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JPH0576890B2 - - Google Patents
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JPH0576890B2 - - Google Patents

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Publication number
JPH0576890B2
JPH0576890B2 JP23155587A JP23155587A JPH0576890B2 JP H0576890 B2 JPH0576890 B2 JP H0576890B2 JP 23155587 A JP23155587 A JP 23155587A JP 23155587 A JP23155587 A JP 23155587A JP H0576890 B2 JPH0576890 B2 JP H0576890B2
Authority
JP
Japan
Prior art keywords
hot air
volume reduction
volume
kiln
waste 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.)
Expired - Fee Related
Application number
JP23155587A
Other languages
Japanese (ja)
Other versions
JPS6472811A (en
Inventor
Makoto Uchida
Hitoshi Matsubara
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 JP23155587A priority Critical patent/JPS6472811A/en
Publication of JPS6472811A publication Critical patent/JPS6472811A/en
Publication of JPH0576890B2 publication Critical patent/JPH0576890B2/ja
Granted 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

  • Processing And Handling Of Plastics And Other Materials For Molding In General (AREA)
  • Separation, Recovery Or Treatment Of Waste Materials Containing Plastics (AREA)

Description

【発明の詳細な説明】 (産業上の利用分野) 本発明は、廃棄プラスチツク減容処理における
発火防止方法、特に処理雰囲気の酸素濃度を15容
積%以下に制限することにより、減容処理すべき
廃棄プラスチツクの発火、熱分解を防止する方法
に関する。
Detailed Description of the Invention (Field of Industrial Application) The present invention provides a method for preventing ignition during volume reduction treatment of waste plastics, in particular, by limiting the oxygen concentration in the treatment atmosphere to 15% by volume or less. Concerning methods for preventing ignition and thermal decomposition of waste plastics.

(従来の技術) 廃棄プラスチツクを減容処理する方法として、
例えば円筒形の頭部とロート状の下部から成る減
容窯に、外周部すなわちロート状下部の側壁に設
けた複数のノズルから熱風を窯内に導入し、窯内
に装入した廃棄プラスチツクを直接加熱して、軟
化溶融することにより減容する方法が公知である
が、この方法においては、廃棄プラスチツクの熱
分解による有害ガス成分や臭気成分の発生を防止
するため、あるいは、廃棄プラスチツクを燃焼さ
せることなく処理するため、廃棄プラスチツクの
熱分解温度より低い温度で軟化溶融することを基
本的な操作条件としており、従つて、加熱媒体と
して窯内に吹き込まれる熱風の温度は、プラスチ
ツクの熱分解開始温度より低い温度に設定され
る。
(Conventional technology) As a method for reducing the volume of waste plastic,
For example, in a volume reduction kiln consisting of a cylindrical head and a funnel-shaped lower part, hot air is introduced into the kiln from multiple nozzles provided on the outer periphery, that is, the side wall of the funnel-shaped lower part, and the waste plastics charged into the kiln are removed. A method of reducing the volume by direct heating to soften and melt is known, but in this method, it is necessary to prevent the generation of harmful gas components and odor components due to thermal decomposition of waste plastics, or to reduce the volume by burning waste plastics. In order to process the waste plastic without causing any decomposition, the basic operating conditions are to soften and melt the waste plastic at a temperature lower than the thermal decomposition temperature of the plastic. The temperature is set lower than the starting temperature.

通常、廃棄プラスチツクは、着火温度、発火温
度、分解温度など熱的特性の異なる各種のプラス
チツクが混在しているので、熱風の温度は、含ま
れる各種のプラスチツクの中のどのプラスチツク
の分解温度より低い温度に設定され、それは一般
的には150〜200℃の範囲である。
Usually, waste plastics are a mixture of various plastics with different thermal characteristics such as ignition temperature, ignition temperature, and decomposition temperature, so the temperature of the hot air is lower than the decomposition temperature of any of the various plastics included. The temperature is set, which is generally in the range of 150-200℃.

ところが、現実には、このような低い温度で加
熱しているにかかわらず、場合によつては、熱分
解が起こつて臭気成分が発生したり、更にそれが
進展して、発火燃焼するという事態に到ることが
ある。
However, in reality, despite heating at such low temperatures, in some cases thermal decomposition occurs and odor components are generated, and this progresses further, resulting in ignition and combustion. may reach.

臭気成分の発生あるいは発火燃焼は、安定した
処理操作を妨げるのは言うに及ばず、安全上及び
環境保全上の問題を惹起するので、それを防止す
る対策が求められている。
The generation of odor components or ignition and combustion not only impede stable treatment operations but also cause safety and environmental conservation problems, and therefore measures to prevent this are required.

