JPH10216674A - Treatment of chlorine-containing plastic waste and device therefor - Google Patents

Treatment of chlorine-containing plastic waste and device therefor

Info

Publication number
JPH10216674A
JPH10216674A JP9024877A JP2487797A JPH10216674A JP H10216674 A JPH10216674 A JP H10216674A JP 9024877 A JP9024877 A JP 9024877A JP 2487797 A JP2487797 A JP 2487797A JP H10216674 A JPH10216674 A JP H10216674A
Authority
JP
Japan
Prior art keywords
carbonization
hydrogen chloride
dry distillation
gas
chlorine
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
JP9024877A
Other languages
Japanese (ja)
Inventor
Yoshitoshi Sekiguchi
善利 関口
Kunio Sasaki
邦夫 佐々木
Kenji Nishiyama
健治 西山
Takusen Ito
拓仙 伊藤
Iwao Yanaka
巌 谷中
Osamu Onishi
修 尾西
Sanji Morimoto
三次 森本
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.)
KEIHANNA KANKYO KK
Hitachi Zosen Corp
Osaka Gas Engineering Co Ltd
Original Assignee
KEIHANNA KANKYO KK
Hitachi Zosen Corp
Osaka Gas Engineering Co 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 KEIHANNA KANKYO KK, Hitachi Zosen Corp, Osaka Gas Engineering Co Ltd filed Critical KEIHANNA KANKYO KK
Priority to JP9024877A priority Critical patent/JPH10216674A/en
Publication of JPH10216674A publication Critical patent/JPH10216674A/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
    • Y02PCLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P20/00Technologies relating to chemical industry
    • Y02P20/141Feedstock
    • Y02P20/143Feedstock the feedstock being recycled material, e.g. plastics

Landscapes

  • Chimneys And Flues (AREA)
  • Gasification And Melting Of Waste (AREA)
  • Processing Of Solid Wastes (AREA)
  • Coke Industry (AREA)

Abstract

PROBLEM TO BE SOLVED: To enable discharging of an incineration discharge gas into air by subjecting a chlorine-contg. plastic waste to dry distillation, absorbing the hydrogen chloride gas produced by the dry distillation to water to collect, and incinerating the carbon residue after the dry distillation. SOLUTION: A waste of polyvinyl chloride products is put in a furnace 2 for dry distillation and incineration, then a boiler 6 and a heating furnace 8 are operated to produce an overheated vapor, which is supplied to the furnace 2 to dry distillate the waste. The discharged gas containing the overheated vapor, the gas produced by dry distillation and hydrogen chloride gas produced by dry distillation is sent through a gas cooling device 14, a hydrogen chloride concentration meter 6 and a switching valve 15 to a collecting device 3 for hydrogen chloride, where the discharged gas is successively introduced to bubble in three water tanks 16 to 18. Thereby, the overheated vapor in the discharged gas is condensed into water and recovered. The hydrogen chloride gas is absorbed by the water while the gas produced by dry distillation is passed through the water tank 18 and then supplied by a blower 24 to a burner of the heating furnace 8 with air for combustion. Thus, the gas produced by dry distillation is rendered harmless.

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】この発明は、ポリ塩化ビニル
やポリ塩化ビニリデンのような塩素含有プラスチックの
廃棄物を効率よく処理する方法およびこの方法を実施す
るための処理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 a method for efficiently treating a chlorine-containing plastic waste such as polyvinyl chloride and polyvinylidene chloride, and a treatment apparatus for carrying out the method.

【0002】この明細書において、塩素含有プラスチッ
クの廃棄物とは、塩素含有プラスチックのみからなる廃
棄物のほか、少なくとも一部が塩素含有プラスチックで
構成されている複合材ないしはその製品の廃棄物をも意
味することとする。
[0002] In this specification, the term "chlorine-containing plastic waste" refers to not only waste consisting of chlorine-containing plastic but also waste of a composite material or a product thereof at least partially composed of chlorine-containing plastic. Shall mean.

