JPH08157834A - Treatment of waste plastic - Google Patents

Treatment of waste plastic

Info

Publication number
JPH08157834A
JPH08157834A JP6321170A JP32117094A JPH08157834A JP H08157834 A JPH08157834 A JP H08157834A JP 6321170 A JP6321170 A JP 6321170A JP 32117094 A JP32117094 A JP 32117094A JP H08157834 A JPH08157834 A JP H08157834A
Authority
JP
Japan
Prior art keywords
waste plastic
coke
coal
charging
furnace
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.)
Granted
Application number
JP6321170A
Other languages
Japanese (ja)
Other versions
JP2967329B2 (en
Inventor
Katsuhiko Shiraishi
勝彦 白石
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
Nippon Steel Corp
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
Family has litigation
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Application filed by Nippon Steel Corp filed Critical Nippon Steel Corp
Priority to JP6321170A priority Critical patent/JP2967329B2/en
Publication of JPH08157834A publication Critical patent/JPH08157834A/en
Application granted granted Critical
Publication of JP2967329B2 publication Critical patent/JP2967329B2/en
Anticipated expiration legal-status Critical
Expired - Lifetime legal-status Critical Current

Links

Abstract

PURPOSE: To provide a method for increasing tar, light oil and gas which are by-products having high value added and obtained from coke oven by treating waste plastic with the coke oven. CONSTITUTION: A waste plastic is blended into a blending coal in a coke furnace or the waste plastic is charged into a space part of furnace top just after coal is charged into the coke furnace or the waste plastic is fed through an introduction hole which communicates to the space part of the furnace top in carbonization of coal.

Description

【発明の詳細な説明】Detailed Description of the Invention

【0001】[0001]

【産業上の利用分野】本発明は既存のコークス炉を用い
る廃プラスチックの処理方法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 treating waste plastic using an existing coke oven.

【0002】[0002]

【従来の技術】既存コークス炉を用いる廃プラスチック
の処理方法としては、例えば特開昭48―34901号
公報ではコークス製造用装入炭に廃プラスチックを配合
しコークスを製造する方法が提案されている。
2. Description of the Related Art As a method for treating waste plastics using an existing coke oven, for example, Japanese Unexamined Patent Publication (Kokai) No. 48-34901 proposes a method for producing coke by blending the waste plastics with a charging coal for producing coke. .

【0003】[0003]

【発明が解決しようとする課題】コークス炉の副産物で
あるタール、軽油、ガスはコークスとともに、付加価値
の高い製品である。
Tar, gas oil and gas, which are by-products of a coke oven, are high value-added products together with coke.

【0004】廃プラスチックの処理方法としては、例え
ば特開昭48―34901号公報ではコークス製造用装
入炭に廃プラスチックを9〜23wt%配合しコークス
を製造する方法を提案している。
As a method for treating waste plastic, for example, Japanese Unexamined Patent Publication (Kokai) No. 48-34901 proposes a method for producing coke by blending 9 to 23 wt% of waste plastic into charging coal for producing coke.

【0005】廃プラスチックをコークス製造用装入炭に
配合した場合、目標コークス強度を確保するため廃プラ
スチック量に上限が存在する。目標コークス強度を確保
し、かつ多量の廃プラスチックをコークス炉で処理する
方法はない。
When the waste plastic is blended with the charging coal for the production of coke, there is an upper limit to the amount of the waste plastic in order to secure the target coke strength. There is no method to secure the target coke strength and process a large amount of waste plastic in the coke oven.

【0006】本発明は多量の廃プラスチックをコークス
炉で処理することにより、付加価値の高い、タール、軽
油、ガスを多く得る方法を提供することを目的としてい
る。
An object of the present invention is to provide a method for obtaining a large amount of tar, gas oil and gas with high added value by treating a large amount of waste plastic in a coke oven.

【0007】[0007]

【課題を解決するための手段】上記課題を解決するため
に本発明では、コークス製造用装入炭、または廃プラス
チックを0.1〜1.0wt%配合したコークス製造用
装入炭をコークス炉に装入後、装入口から前記装入炭の
上の炉頂空間に廃プラスチックを装入し、乾留中に廃プ
ラスチックを熱分解してタール、軽油、ガスとして回収
する事を特徴とする。
In order to solve the above problems, in the present invention, a charging coal for the production of coke or a charging coal for the production of coke containing 0.1 to 1.0 wt% of waste plastic is added to the coke oven. After the charging, the waste plastic is charged into the furnace top space above the charging coal from the charging port, and the waste plastic is thermally decomposed during the carbonization to be recovered as tar, light oil, and gas.

【0008】またコークス製造用装入炭、または廃プラ
スチックを0.1〜1.0wt%配合したコークス製造
用装入炭をコークス炉に装入後から乾留終了まで、コー
クス炉の炉頂空間部へ通じる供給装置より廃プラスチッ
クを供給し、乾留中に廃プラスチックを熱分解してター
ル、軽油、ガスとして回収する事を特徴とする廃プラス
チックの処理方法である。
Further, from the charging of the coke for the production of coke or the charging of the coke for the production of 0.1 to 1.0 wt% of waste plastic into the coke oven until the end of the carbonization, the top space of the coke oven It is a method of treating waste plastic, which comprises supplying waste plastic from a supply device leading to and then thermally decomposing the waste plastic during carbonization and recovering it as tar, light oil, and gas.

【0009】上記廃プラスチックは、ポリエチレン、ポ
リエチレンテレフタレートなどのプラスチックの廃棄物
である。
The waste plastics are wastes of plastics such as polyethylene and polyethylene terephthalate.