(発明が解決しようとする問題点) 本発明は、このような廃棄プラスチツクの熱分
解あるいは発火燃焼を可及的に防止するための方
法を提供することを目的とする。
(Problems to be Solved by the Invention) An object of the present invention is to provide a method for preventing such thermal decomposition or ignition combustion of waste plastics as much as possible.

(問題点を解決するための手段) 本発明者らはかかる問題点の解決を図つて種々
検討を重ねた結果、次のような知見を得た。
(Means for Solving the Problems) As a result of various studies aimed at solving the problems, the present inventors have obtained the following knowledge.

まず、前述のような熱分解温度以下の低温雰囲
気にもかかわらず、ときとして、プラスチツクの
熱分解あるいは発火燃焼が起きるという事態は、
プラスチツクの酸化発熱に主な原因があると推定
される。通常、プラスチツクは大気温度付近で
は、ほとんど酸化しないか、酸化しても酸化速度
は極めて小さいが、減容窯内における如く、加熱
された状態では、酸化が著しく促進され、それに
伴つて酸化熱の発生があると考えられる。
First of all, despite the low temperature atmosphere below the thermal decomposition temperature as mentioned above, plastics sometimes undergo thermal decomposition or ignition combustion.
It is assumed that the main cause is the oxidation heat generated by the plastic. Normally, plastics are hardly oxidized at ambient temperature, or even if they are oxidized, the oxidation rate is extremely low. However, when heated, such as in a volume reduction kiln, oxidation is significantly accelerated, and the heat of oxidation is increased. It is thought that there is an outbreak.

そのようにしてプラスチツクの酸化が起こつた
とき、プラスチツク同士が十分分散していて、酸
化熱が放散される状態にあれば、プラスチツク自
身の温度上昇はほとんどないが、プラスチツクが
凝集密着した状態にあると、酸化熱が十分放散さ
れず凝集体の内部に蓄積され、温度が徐々に上昇
することになる。
When plastic oxidation occurs in this way, if the plastics are sufficiently dispersed and the oxidation heat is dissipated, the temperature of the plastic itself will hardly rise, but the plastic will remain in a cohesive state. In this case, the oxidation heat is not sufficiently dissipated and accumulates inside the aggregate, causing the temperature to gradually rise.

もしも、減容窯内にプラスチツクの一部が付着
あるいは固着するような現象によつて、凝集した
状態で長時間滞在することがあると、その内部で
上述の温度上昇がおこり、ついにはプラスチツク
が熱分解を始める温度以上に上昇し、場合によつ
ては、発火温度まで到達することが予想される。
If a part of the plastic sticks or sticks inside the volume reduction kiln and stays in an agglomerated state for a long time, the above-mentioned temperature rise will occur inside the kiln, and the plastic will eventually break down. It is expected that the temperature will rise above the temperature at which thermal decomposition begins, and in some cases even reach the ignition temperature.

そこで、本発明者らは、酸化熱の放散は困難で
あるため高温でも酸化が起こらない条件を実現す
ることに着目して検討したところ、減容窯に吹き
込まれる熱風の酸素濃度を下げるという簡便な手
段により、プラスチツクの酸化を防止あるいは減
速させ、プラスチツクの熱分解、燃焼を効果的に
防止できることを知り、本発明を完成した。
Therefore, since it is difficult to dissipate oxidation heat, the present inventors focused on creating conditions where oxidation does not occur even at high temperatures. The present invention was completed based on the knowledge that the oxidation of plastics can be prevented or slowed down, and the thermal decomposition and combustion of plastics can be effectively prevented.

なお、従来の方法では所定の温度の熱風を得る
方法として、灯油等の燃料をバーナで燃焼させて
高温ガスを生成し、それを空気で希釈して、所定
の温度に調整するという方法が用いられている
が、通常必要とされる熱風温度150〜200℃を得る
には、多量の空気で希釈しなければならず、希釈
後の熱風は酸素濃度が20%前後の高い値となるの
が必至で、プラスチツクの酸化が進行しやすい状
況にあつたのである。
In addition, in the conventional method, to obtain hot air at a predetermined temperature, a method is used in which fuel such as kerosene is burned in a burner to generate high-temperature gas, which is diluted with air and adjusted to a predetermined temperature. However, in order to obtain the normally required hot air temperature of 150 to 200°C, it must be diluted with a large amount of air, and the hot air after dilution has a high oxygen concentration of around 20%. This was inevitable, and the situation was such that plastic oxidation was likely to proceed.

