Deprecated: The each() function is deprecated. This message will be suppressed on further calls in /home/zhenxiangba/zhenxiangba.com/public_html/phproxy-improved-master/index.php on line 456
JPS5856556B2 - Heat treatment method for waste vinyl chloride resin, etc. - Google Patents
[go: Go Back, main page]

JPS5856556B2 - Heat treatment method for waste vinyl chloride resin, etc. - Google Patents

Heat treatment method for waste vinyl chloride resin, etc.

Info

Publication number
JPS5856556B2
JPS5856556B2 JP54112218A JP11221879A JPS5856556B2 JP S5856556 B2 JPS5856556 B2 JP S5856556B2 JP 54112218 A JP54112218 A JP 54112218A JP 11221879 A JP11221879 A JP 11221879A JP S5856556 B2 JPS5856556 B2 JP S5856556B2
Authority
JP
Japan
Prior art keywords
gas
heat treatment
combustion
pyrolysis
vinyl chloride
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
Application number
JP54112218A
Other languages
Japanese (ja)
Other versions
JPS5637120A (en
Inventor
剛 山田
克巳 松島
隆生 青葉
豊司 北島
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.)
Chugai Ro Co Ltd
Original Assignee
Chugai Ro 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 Chugai Ro Co Ltd filed Critical Chugai Ro Co Ltd
Priority to JP54112218A priority Critical patent/JPS5856556B2/en
Publication of JPS5637120A publication Critical patent/JPS5637120A/en
Publication of JPS5856556B2 publication Critical patent/JPS5856556B2/en
Expired legal-status Critical Current

Links

Classifications

    • BPERFORMING OPERATIONS; TRANSPORTING
    • B29WORKING OF PLASTICS; WORKING OF SUBSTANCES IN A PLASTIC STATE IN GENERAL
    • B29BPREPARATION OR PRETREATMENT OF THE MATERIAL TO BE SHAPED; MAKING GRANULES OR PREFORMS; RECOVERY OF PLASTICS OR OTHER CONSTITUENTS OF WASTE MATERIAL CONTAINING PLASTICS
    • B29B17/00Recovery of plastics or other constituents of waste material containing plastics
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B29WORKING OF PLASTICS; WORKING OF SUBSTANCES IN A PLASTIC STATE IN GENERAL
    • B29BPREPARATION OR PRETREATMENT OF THE MATERIAL TO BE SHAPED; MAKING GRANULES OR PREFORMS; RECOVERY OF PLASTICS OR OTHER CONSTITUENTS OF WASTE MATERIAL CONTAINING PLASTICS
    • B29B13/00Conditioning or physical treatment of the material to be shaped
    • B29B13/02Conditioning or physical treatment of the material to be shaped by heating
    • 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

  • Engineering & Computer Science (AREA)
  • Mechanical Engineering (AREA)
  • Physics & Mathematics (AREA)
  • Thermal Sciences (AREA)
  • Environmental & Geological Engineering (AREA)
  • Processing And Handling Of Plastics And Other Materials For Molding In General (AREA)
  • Separation, Recovery Or Treatment Of Waste Materials Containing Plastics (AREA)
  • Production Of Liquid Hydrocarbon Mixture For Refining Petroleum (AREA)

Description

【発明の詳細な説明】 この発明は、廃塩化ビニール樹脂等の熱処理方法に関す
るものである。
DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a method for heat treating waste vinyl chloride resin, etc.

従来、塩化ビニール樹脂等の廃棄物の処理方法としては
、熱分解室において熱処理し、その熱分解生成ガスを水
蒸気によって熱分解ガス凝縮塔に導いて、塩化水素を凝
縮し、さらに、分離器によって塩酸を回収するようにな
っているもの等が存在する。
Conventionally, wastes such as vinyl chloride resin are treated by heat treatment in a pyrolysis chamber, and the resulting pyrolysis gas is led to a pyrolysis gas condensation tower using steam to condense hydrogen chloride, and then to a separator to condense hydrogen chloride. There are some that are designed to recover hydrochloric acid.

ところが、上記の方法では、熱分解生成ガスは、水蒸気
により熱分解ガス凝縮塔に導くようになっており、その
搬送中の低温部分で塩化水素が凝縮しやすいため、ダク
ト等に腐食が生じる。
However, in the above method, the pyrolysis product gas is guided to the pyrolysis gas condensation tower by steam, and hydrogen chloride is likely to condense in the low-temperature portion during transportation, resulting in corrosion of the ducts and the like.

また、凝縮水量が多いため高い濃度の塩酸を回収するこ
とができない等の問題があった。
In addition, there were other problems such as the inability to recover highly concentrated hydrochloric acid due to the large amount of condensed water.