【0003】[0003]

【従来の技術】塩素含有プラスチックの廃棄物は、これ
をそのまま焼却処理すると塩化水素ガスが多量に発生す
るとともに有害なダイオキシンが発生しやすいため、従
来はほとんど埋立て処理されていた。
2. Description of the Related Art Waste of chlorine-containing plastics has been conventionally disposed of in landfills when incinerated as it produces a large amount of hydrogen chloride gas and harmful dioxins.

【0004】[0004]

【発明が解決しようとする課題】しかし、埋立て地の確
保は次第に困難になって来ており、新たな処理策が求め
られている。
However, it is becoming increasingly difficult to secure landfill sites, and new treatment measures are required.

【0005】この発明は上記の要望に応えることができ
る塩素含有プラスチックの処理方法およびこの方法を実
施するための処理装置を提供することを目的とする。
An object of the present invention is to provide a method for treating chlorine-containing plastics which can meet the above-mentioned demands, and a treatment apparatus for performing the method.

【0006】[0006]

【課題を解決するための手段】本発明による塩素含有プ
ラスチック廃棄物の処理方法は、塩素含有プラスチック
廃棄物を乾留し、乾留に伴って発生した塩化水素ガスを
水に吸収させて回収し、乾留終了後にカーボン残渣を焼
却することを特徴とする。
According to the present invention, there is provided a method for treating chlorine-containing plastic waste, which comprises subjecting chlorine-containing plastic waste to dry distillation, absorbing and collecting hydrogen chloride gas generated by the dry distillation, and subjecting the waste to carbonization. After the completion, the carbon residue is incinerated.

【0007】この方法において、塩素含有プラスチック
廃棄物の乾留用熱源として好ましくは過熱蒸気を用い、
乾留後の過熱蒸気を冷却し塩化水素回収工程で凝縮水と
して回収する。
In this method, superheated steam is preferably used as a heat source for carbonization of chlorine-containing plastic waste,
The superheated steam after the carbonization is cooled and recovered as condensed water in a hydrogen chloride recovery step.

【0008】また、乾留によって発生した乾留ガスを塩
化水素回収後に乾留用熱源を発生するための補助燃料と
して用いることもできる。
[0008] The carbonized gas generated by carbonization can also be used as an auxiliary fuel for generating a carbonization heat source after recovering hydrogen chloride.

【0009】乾留工程と塩化水素回収工程の間で塩化水
素濃度を測定し、得られた測定値によって乾留終了を確
認した後、カーボン残渣の焼却を行うことが好ましい。
Preferably, the concentration of hydrogen chloride is measured between the carbonization step and the hydrogen chloride recovery step, and the carbonization residue is incinerated after confirming the completion of carbonization based on the measured values.

【0010】本発明による塩素含有プラスチック廃棄物
の処理方法を実施するには、次の装置を用いる。
The following apparatus is used to carry out the method for treating chlorine-containing plastic waste according to the present invention.

【0011】すなわち、塩素含有プラスチック廃棄物を
乾留するとともに乾留後のカーボン残渣を焼却する乾留
兼焼却炉と、乾留兼焼却炉で乾留に伴って発生した塩化
水素ガスを水に吸収させる塩化水素回収装置を具備して
なる塩素含有プラスチック廃棄物の処理装置。
That is, a carbonization / incinerator for carbonizing chlorine-containing plastic waste and incinerating carbon residues after carbonization, and a hydrogen chloride recovery system for absorbing hydrogen chloride gas generated by carbonization in the carbonization / incineration furnace into water. An apparatus for treating chlorine-containing plastic waste, comprising an apparatus.

【0012】上記構成の装置は、好ましくは、乾留用の
過熱蒸気を発生して乾留兼焼却炉へ送る過熱蒸気発生装
置を具備している。また、上記構成の装置は、好ましく
は、乾留によって発生し塩化水素回収装置を通過した乾
留ガスを過熱蒸気発生装置へ送るラインを具備してい
る。
The apparatus having the above configuration preferably includes a superheated steam generator for generating superheated steam for dry distillation and sending it to the incinerator. Further, the apparatus having the above configuration preferably includes a line for sending the carbonized gas generated by carbonization and passing through the hydrogen chloride recovery device to the superheated steam generator.