ここに、本発明の要旨とするところは、例えば
円筒形の頭部とロート状の下部とから成る廃棄プ
ラスチツク減容窯に廃棄プラスチツクを投入する
とともに、その外周部に設けたノズルから熱風を
導入して廃棄プラスチツク減容処理を行うに際
し、前記減容窯の内部雰囲気中の酸素濃度を15容
積%以下に制限することを特徴とする、廃棄プラ
スチツク減容処理の発火防止方法である。
Here, the gist of the present invention is to introduce waste plastic into a waste plastic volume reduction kiln consisting of, for example, a cylindrical head and a funnel-shaped lower part, and introduce hot air from a nozzle provided on the outer periphery of the kiln. This is a method for preventing ignition in waste plastic volume reduction processing, which is characterized in that when performing waste plastic volume reduction processing, the oxygen concentration in the internal atmosphere of the volume reduction oven is limited to 15% by volume or less.

かくして、本発明によれば、減容窯の内部雰囲
気中の酸素濃度は15容積%以下に制限するが、か
かる条件は、減容窯に吹き込まれて廃棄プラスチ
ツクの加熱に供されたあとの温度の下がつた熱風
を希釈ガスとして熱風発生器へ再循環させること
により、好ましくは空気による希釈をなくし、窯
にノズルを通して吹き込まれる熱風の酸素濃度を
15容積%以下に下げることによつて実現されるの
であつて、これにより廃棄プラスチツクの酸化を
防止あるいは減速させ、万一窯内でプラスチツク
の凝集がおこつた場合でも、それが熱分解を始め
たり、発火燃焼したりすることを回避することが
出来る。
Thus, according to the present invention, the oxygen concentration in the internal atmosphere of the volume reduction kiln is limited to 15% by volume or less, but this condition is limited to the temperature at which the waste plastics are heated after being blown into the volume reduction kiln. Recirculating the sagging hot air as a diluent gas to the hot air generator preferably eliminates air dilution and reduces the oxygen concentration of the hot air blown through the nozzle into the kiln.
This is achieved by reducing the amount of plastic to 15% by volume or less, thereby preventing or slowing down the oxidation of waste plastics, and even if plastic agglomeration occurs in the kiln, it will not start thermal decomposition. It is possible to avoid ignition and combustion.

ここに、酸素濃度は、低ければ低い程、酸化防
止には良いが、余り低くすることは経済的に高価
となるため、一般には15〜5容積%程度が好まし
い。
The lower the oxygen concentration is, the better it is for preventing oxidation, but it is economically expensive to lower it too much, so it is generally preferred to be about 15 to 5% by volume.

したがつて、本発明はその別の態様によれば、
例えば円筒形の頭部とロート状の下部とから成る
廃棄プラスチツク減容窯に廃棄プラスチツクを投
入するとともに、その外周部に設けたノズルから
熱風を導入して廃棄プラスチツク減容処理を行う
に際し、廃棄プラスチツクの加熱に供された熱風
を減容窯上部から回収し熱風発生器を経て再使用
するとともに減容窯に供給する熱風の酸素濃度を
15容積%以下に制限することを特徴とする、廃棄
プラスチツク減容処理における発火防止方法であ
る。
Accordingly, according to another aspect of the invention,
For example, waste plastics are put into a waste plastics volume reduction kiln consisting of a cylindrical head and a funnel-shaped lower part, and hot air is introduced from a nozzle installed on the outer periphery of the kiln to reduce the volume of the waste plastics. The hot air used to heat the plastic is recovered from the upper part of the volume reduction kiln, passed through a hot air generator and reused, and the oxygen concentration of the hot air supplied to the volume reduction kiln is
This is a method for preventing ignition in waste plastic volume reduction processing, which is characterized by limiting the amount to 15% by volume or less.