この発明は、上記問題点を考慮してなされたものであっ
て、その目的は、炭化水素系燃料の燃焼生成ガスで、あ
らかじめ熱分解室内をパージして不活性雰囲気とすると
ともに、塩化ビニール樹脂および/または熱可塑性合成
樹脂廃棄物の被処理材の熱処理時に発生する熱分解生成
ガスを熱分解室外部に搬送するようにして、爆発、処理
装置の腐食等の阻止を図り、かつ、高濃度の塩酸等を回
収することができる廃塩化ビニール樹脂等の熱処理方法
およびその装置を提供しようとするものである。
This invention was made in consideration of the above-mentioned problems, and its purpose is to purge the inside of the pyrolysis chamber to create an inert atmosphere in advance with the combustion generated gas of hydrocarbon fuel, and to and/or the thermal decomposition gas generated during heat treatment of materials to be treated, such as thermoplastic synthetic resin waste, is transported to the outside of the thermal decomposition chamber to prevent explosions, corrosion of processing equipment, etc., and to achieve high concentration. The purpose of the present invention is to provide a heat treatment method for waste vinyl chloride resin, etc., which can recover hydrochloric acid, etc., and an apparatus therefor.

以下、この発明を図面に示す一実施例で説明する。The present invention will be explained below with reference to an embodiment shown in the drawings.

図は、この発明にかかる方法を実現するための具体的な
構成を示す配置図であって、間接加熱型熱分解炉1は、
熱分解室2と、これを包囲し加熱するための加熱炉2a
とから構成し熱分解室2には、廃塩化ビニール樹脂等の
被処理材装入口3および炭化水素系燃料の燃焼生成ガス
(以下、燃焼排ガス、DXガスなどの炭化水素系燃料の
燃焼生成ガスを、単に燃焼生成ガスという。
The figure is a layout diagram showing a specific configuration for realizing the method according to the present invention, and the indirect heating type pyrolysis furnace 1 includes:
A pyrolysis chamber 2 and a heating furnace 2a for surrounding and heating the pyrolysis chamber 2
The pyrolysis chamber 2 has an inlet 3 for charging materials to be treated such as waste vinyl chloride resin, and a gas generated by combustion of hydrocarbon fuel (hereinafter referred to as combustion exhaust gas, gas generated by combustion of hydrocarbon fuel such as DX gas). is simply called combustion gas.

)供給口4が設けられている。) A supply port 4 is provided.

この燃焼生成ガス供給口4は、燃焼生成ガス発生機5に
接続されている。
This combustion gas supply port 4 is connected to a combustion gas generator 5.

また、熱分解室2は、ダクト6を介してクーラ7、循環
ポンプ8を備えた熱分解生成ガス凝縮基9に接続されて
おり、上記被処理材の熱処理時に発生する熱分解生成ガ
スは、上記燃焼生成ガスによって上記凝縮基9に搬送さ
れるようになっている。
The pyrolysis chamber 2 is connected via a duct 6 to a pyrolysis product gas condensing unit 9 equipped with a cooler 7 and a circulation pump 8, and the pyrolysis product gas generated during the heat treatment of the material to be treated is The combustion product gas is transported to the condensing group 9.

上記凝縮基9は循環ポンプ10を備えた熱分解塗床ガス
冷却洗滌塔11に接続されて、この冷却洗滌基11には
凝縮基9を通過した熱分解生成ガスが導かれる。
The condensing group 9 is connected to a pyrolysis coating bed gas cooling and washing tower 11 equipped with a circulation pump 10, and the pyrolysis product gas that has passed through the condensing group 9 is guided to this cooling and washing group 11.

そして、この冷却洗滌基11は、カスポンプ12を介し
てガスタンク13に接続されて、冷却洗滌基11で精製
された熱分解生成ガスを貯留する。
The cooling washing base 11 is connected to a gas tank 13 via a cassette pump 12, and stores the pyrolysis product gas purified by the cooling washing base 11.

一方、ガスタンク13は、上記熱分解炉1の加熱炉2a
に設けられた図示しないバーナに接続されて、貯留ガス
は加熱炉2aの燃料として使用されるとともに、上記燃
焼生成ガス発生機5の炭化水素系燃料としても使用され
る。
On the other hand, the gas tank 13 is connected to the heating furnace 2a of the pyrolysis furnace 1.
The stored gas is connected to a burner (not shown) provided in the heating furnace 2a, and is used as a fuel for the heating furnace 2a, and is also used as a hydrocarbon fuel for the combustion gas generator 5.