【0013】乾留兼焼却炉と塩化水素回収装置の間に好
ましくは塩化水素濃度計が設けられている。
[0013] A hydrogen chloride concentration meter is preferably provided between the dry distillation and incinerator and the hydrogen chloride recovery device.

【0014】[0014]

【発明の実施の形態】まず、この発明による塩素含有プ
ラスチック廃棄物の処理装置について、図面に基づいて
説明をする。
DETAILED DESCRIPTION OF THE PREFERRED EMBODIMENTS First, an apparatus for treating chlorine-containing plastic waste according to the present invention will be described with reference to the drawings.

【0015】この発明による塩素含有プラスチック廃棄
物の処理装置は、乾留用の過熱蒸気を発生する過熱蒸気
発生装置(1) と、過熱蒸気発生装置(1) から来る過熱蒸
気によって塩素含有プラスチックの廃棄物を乾留すると
ともに乾留後のカーボン残渣を焼却する乾留兼焼却炉
(2) と、乾留兼焼却炉(2) で乾留に伴って発生した塩化
水素ガスを水に吸収させる塩化水素回収装置(3) と、乾
留によって発生し塩化水素回収装置(3)を通過した乾留
ガスを過熱蒸気発生装置(1) へ供給するライン(4)と、
乾留兼焼却炉(2) と塩化水素回収装置(3) の間に設けら
れた塩化水素濃度計(5) とから主として構成されてい
る。
An apparatus for treating chlorine-containing plastic waste according to the present invention comprises a superheated steam generator (1) for generating superheated steam for dry distillation, and a chlorine-containing plastic waste disposed by superheated steam coming from the superheated steam generator (1). A carbonization and incinerator that carbonizes materials and incinerates carbon residues after carbonization.
(2), a hydrogen chloride recovery unit (3) that absorbs hydrogen chloride gas generated by dry distillation in the carbonization and incinerator (2), and a hydrogen chloride recovery unit (3) generated by dry distillation and passed through A line (4) for supplying the carbonized gas to the superheated steam generator (1),
It mainly consists of a hydrogen chloride concentration meter (5) installed between the carbonization and incinerator (2) and the hydrogen chloride recovery unit (3).

【0016】過熱蒸気発生装置(1) は、ボイラ(6) と、
ボイラ(6) から水蒸気弁(7) を経て来る水蒸気を加熱し
て過熱蒸気を発生する加熱炉(8) とからなる。加熱炉
(8) のバーナ(9) には燃料弁(10)を経て燃料が供給さ
れ、ブロワ(24)によって空気弁(21)を経て燃焼用空気が
供給される。
The superheated steam generator (1) comprises a boiler (6) and
A heating furnace (8) for heating steam coming from the boiler (6) through the steam valve (7) to generate superheated steam. heating furnace
Fuel is supplied to the burner (9) of (8) through a fuel valve (10), and combustion air is supplied by a blower (24) through an air valve (21).

【0017】乾留兼焼却炉(2) は、縦長ドラム状であっ
て、頂部に蓋体(11)を備え、底部一側にバーナ(12)を有
し、さらに内部下端寄りに火格子(13)を有している。バ
ーナ(12)には燃料弁(23)を経て燃料が供給され、ブロワ
(24)によって空気弁(22)を経て燃焼用空気が供給され
る。加熱炉(8) から来る過熱蒸気は火格子(13)の上のレ
ベルにて乾留兼焼却炉(2) 内に周壁から中心部に向かっ
て噴射供給される。また、乾留兼焼却炉(2) にはその内
部温度を測定してコントロールする温度制御装置(24)が
設けられている。
The carbonization and incinerator (2) has a vertically long drum shape, has a lid (11) on the top, has a burner (12) on one side of the bottom, and has a grate (13) near the lower end inside. )have. Fuel is supplied to the burner (12) via a fuel valve (23),
By (24), combustion air is supplied via an air valve (22). The superheated steam coming from the heating furnace (8) is injected and supplied from the peripheral wall toward the center into the carbonization and incinerator (2) at a level above the grate (13). The carbonization and incinerator (2) is provided with a temperature controller (24) for measuring and controlling the internal temperature.