さらに別の態様によれば、本発明は、廃棄プラ
スチツク減容窯に廃棄プラスチツクを投入すると
ともに、その外周部に設けたノズルから熱風を導
入して廃棄プラスチツク減容処理を行うに際し、
廃棄プラスチツクの加熱に供された熱風を減容窯
から回収するとともに、別の適宜燃焼炉から回収
した排ガスを前記の回収した熱風に混合して減容
窯に供給し、その酸素濃度を15容積%以下に制限
すること特徴とする、廃棄プラスチツク減容処理
における発火防止方法である。
According to yet another aspect, the present invention provides a method for reducing the volume of waste plastic by charging the waste plastic into a waste plastic volume reduction kiln and introducing hot air from a nozzle provided on the outer periphery of the kiln.
The hot air used to heat the waste plastic is recovered from the volume reduction kiln, and exhaust gas recovered from another appropriate combustion furnace is mixed with the recovered hot air and supplied to the volume reduction kiln, and its oxygen concentration is reduced to 15 volumes. This is a method for preventing ignition in waste plastic volume reduction processing, which is characterized by limiting the amount of ignition to below %.

(作用) 添付図面を参照しながらさらに本発明を詳述す
る。
(Operation) The present invention will be further described in detail with reference to the accompanying drawings.

本発明にかかる装置の構成を第1図に示す。 The configuration of the apparatus according to the present invention is shown in FIG.

図示例において円筒形の頭部2とロート状の下
部4とから成る炉本体6はその全体を外囲体8に
より取り囲まれ、炉本体6と外囲体8とで取り囲
まれる空間9は1種の風箱および保温体を構成し
ており、これを通して熱風が窯内に送られる。
In the illustrated example, a furnace body 6 consisting of a cylindrical head 2 and a funnel-shaped lower part 4 is entirely surrounded by an envelope 8, and there is only one type of space 9 surrounded by the furnace body 6 and the envelope 8. It consists of a wind box and a heat insulator, through which hot air is sent into the kiln.

従来の装置では減容処理装置つまり減容窯10
に導入され、廃棄プラスチツクの加熱に供された
あとの排ガスである熱風12は、従来そのまま外
気へ放出されていたが、本発明ではこの排ガス1
2を循環フアン14を通じて熱風発生器16へ再
循環させる。この熱風発生器16はバーナ18か
ら構成される。これにより、バーナ18での燃焼
用空気以外に、新鮮な空気を導入する必要がなく
なり、熱風の酸素濃度を下げることができる。通
常、バーナ18の空気比を2以下に抑え、減容窯
10の投入口20付近の圧力を若干揚圧にして、
空気が吸込まれるのを防止することによつて、循
環ガス中の酸素濃度を10%程度以下に抑えること
ができる。
In the conventional device, the volume reduction processing device, that is, the volume reduction kiln 10
Conventionally, the hot air 12, which is the exhaust gas introduced into the waste plastic and used to heat the waste plastic, is released directly to the outside air, but in the present invention, the exhaust gas 12 is
2 is recirculated to the hot air generator 16 through the circulation fan 14. This hot air generator 16 is composed of a burner 18 . Thereby, there is no need to introduce fresh air other than the combustion air in the burner 18, and the oxygen concentration of the hot air can be lowered. Normally, the air ratio of the burner 18 is suppressed to 2 or less, and the pressure near the input port 20 of the volume reduction kiln 10 is raised slightly.
By preventing air from being sucked in, the oxygen concentration in the circulating gas can be suppressed to about 10% or less.

このようにして調製された熱風22は投入口2
0を経て減容窯10の外周部24に設けた複数の
ノズル26から炉内に吹き込まれる。
The hot air 22 prepared in this way is supplied to the input port 2.
0, and is blown into the furnace from a plurality of nozzles 26 provided on the outer circumference 24 of the volume reduction furnace 10.

第2図は、別の適宜燃焼炉26(例:ボイラ、
ごみ焼却炉、etc.)から回収した排ガスである熱
風を使用する例を示す略式説明図である。かかる
排ガスが多量に入手できる場合には第1図に示す
バーナから成る熱風発生器を用いる必要はなく、
単に上記排ガスと減容窯から回収した熱風を配合
するだけでよい。一般に燃焼炉排ガスの酸素濃度
は2〜3容積%であり、したがつてこれに冷却を
目的に多少の空気を配合してもよい。図中、同一
部材は第1図と同一符号でもつて示す。
FIG. 2 shows another suitable combustion furnace 26 (e.g. boiler,
FIG. 2 is a schematic explanatory diagram showing an example of using hot air, which is exhaust gas collected from a garbage incinerator, etc. If such exhaust gas is available in large quantities, there is no need to use a hot air generator consisting of a burner as shown in FIG.
It is sufficient to simply mix the above exhaust gas and the hot air recovered from the volume reduction kiln. Generally, the oxygen concentration of the combustion furnace exhaust gas is 2 to 3% by volume, and therefore some air may be added to this for cooling purposes. In the drawings, the same members are designated by the same reference numerals as in FIG.