さらに上記加熱炉2aの排気口1aが上記燃焼生成ガス
供給口4に接続されると、燃焼排ガスも同様に、熱分解
室2内に燃焼生成ガスとして供給することができる。
Further, when the exhaust port 1a of the heating furnace 2a is connected to the combustion product gas supply port 4, the combustion exhaust gas can be similarly supplied into the pyrolysis chamber 2 as a combustion product gas.

なお、熱分解室2には残渣排出口1bが設けられて、被
処理材の熱分解の際に生じるカーボン等の残渣の排出を
行なうようになっている。
The thermal decomposition chamber 2 is provided with a residue discharge port 1b for discharging carbon and other residues generated during thermal decomposition of the material to be treated.

上記構成において、いま、被処理材の熱処理に際して、
まず、加熱炉2aから加熱室2内を約400〜800℃
に加熱し、つづいて、燃焼生成ガス発生機5から熱分解
室2に燃焼生成ガスを供給し活性雰囲気をパージして室
内を不活性雰囲気とした後に、被処理材装入口3から被
処理材を装入する。
In the above configuration, when heat treating the material to be treated,
First, the inside of the heating chamber 2 is heated from the heating furnace 2a to approximately 400 to 800°C.
Next, the combustion gas is supplied from the combustion gas generator 5 to the pyrolysis chamber 2 to purge the active atmosphere to make the chamber an inert atmosphere. Charge.

ここで、熱分解室2内の酸素濃度は、約1.5%以下と
しであるので、熱分解の際に、爆発等を誘起するような
ことはない。
Here, since the oxygen concentration in the pyrolysis chamber 2 is about 1.5% or less, there is no possibility of inducing an explosion or the like during the pyrolysis.

そして、被処理材は、熱分解室2内において熱分解され
て、その際に発生する塩化水素、水素、メタンなどを含
む熱分解生成ガスは、つぎに搬送用として上記燃焼生成
ガス発生機5から供給される燃焼生成ガスによってダク
ト6を介して凝縮基9に導かれる。
The material to be treated is thermally decomposed in the thermal decomposition chamber 2, and the thermal decomposition gas containing hydrogen chloride, hydrogen, methane, etc. generated at that time is transferred to the combustion gas generator 5 for transportation. The combustion product gas supplied from the duct 6 is guided to the condensing group 9 through the duct 6.

凝縮基9では、熱分解生成ガス中の塩化水素および約6
0℃以上の沸点の有機物は凝縮分離される。
In the condensing group 9, hydrogen chloride in the pyrolysis product gas and about 6
Organic substances with a boiling point of 0°C or higher are condensed and separated.

ここで、搬送用の燃焼生成ガスの主成分は、非凝縮性で
あり、水蒸気のように凝縮潜熱がないか、または少ない
ために、クーラ7の能力は小さくてよい。
Here, the main component of the combustion generated gas for conveyance is non-condensable and has no or little latent heat of condensation unlike water vapor, so the capacity of the cooler 7 may be small.

分離された塩化水素等は、凝縮基9から図示しない分離
器に導かれて塩酸と油分に重力分離法で分離され、さら
に、塩酸は図示しない活性炭吸着塔に導かれて、塩酸中
に混入した異臭成分としての有機物が吸着除去されて、
合成塩酸と同程度の濃度の約30〜35%の塩酸を回収
することができる。
The separated hydrogen chloride, etc. is led from the condensing group 9 to a separator (not shown) and separated into hydrochloric acid and oil by gravity separation, and the hydrochloric acid is further led to an activated carbon adsorption column (not shown) and mixed into the hydrochloric acid. Organic substances as off-flavor components are adsorbed and removed,
It is possible to recover hydrochloric acid with a concentration of about 30-35% comparable to that of synthetic hydrochloric acid.

方、凝縮基9で処理された熱分解生成ガスは、冷却洗滌
基11に導かれ、アルカリ洗滌されて不純物が除去され
た後、ポンプ12によりタンク13に貯留されて、上記
熱分解炉1の燃料または燃焼生成ガス発生機5の炭化水
素系燃料として供せられる。
On the other hand, the pyrolysis product gas treated in the condensing group 9 is led to the cooling and washing group 11, where it is washed with alkali to remove impurities, and then stored in the tank 13 by the pump 12, and then transferred to the pyrolysis furnace 1. It is provided as a fuel or a hydrocarbon fuel for the combustion gas generator 5.