【0018】乾留兼焼却炉(2) の後流にはガス冷却装置
(14)と塩化水素濃度計(5) と切り換え弁(15)と塩化水素
回収装置(3) とがこの順に設けられている。
A gas cooling device is provided downstream of the dry distillation and incinerator (2).
(14), a hydrogen chloride concentration meter (5), a switching valve (15), and a hydrogen chloride recovery device (3) are provided in this order.

【0019】塩化水素回収装置(3) は、3基の水槽(16)
(17)(18)からなり、ガス冷却装置(14)から来たガスが各
槽で順次バブリングされる。ガス冷却装置(14)と3基の
水槽(16)(17)(18)にはこれらを巡る冷却水がクーリング
タワー(20)を経てポンプ(19)によって循環させられてい
る。
The hydrogen chloride recovery unit (3) comprises three water tanks (16)
The gas coming from the gas cooling device (14) consisting of (17) and (18) is sequentially bubbled in each tank. Cooling water circulating through the gas cooling device (14) and the three water tanks (16), (17), (18) is circulated by a pump (19) through a cooling tower (20).

【0020】ライン(4) は、最終の水槽(18)を通過した
乾留ガスをブロワ(24)によって空気弁(21)を経て加熱炉
(8) のバーナ(9) へ送る。
The line (4) is connected to a heating furnace through an air valve (21) by a blower (24).
Send it to the burner (9) in (8).

【0021】乾留兼焼却炉(2) にはその内部温度を測定
してコントロールする温度制御装置(24)が設けられてい
る。
The dry distillation and incinerator (2) is provided with a temperature control device (24) for measuring and controlling the internal temperature.

【0022】上記構成の塩素含有プラスチック廃棄物の
処理装置において、まず、乾留兼焼却炉(2) にポリ塩化
ビニル製品の廃棄物を投入しておく。次いでボイラ(6)
と過熱炉(8) を稼働して過熱蒸気を発生させ、乾留兼焼
却炉(2) に噴射供給して、所定炉内温度(400℃〜6
00℃)にて所定時間(30分〜2時間)、廃棄物を乾
留処理する。この温度コントロールは、温度制御装置(2
4)による測定温度に基づいて過熱蒸気発生装置(1) の水
蒸気弁(7) 、燃料弁(10)および空気弁(21)の開き具合を
自動的に調整することによって行う。
In the apparatus for treating chlorine-containing plastic waste having the above-mentioned structure, first, the waste of polyvinyl chloride product is put into the carbonization and incinerator (2). Then boiler (6)
And a superheating furnace (8) to operate to generate superheated steam, which is injected and supplied to a carbonization and incineration furnace (2) to obtain a predetermined furnace temperature (400 ° C to 6 ° C).
(00 ° C.) for a predetermined time (30 minutes to 2 hours). This temperature control uses a temperature control device (2
This is performed by automatically adjusting the degree of opening of the steam valve (7), fuel valve (10) and air valve (21) of the superheated steam generator (1) based on the temperature measured by 4).

【0023】乾留に用いた過熱蒸気と乾留によって発生
した乾留ガスと乾留に伴って発生した塩化水素ガスとを
含む排ガスを、乾留兼焼却炉(2) の頂部からガス冷却装
置(14)、塩化水素濃度計(5) および切り換え弁(15)を介
して塩化水素回収装置(3) へ送り、同装置(3) の3基の
水槽(16)(17)(18)の水中に順次バブリングする。排ガス
中の過熱蒸気はガス冷却装置(14)の通過ついで3基の水
槽(16)(17)(18)でのバブリングによって冷却され、凝縮
水として水槽内の水に回収される。また、塩化水素ガス
は3基の水槽(16)(17)(18)でのバブリングによって水に
吸収される。乾留ガスは水槽(16)(17)(18)でのバブリン
グでは水に吸収されない。最終の水槽(18)を通過した乾
留ガスを、ライン(4) によってブロワ(24)で弁(21)を経
て燃焼用空気と共に加熱炉(8) のバーナ(9) へ供給し、
同バーナ(9) の補助燃料として用いると同時に、乾留ガ
スの無害化処理を行う。
Exhaust gas containing the superheated steam used for the carbonization, the carbonization gas generated by the carbonization, and the hydrogen chloride gas generated by the carbonization was discharged from the top of the carbonization and incinerator (2) to a gas cooling device (14). It is sent to the hydrogen chloride recovery unit (3) via the hydrogen concentration meter (5) and the switching valve (15), and is sequentially bubbled into the water in the three water tanks (16), (17) and (18) of the unit (3) . The superheated steam in the exhaust gas is cooled by bubbling in three water tanks (16), (17), and (18) after passing through the gas cooling device (14), and is recovered as water in the water tank as condensed water. Hydrogen chloride gas is absorbed by water by bubbling in three water tanks (16), (17) and (18). The carbonization gas is not absorbed by water when bubbling in water tanks (16), (17) and (18). The dry distillation gas passed through the final water tank (18) is supplied to the burner (9) of the heating furnace (8) together with the combustion air via the valve (21) by the blower (24) by the line (4),
At the same time as using it as an auxiliary fuel for the burner (9), the carbonized gas is made harmless.