次に、本発明をその具体的実施例をもつて詳述
するが、これは単に本発明を例示するものであつ
て、それにのみ本発明が制限されるものではな
い。
Next, the present invention will be described in detail with reference to specific examples thereof, but these are merely illustrative of the present invention, and the present invention is not limited thereto.

実施例: 本発明は、排ガス再循環により、熱風の酸素濃
度を低下させて、プラスチツクの酸化による発
熱、温度上昇を抑制し、プラスチツクの熱分解、
発火燃焼を防止しようとするものであるが、その
効果を予備試験としての加熱テスト及び実地実験
としての大型試験機による大規模テストによつて
確認した。
Example: The present invention reduces the oxygen concentration of hot air through exhaust gas recirculation, suppresses heat generation and temperature rise due to oxidation of plastics, and reduces thermal decomposition of plastics.
This is intended to prevent ignition and combustion, and its effectiveness was confirmed through a preliminary heating test and a large-scale field test using a large testing machine.

(予備試験) サンプルによるテストは、都市ごみ系の廃棄プ
ラスチツク約50gを圧縮成型したサンプルを2個
用意し、1個は空気雰囲気で、他方は空気を遮断
した状態で、180℃の加熱器に装入し、そのとき
のサンプル中心部の温度推移を比較することによ
つて行つた。その結果、空気雰囲気で加熱したサ
ンプルは、急速に中心部の温度が上昇し、約20分
後には、300℃を越えたが、空気遮断状態で加熱
したサンプルは、温度上昇が緩慢で約30分後に
180℃に到達し、それから更に1時間保持したが、
温度が180℃を越えることがなかつた。
(Preliminary test) In the sample test, two samples were prepared by compression molding approximately 50 g of waste plastic from municipal waste, and one was placed in an air atmosphere and the other was placed in a heater at 180°C with the air shut off. This was done by comparing the temperature change at the center of the sample at that time. As a result, the temperature of the sample heated in an air atmosphere rapidly rose to exceed 300°C after about 20 minutes, but the temperature of the sample heated in an air-blocked state rose slowly, reaching about 300°C. in minutes
It reached 180℃ and then held for another hour, but
The temperature never exceeded 180°C.

この結果から、酸素濃度がプラスチツクの酸化
に大きな影響を及ぼし、酸素を断てば、酸化発熱
をほぼ完全に抑制できることが確認できた。
These results confirmed that oxygen concentration has a large effect on plastic oxidation, and that cutting off oxygen can almost completely suppress oxidation heat generation.

(実地試験) 次に、第1図に示す窯内容積2m3の減容窯大型
試験機で、窯からの排ガス(100℃)を再循環し
て熱風の酸素濃度を20%、15%(各180℃)にそ
れぞれ下げ、酸素濃度の低下が、プラスチツクの
酸化発熱の防止に果たす効果について調査した。
(Practical test) Next, using a large volume reduction kiln test machine with a kiln internal volume of 2 m 3 as shown in Figure 1, exhaust gas (100°C) from the kiln was recirculated to increase the oxygen concentration of the hot air to 20%, 15% ( The effect of lowering the oxygen concentration on preventing plastic oxidation heat generation was investigated.

試験方法は、吹き込み熱風の温度は180℃一定
とし、供試物である都市ごみ系の廃棄プラスチツ
ク50Kgを減容窯に投入して十分収縮溶融したのち
も、長時間放置し、そのときの臭気発生や発火燃
焼状態を観察した。
The test method was to keep the temperature of the blown hot air constant at 180℃, put 50 kg of waste plastic from municipal waste as a test material into a volume reduction kiln, and after sufficiently shrinking and melting, leave it for a long time to check the odor at that time. The generation and ignition combustion conditions were observed.

窯上部から回収した熱風の再循環をせず、熱風
の酸素濃度を20%に調整した場合は、投入後、約
15分で、発煙が著しくなり、そのあと直ちに発火
した。
If the hot air collected from the top of the kiln is not recirculated and the oxygen concentration of the hot air is adjusted to 20%, approximately
After 15 minutes, the smoke became noticeable and then the fire started immediately.

窯上部から回収した熱風排ガスを再循環して、
酸素濃度を15容積%に制限した場合は、投入後30
分間放置しても、発火は見られず分解温度まで上
がらないため過熱なく臭気の増加も認められなか
つた。
The hot air exhaust gas collected from the top of the kiln is recirculated,
If the oxygen concentration is limited to 15% by volume, 30
Even after being left for a minute, no ignition was observed and the temperature did not rise to the decomposition temperature, so there was no overheating and no increase in odor was observed.