上記の方法において、熱分解生成ガスの搬送用として燃
焼生成ガスを用いるようにしているが、熱分解生成ガス
量が多いとか、発熱量の高い生成ガスを得るためには常
時は使用しなくてもよい。
In the above method, combustion gas is used to transport the pyrolysis gas, but if the amount of pyrolysis gas is large or to obtain gas with a high calorific value, it may not be necessary to use it all the time. Good too.

上記の装置において、加熱炉2aの排気口1aを上記熱
分解室2の燃焼生成ガス供給口4に接続すれば、燃焼生
成ガス発生機5を設けなくてよく、設備費および維持費
を軽減することができる。
In the above apparatus, if the exhaust port 1a of the heating furnace 2a is connected to the combustion product gas supply port 4 of the pyrolysis chamber 2, the combustion product gas generator 5 is not required, reducing equipment costs and maintenance costs. be able to.

なお、上記実施例では、被処理材として塩化ビニール樹
脂を使用する場合について説明したがこの発明の技術思
想は熱可塑性樹脂廃棄物にも適用できることは言う迄も
ない。
In the above embodiments, the case where vinyl chloride resin is used as the material to be treated has been described, but it goes without saying that the technical idea of the present invention can also be applied to thermoplastic resin waste.

以上のように、この発明にかかる方法によれば、炭化水
素系燃料の燃焼生成ガスで熱分解室をあらかじめパージ
して不活性雰囲気とするようにしであるので、塩化ビニ
ール樹脂および/または熱可塑性樹脂廃棄物の被処理材
の熱分解の際に、爆発等を誘起することすく、シかも、
燃焼生成ガス中のCO2,H2Oと熱分解成分との反応
が起こり、十分に軽質化した熱分解生成ガスを得ること
ができる。
As described above, according to the method according to the present invention, the pyrolysis chamber is purged in advance with the gas produced by combustion of hydrocarbon fuel to create an inert atmosphere, so that vinyl chloride resin and/or thermoplastic When thermally decomposing the resin waste material to be treated, it is possible to cause an explosion, etc.
Reactions occur between CO2 and H2O in the combustion gas and the thermal decomposition components, and a sufficiently lightened thermal decomposition gas can be obtained.

また、上記軽質化した燃焼生成ガスは、非凝縮性である
ので、処理装置中の低温部分での結露現象を減じること
ができ、腐食を防止できるとともに、水蒸気のように凝
縮潜熱がないために、熱分解生成ガス凝縮基におけるク
ーラの能力を小さいものとすることができる。
In addition, since the lightened combustion gas is non-condensable, it can reduce condensation in low-temperature parts of the processing equipment, prevent corrosion, and has no latent heat of condensation unlike water vapor. , the capacity of the cooler in the pyrolysis product gas condensation group can be made small.

また、熱分解生成ガスの搬送用として燃焼生成ガスを使
用しでいるので、特に塩化ビニール樹脂については、回
収塩酸の濃度を合成塩酸と同じ程度の濃度の約30〜3
5%のものとすることができる。
In addition, since combustion gas is already used for conveying the pyrolysis gas, especially for vinyl chloride resin, the concentration of recovered hydrochloric acid is about 30 to 30%, which is the same concentration as synthetic hydrochloric acid.
It can be 5%.

また上記加熱炉の燃焼排ガスを上記熱分解室のパージ用
および熱分解生成ガスとして使用するようにすれば、燃
焼生成ガス発生機等が不要となり、設備費およびその維
持費を軽減することができる。
Furthermore, if the combustion exhaust gas of the heating furnace is used for purging the pyrolysis chamber and as the pyrolysis product gas, a combustion product gas generator, etc. is not required, and equipment costs and maintenance costs can be reduced. .

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

図はこの発明の方法を実現するための具体的な装置の配
置図である。 1・・・・・・間接型加熱炉、2・・・・・・熱分解室
、2a・・・・・・加熱炉、3・・・・・・被処理材装
入口、4・・・・・・燃焼生成ガス供給口、5・・・・
・・燃焼生成ガス発生機、9・・・・・・凝縮基、11
・・・・・・冷却洗滌基、13・・・・・ガスタンク。
The figure is a layout diagram of a specific device for implementing the method of the present invention. 1... Indirect heating furnace, 2... Pyrolysis chamber, 2a... Heating furnace, 3... Processing material charging port, 4... ...Combustion generated gas supply port, 5...
... Combustion product gas generator, 9... Condensation group, 11
...Cooling cleaning base, 13...Gas tank.

