery substance selected from coke powder and powdery thermosetting resin. Method for removing chlorine from polymer resin.
JP27962297A 1997-01-20 1997-09-26 Chlorine removal from chlorine-containing polymeric resin Pending JPH10259273A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP27962297A JPH10259273A (en) 1997-01-20 1997-09-26 Chlorine removal from chlorine-containing polymeric resin

Applications Claiming Priority (3)

Application Number Priority Date Filing Date Title
JP2104497 1997-01-20
JP9-21044 1997-01-20
JP27962297A JPH10259273A (en) 1997-01-20 1997-09-26 Chlorine removal from chlorine-containing polymeric resin

Publications (1)

Publication Number Publication Date
JPH10259273A true JPH10259273A (en) 1998-09-29

Family

ID=26358058

Family Applications (1)

Application Number Title Priority Date Filing Date
JP27962297A Pending JPH10259273A (en) 1997-01-20 1997-09-26 Chlorine removal from chlorine-containing polymeric resin

Country Status (1)

Country Link
JP (1) JPH10259273A (en)

Cited By (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2009235215A (en) * 2008-03-27 2009-10-15 Ube Ind Ltd Solid fuel and method for manufacturing solid fuel
JP2011057750A (en) * 2009-09-07 2011-03-24 Ube Industries Ltd Solid fuel and method for producing the same
JP2011068769A (en) * 2009-09-25 2011-04-07 Ube Industries Ltd Solid fuel and manufacturing method therefor
JP2011068771A (en) * 2009-09-25 2011-04-07 Ube Industries Ltd Solid fuel and manufacturing method therefor
JP2011068770A (en) * 2009-09-25 2011-04-07 Ube Industries Ltd Solid fuel and manufacturing method therefor
JP2012031283A (en) * 2010-07-30 2012-02-16 Taiheiyo Cement Corp Method of manufacturing fuel

Cited By (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2009235215A (en) * 2008-03-27 2009-10-15 Ube Ind Ltd Solid fuel and method for manufacturing solid fuel
JP2011057750A (en) * 2009-09-07 2011-03-24 Ube Industries Ltd Solid fuel and method for producing the same
JP2011068769A (en) * 2009-09-25 2011-04-07 Ube Industries Ltd Solid fuel and manufacturing method therefor
JP2011068771A (en) * 2009-09-25 2011-04-07 Ube Industries Ltd Solid fuel and manufacturing method therefor
JP2011068770A (en) * 2009-09-25 2011-04-07 Ube Industries Ltd Solid fuel and manufacturing method therefor
JP2012031283A (en) * 2010-07-30 2012-02-16 Taiheiyo Cement Corp Method of manufacturing fuel

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