(発明の効果) 以上詳述したように、本発明によれば、廃棄プ
ラスチツクの過熱部分がなく、従来問題であつた
減容処理時の発火、臭気発生が効果的に防止さ
れ、したがつて、人口密集地域に設けた小規模設
備でも、公害発生源にならずに安心して操業が継
続できる。
(Effects of the Invention) As detailed above, according to the present invention, there is no overheating part of waste plastic, and the conventional problems of ignition and odor generation during volume reduction processing are effectively prevented. Even small-scale facilities installed in densely populated areas can continue to operate with peace of mind without becoming a source of pollution.

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

第1図は、本発明にかかる方法を実施するため
の装置の概略図;および第2図は、同じく変更例
を示す概略図である。 10:減容窯、12:排ガス、14:循環フア
ン、16:熱風発生器、18:バーナ、20:ノ
ズル。
FIG. 1 is a schematic diagram of an apparatus for carrying out the method according to the invention; and FIG. 2 is a schematic diagram also showing a modification. 10: Volume reduction kiln, 12: Exhaust gas, 14: Circulation fan, 16: Hot air generator, 18: Burner, 20: Nozzle.

Claims (1)

【特許請求の範囲】 1 廃棄プラスチツク減容窯に廃棄プラスチツク
を投入するとともに、該減容窯の外周部に設けた
ノズルから熱風を導入して廃棄プラスチツクの減
容処理を行うに際し、前記減容窯の内部雰囲気中
の酸素濃度を15容積%以下に制限することを特徴
とする、廃棄プラスチツク減容処理の発火防止方
法。 2 廃棄プラスチツクの加熱に供された熱風を減
容窯から回収し熱風発生器を経て再使用するとと
もに該熱風発生器からの熱風の酸素濃度を15容積
%以下に制限することを特徴とする、特許請求の
範囲第1項記載の廃棄プラスチツク減容処理の発
火防止方法。 3 廃棄プラスチツクの加熱に供された熱風を減
容窯から回収するととに、別の適宜燃焼炉からの
排ガスを回収して、前記の回収した熱風に配合し
て再使用するとともに、その酸素濃度を15容積%
以下に制限することを特徴とする、特許請求の範
囲第1項記載の廃棄プラスチツク減容処理の発火
防止方法。
[Scope of Claims] 1. When waste plastic is charged into a waste plastic volume reduction kiln and hot air is introduced from a nozzle provided on the outer periphery of the volume reduction kiln to reduce the volume of the waste plastic, A method for preventing ignition during volume reduction treatment of waste plastics, which is characterized by limiting the oxygen concentration in the internal atmosphere of a kiln to 15% by volume or less. 2. The hot air used to heat the waste plastic is recovered from the volume reduction kiln, passed through a hot air generator, and reused, and the oxygen concentration of the hot air from the hot air generator is limited to 15% by volume or less. A method for preventing ignition during volume reduction treatment of waste plastics according to claim 1. 3. When the hot air used to heat the waste plastic is recovered from the volume reduction kiln, exhaust gas from another appropriate combustion furnace is recovered and mixed with the above-mentioned recovered hot air for reuse, and its oxygen concentration is 15% by volume
A method for preventing ignition in waste plastic volume reduction treatment according to claim 1, which is limited to the following.
JP23155587A 1987-09-16 1987-09-16 Prevention of ignition in volume decrease of waste plastics Granted JPS6472811A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP23155587A JPS6472811A (en) 1987-09-16 1987-09-16 Prevention of ignition in volume decrease of waste plastics

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP23155587A JPS6472811A (en) 1987-09-16 1987-09-16 Prevention of ignition in volume decrease of waste plastics

Publications (2)

Publication Number Publication Date
JPS6472811A JPS6472811A (en) 1989-03-17
JPH0576890B2 true JPH0576890B2 (en) 1993-10-25

Family

ID=16925337

Family Applications (1)

Application Number Title Priority Date Filing Date
JP23155587A Granted JPS6472811A (en) 1987-09-16 1987-09-16 Prevention of ignition in volume decrease of waste plastics

Country Status (1)

Country Link
JP (1) JPS6472811A (en)

Families Citing this family (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH0624727B2 (en) * 1989-07-18 1994-04-06 株式会社クラウド Deodorization melting method of thermoplastic waste plastic

Also Published As

Publication number Publication date
JPS6472811A (en) 1989-03-17

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