【0024】乾留兼焼却炉(2) から出た排ガス中の塩化
水素濃度をガス冷却装置(14)の後流で塩化水素濃度計
(5) で測定し、塩化水素ガスの発生がなくなって乾留が
終了したことを確認した後、切り換え弁(15)を排気側
(B) へ手動でまたは自動的に切り換え、過熱蒸気発生装
置(1) の水蒸気弁(7) 、燃料弁(10)および空気弁(10)を
いずれも閉じ、他方、乾留兼焼却炉(2) の燃料弁(23)お
よび空気弁(22)を開く。ついで、過熱蒸気発生装置(1)
のバーナ(12)を点火し、炉内温度を所定温度(800℃
以上)にコントロールし、火格子(13)上に残ったカーボ
ン残渣を焼却処理する。この温度コントロールは、温度
制御装置(24)による測定温度に基づいて乾留兼焼却炉
(2) の燃料弁(23)および空気弁(22)の開き具合を自動的
に調整することによって行う。このようにして、各弁を
乾留モード(A) から焼却モード(B) へ切り換え、カーボ
ン残渣を完全に焼却処理する。その結果、カーボン残渣
は完全に脱塩素化されている。また、発生した焼却ガス
は塩化水素ガスを含まないので、同ガスをそのまま大気
に放出できる。
The concentration of hydrogen chloride in the exhaust gas discharged from the carbonization and incinerator (2) is measured by a hydrogen chloride concentration meter downstream of the gas cooling device (14).
After confirming that hydrogen chloride gas is no longer generated and dry distillation is completed, set the switching valve (15) to the exhaust side.
(B) is switched manually or automatically, and the steam valve (7), fuel valve (10) and air valve (10) of the superheated steam generator (1) are all closed. ) Open the fuel valve (23) and air valve (22). Next, superheated steam generator (1)
The burner (12) is ignited and the furnace temperature is raised to a predetermined temperature (800 ° C).
And the carbon residue remaining on the grate (13) is incinerated. This temperature control is based on the temperature measured by the temperature controller (24).
This is performed by automatically adjusting the opening degree of the fuel valve (23) and the air valve (22) in (2). In this way, each valve is switched from the carbonization mode (A) to the incineration mode (B), and the carbon residue is completely incinerated. As a result, the carbon residue is completely dechlorinated. Further, since the generated incineration gas does not contain hydrogen chloride gas, the gas can be released to the atmosphere as it is.

【0025】[0025]

【発明の効果】この発明の効果は次のとおりである。The effects of the present invention are as follows.

【0026】1)塩素含有プラスチック廃棄物を乾留
し、乾留に伴って発生した塩化水素ガスを水に吸収させ
て回収するので、乾留後のカーボン残渣の焼却排ガスに
は塩化水素ガスが含まれず、したがってこの焼却排ガス
をそのまま大気中へ排出することができる。
1) Since carbon-containing plastic waste is carbonized, and hydrogen chloride gas generated by carbonization is absorbed in water and collected, the incineration exhaust gas of carbon residue after carbonization does not contain hydrogen chloride gas. Therefore, the incineration exhaust gas can be directly discharged into the atmosphere.