Claims (1)

【特許請求の範囲】 1 塩化ビニール樹脂および/または熱可塑性合成樹脂
廃棄物の被処理材を、間接加熱型熱分解炉により低酸素
雰囲気下で熱分解する熱処理方法において、熱処理に際
して、まず、炭化水素系燃料の燃焼生成ガスで上記熱分
解炉の熱分解室の高酸素雰囲気をパージしたのち、上記
被処理材を上記熱分解室に供給して熱処理するとともに
、上記熱分解室で発生した熱分解生成ガスを上記燃焼生
成ガスにより凝縮基に搬送するようにしたことを特徴と
する廃塩化ビニール樹脂等の熱処理方法。 2 上記燃焼生成ガス供給源として上記熱分解炉の燃焼
排ガスを用いるようにしたことを特徴とする特許請求の
範囲第1項記載の廃塩化ビニール樹脂等の熱処理方法。
[Scope of Claims] 1. In a heat treatment method in which a material to be treated of vinyl chloride resin and/or thermoplastic synthetic resin waste is pyrolyzed in a low-oxygen atmosphere in an indirect heating type pyrolysis furnace, during the heat treatment, carbonization is first performed. After purging the high oxygen atmosphere in the pyrolysis chamber of the pyrolysis furnace with the combustion generated gas of the hydrogen-based fuel, the material to be treated is supplied to the pyrolysis chamber for heat treatment, and the heat generated in the pyrolysis chamber is A method for heat treatment of waste vinyl chloride resin, etc., characterized in that the decomposition product gas is transported to a condensation group by the combustion product gas. 2. The method for heat treatment of waste vinyl chloride resin, etc. according to claim 1, characterized in that the combustion exhaust gas from the pyrolysis furnace is used as the combustion generated gas supply source.
JP54112218A 1979-08-31 1979-08-31 Heat treatment method for waste vinyl chloride resin, etc. Expired JPS5856556B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP54112218A JPS5856556B2 (en) 1979-08-31 1979-08-31 Heat treatment method for waste vinyl chloride resin, etc.

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP54112218A JPS5856556B2 (en) 1979-08-31 1979-08-31 Heat treatment method for waste vinyl chloride resin, etc.

Publications (2)

Publication Number Publication Date
JPS5637120A JPS5637120A (en) 1981-04-10
JPS5856556B2 true JPS5856556B2 (en) 1983-12-15

Family

ID=14581204

Family Applications (1)

Application Number Title Priority Date Filing Date
JP54112218A Expired JPS5856556B2 (en) 1979-08-31 1979-08-31 Heat treatment method for waste vinyl chloride resin, etc.

Country Status (1)

Country Link
JP (1) JPS5856556B2 (en)

Family Cites Families (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5753397B2 (en) * 1974-03-29 1982-11-12

Also Published As

Publication number Publication date
JPS5637120A (en) 1981-04-10

Similar Documents

Publication Publication Date Title
JPS61101232A (en) Method and plant for cleaning waste gas
EP0378482A1 (en) Regeneration process of a catalyst for the reforming or for the production of aromatic hydrocarbons
GB824517A (en) Improvements in or relating to the separation and recovery of vaporous and gaseous oxides from gases
US7214254B2 (en) Method of removing mercury from mercury contaminated materials
EP1670726A1 (en) Method and apparatus for treating organic matter
CA1075903A (en) Coal gasification apparatus
US4708641A (en) Waste removal system for problematic materials
JPH02504157A (en) Processes and equipment for converting combustible pollutants and waste into clean energy and usable products
JPH04501168A (en) Method and apparatus for recovering heat from solid substances separated in gasification or combustion treatment
JPS5856556B2 (en) Heat treatment method for waste vinyl chloride resin, etc.
JPS63159496A (en) Method and apparatus for treating raw gas
JP2005068435A (en) Method and plant for producing decontaminated synthesis gas from feedstock rich in organic matter with high efficiency
JPS5944351B2 (en) Treatment method for waste mainly consisting of organic matter
US7824631B2 (en) Nanocarbon generation equipment
JP2011241339A (en) Desalter and desalting method for chlorine-containing waste material
JP2000273473A (en) Coke oven treatment method
FR2511025A1 (en) IMPROVED PREHEATING PROCESS OF OILY SHIST BEFORE PYROLYSIS
JP4505178B2 (en) Process and plant for raw gas generated by pyrolysis of solid feed
EP1015143B1 (en) Treatment of contaminated soil
JPS5589385A (en) Treatment of wastes consisting mainly of organic substances and its device
WO2019186216A1 (en) Method and apparatus for processing biomass
JPH049571B2 (en)
JP2000234714A (en) Flue tube thermal cracking furnace and recycling facility for wasted rubber product
JP3519622B2 (en) Multi-stage treatment of charge
US4256539A (en) Method of generating gas and coke dust by rapid degasification and rapid vaporization