【0027】2)乾留とその後の焼却とを1基の炉で行
うことができるので、装置の建設費のコストダウンが達
成できる。
2) Since the carbonization and the subsequent incineration can be performed in one furnace, the construction cost of the apparatus can be reduced.

【0028】3)乾留用の熱源として過熱蒸気を使用す
る方法では、乾留後の過熱蒸気を冷却凝縮して回収する
ことによって、処理すべき排ガス量を大幅に減少させる
ことができる。
3) In the method using superheated steam as a heat source for dry distillation, the amount of exhaust gas to be treated can be greatly reduced by cooling and condensing the superheated steam after dry distillation to recover it.

【0029】4)乾留ガスを過熱蒸気発生装置へ送る方
法では、乾留ガスを同装置の補助燃料として用いて燃料
の節減を図り、乾留ガスの燃焼無害化処理を達成するこ
とができる。
4) In the method of sending the carbonized gas to the superheated steam generator, the carbonized gas can be used as an auxiliary fuel for the device to save fuel and achieve the combustion detoxification treatment of the carbonized gas.

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

【図1】本発明の実施例を示す管系統図である。FIG. 1 is a pipe system diagram showing an embodiment of the present invention.

【符号の説明】[Explanation of symbols]

1:過熱蒸気発生装置 2:乾留兼焼却炉 3:塩化水素回収装置 4:ライン 5:塩化水素濃度計 1: Superheated steam generator 2: Dry distillation and incinerator 3: Hydrogen chloride recovery device 4: Line 5: Hydrogen chloride concentration meter

───────────────────────────────────────────────────── フロントページの続き (51)Int.Cl.6 識別記号 FI F23J 15/02 F23J 15/00 C (72)発明者 関口 善利 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 (72)発明者 佐々木 邦夫 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 (72)発明者 西山 健治 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 (72)発明者 伊藤 拓仙 奈良県生駒市高山町8916−12 関西学研都 市サイエンスプラザ3F けいはんな環境 株式会社内 (72)発明者 谷中 巌 奈良県生駒市高山町8916−12 関西学研都 市サイエンスプラザ3F けいはんな環境 株式会社内 (72)発明者 尾西 修 大阪市東成区中道1丁目4番2号 大阪ガ スエンジニアリング株式会社内 (72)発明者 森本 三次 大阪市東成区中道1丁目4番2号 大阪ガ スエンジニアリング株式会社内──────────────────────────────────────────────────続 き Continued on the front page (51) Int.Cl. 6 Identification code FI F23J 15/02 F23J 15/00 C (72) Inventor Yoshitoshi Sekiguchi 5-28 Nishikujo, Konohana-ku, Osaka Hitachi Zosen Corporation (72) Inventor Kunio Sasaki 5-3-28 Nishikujo, Konohana-ku, Osaka-shi Within Hitachi Zosen Corporation (72) Inventor Kenji Nishiyama 5-3-28 Nishikujo, Konohana-ku, Osaka-shi Within Hitachi Zosen Corporation ( 72) Inventor Takusen Ito 8916-12 Takayama-cho, Ikoma City, Nara Prefecture Science Plaza 3F, Kwanai Gakuto City Inside Keihanna Environment Co., Ltd. 3F Keihanna Environment Co., Ltd. (72) Inventor: Osamu Onishi 1-4-2 Nakamichi, Higashinari-ku, Osaka City Osaka Gas Engineering Co., Ltd. Within the company (72) inventor Morimoto tertiary Osaka Higashinari-ku, centrist 1-chome No. 4 No. 2 Osaka Gas Engineering Co., Ltd. in

Claims (8)

【特許請求の範囲】[Claims] 【請求項1】 塩素含有プラスチック廃棄物を乾留し、
乾留に伴って発生した塩化水素ガスを水に吸収させて回
収し、乾留終了後にカーボン残渣を焼却する塩素含有プ
ラスチック廃棄物の処理方法。
Claims 1. A chlorine-containing plastic waste is carbonized,
A method for treating chlorine-containing plastic waste in which hydrogen chloride gas generated during carbonization is absorbed by water and collected, and carbon residues are incinerated after carbonization.
【請求項2】 塩素含有プラスチック廃棄物の乾留用熱
源として過熱蒸気を用い、乾留後の過熱蒸気を冷却し塩
化水素回収工程で凝縮水として回収する請求項1記載の
方法。
2. The method according to claim 1, wherein superheated steam is used as a heat source for dry distillation of chlorine-containing plastic waste, and the superheated steam after dry distillation is cooled and recovered as condensed water in a hydrogen chloride recovery step.
【請求項3】 乾留によって発生した乾留ガスを塩化水
素回収後に乾留用熱源を発生するための補助燃料として
用いる請求項1または2記載の方法。
3. The method according to claim 1, wherein the carbonization gas generated by carbonization is used as an auxiliary fuel for generating a carbonization heat source after recovering hydrogen chloride.
【請求項4】 乾留工程と塩化水素回収工程の間で塩化
水素濃度を測定し、得られた測定値によって乾留終了を
確認した後、カーボン残渣の焼却を行う請求項1〜3の
うち1項記載の方法。
4. The method according to claim 1, wherein the concentration of hydrogen chloride is measured between the carbonization step and the hydrogen chloride recovery step, and the carbonization residue is incinerated after confirming the completion of carbonization based on the measured value. The described method.
【請求項5】 塩素含有プラスチック廃棄物を乾留する
とともに乾留後のカーボン残渣を焼却する乾留兼焼却炉
と、乾留兼焼却炉で乾留に伴って発生した塩化水素ガス
を水に吸収させる塩化水素回収装置を具備してなる塩素
含有プラスチック廃棄物の処理装置。
5. A carbonization and incinerator for carbonizing chlorine-containing plastic waste and incinerating carbon residues after carbonization, and hydrogen chloride recovery for absorbing hydrogen chloride gas generated by carbonization in the carbonization and incinerator in water. An apparatus for treating chlorine-containing plastic waste, comprising an apparatus.
【請求項6】 乾留用の過熱蒸気を発生して乾留兼焼却
炉へ送る過熱蒸気発生装置が設けられている請求項5記
載の装置。
6. The apparatus according to claim 5, further comprising a superheated steam generator that generates superheated steam for carbonization and sends it to the carbonization and incinerator.
【請求項7】 乾留によって発生し塩化水素回収装置を
通過した乾留ガスを過熱蒸気発生装置へ送るラインが設
けられている請求項6記載の装置。
7. The apparatus according to claim 6, further comprising a line for sending the carbonized gas generated by carbonization and passing through the hydrogen chloride recovery device to a superheated steam generator.
【請求項8】 乾留兼焼却炉と塩化水素回収装置の間に
塩化水素濃度計が設けられている請求項5〜7のうち1
項記載の装置。
8. A hydrogen chloride concentration meter is provided between the dry distillation and incinerator and the hydrogen chloride recovery device.
Item.
JP9024877A 1997-02-07 1997-02-07 Treatment of chlorine-containing plastic waste and device therefor Pending JPH10216674A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP9024877A JPH10216674A (en) 1997-02-07 1997-02-07 Treatment of chlorine-containing plastic waste and device therefor

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP9024877A JPH10216674A (en) 1997-02-07 1997-02-07 Treatment of chlorine-containing plastic waste and device therefor

Publications (1)

Publication Number Publication Date
JPH10216674A true JPH10216674A (en) 1998-08-18

Family

ID=12150437

Family Applications (1)

Application Number Title Priority Date Filing Date
JP9024877A Pending JPH10216674A (en) 1997-02-07 1997-02-07 Treatment of chlorine-containing plastic waste and device therefor

Country Status (1)

Country Link
JP (1) JPH10216674A (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2001051587A1 (en) * 2000-01-14 2001-07-19 Ryoichi Okamoto Dry-distilling/volume reducing device for wastes
JP2012011299A (en) * 2010-06-30 2012-01-19 Altis:Kk Pyrolyzer, dechlorination treatment apparatus, pyrolysis method and dechlorination method

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2001051587A1 (en) * 2000-01-14 2001-07-19 Ryoichi Okamoto Dry-distilling/volume reducing device for wastes
JP2012011299A (en) * 2010-06-30 2012-01-19 Altis:Kk Pyrolyzer, dechlorination treatment apparatus, pyrolysis method and dechlorination method

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