【0010】ポリ塩化ビニールなど塩素を含むプラスチ
ックが入っていると加熱した際に腐食性のある塩化水素
が生成するので塩素を含有しないプラスチックが好まし
い。
When a plastic containing chlorine such as polyvinyl chloride is contained, corrosive hydrogen chloride is generated when heated, so a plastic containing no chlorine is preferable.

【0011】[0011]

【作用】廃プラスチックの乾留生成物の歩留を石炭乾留
生成物歩留測定装置で測定した。第1表に示すようにタ
ール、ガスがかなり多い。また石炭から得られる軽油の
歩留は1%程度であるが、廃プラスチックから得られる
軽油の歩留は5wt%と比較的多い。
[Operation] The yield of the dry distillation product of waste plastic was measured by a coal dry distillation product retention measuring device. As shown in Table 1, there is much tar and gas. The yield of diesel fuel obtained from coal is about 1%, but the yield of diesel fuel obtained from waste plastic is relatively high at 5 wt%.

【0012】一方廃プラスチックをコークス製造用装入
炭に配合した時のコークス強度と廃プラスチック配合率
の関係を検討した結果、図1に示すように廃ポリエチレ
ンを1.0wt%まで配合してもコークス強度は低下し
ないが1.0wt%超配合するとコークス強度が低下す
ることが判明した。
On the other hand, as a result of studying the relationship between the coke strength when the waste plastic was blended with the charging coal for the production of coke and the blending ratio of the waste plastic, even when the waste polyethylene was blended up to 1.0 wt% as shown in FIG. It was found that the coke strength does not decrease, but the coke strength decreases when the content exceeds 1.0 wt%.

【0013】廃プラスチックの配合率が0.1wt%の
場合は、殆ど効果がない事から廃プラスチックの配合率
の下限は0.1wt%とした。このことからコークス製
造用装入炭への廃プラスチックの配合率は0.1〜1.
0wt%とした。
When the blending ratio of waste plastic is 0.1 wt%, there is almost no effect, so the lower limit of the blending ratio of waste plastic is set to 0.1 wt%. Therefore, the blending ratio of waste plastic to the charging coal for coke production is 0.1 to 1.
It was set to 0 wt%.

【0014】上記のようにコークス強度下限値を維持す
るためコークス製造用装入炭への配合率の上限は1.0
wt%である。
As described above, in order to maintain the lower limit of coke strength, the upper limit of the compounding ratio in the charging coal for coke production is 1.0.
wt%.

【0015】本発明者は炉頂空間部で乾留中に廃プラス
チックを熱分解すれば、より多くの廃プラスチックを処
理してより多くのタール、軽油、ガスを得ることができ
ると考えた。
The inventor of the present invention has considered that if the waste plastic is pyrolyzed during the carbonization in the furnace top space, more waste plastic can be processed and more tar, light oil and gas can be obtained.

【0016】例えば、炉幅430mm、炉高6.5m、
炉長15.7mの炭化室を有するコークス炉に装入炭を
装入した時、装入炭上に高さ0.35mの空間部があ
る。これが炉頂空間部である。
For example, the furnace width is 430 mm, the furnace height is 6.5 m,
When the charging coal is charged into a coke oven having a carbonization chamber having a furnace length of 15.7 m, there is a space of 0.35 m in height above the charging coal. This is the furnace top space.

【0017】乾留中の炉頂空間部の温度は700〜85
0℃であり、廃プラスチックを熱分解するために充分な
温度がある。
The temperature of the furnace top space during carbonization is 700-85.
It is 0 ° C., which is a sufficient temperature for the thermal decomposition of waste plastic.

【0018】炉頂空間部へ廃プラスチックを装入する方
法としては、装入炭、または廃プラスチックを0.1〜
1.0wt%配合した装入炭を装入後、図2に示す供給
装置を用いて炉頂空間部に廃プラスチックを装入する。
The method of charging the waste plastic into the furnace top space is as follows.
After charging the charged coal containing 1.0 wt%, waste plastic is charged into the furnace top space using the supply device shown in FIG.

【0019】炉頂空間部に1tの廃プラスチックを装入
すると、廃プラスチックを5wt%程度配合した時と同
量の廃プラスチックの処理が可能になる。
When 1 ton of waste plastic is charged in the furnace top space, the same amount of waste plastic as when the waste plastic is blended at about 5 wt% can be treated.

【0020】また装入炭、または廃プラスチックを0.
1〜1.0wt%配合した装入炭を装入後、乾留終了時
点まで、図2に示す供給装置を用いて炉頂空間部に廃プ
ラスチックを供給すると、更に多くの廃プラスチックを
処理する事が可能になる。
In addition, the charged coal or the waste plastics can be treated with 0.
After charging the charged coal mixed with 1 to 1.0 wt% and supplying the waste plastic to the furnace top space part using the supply device shown in FIG. 2 until the end of the dry distillation, more waste plastic is treated. Will be possible.

【0021】炉頂空間部に1t/hrの供給速度で19
時間廃プラスチックを供給する場合、廃プラスチックを
79wt%配合した場合と同量の廃プラスチックの処理
が可能になる。
19 hours at a feed rate of 1 t / hr into the space at the top of the furnace.
When supplying waste plastic for a time, the same amount of waste plastic can be treated as when 79 wt% of waste plastic is blended.

【0022】[0022]

【実施例1】炉幅430mm、炉高6.5m、炉長1
5.7mのコークス炉に水分5%、無水基準の揮発分が
27%の装入炭を24トン装入し、炉温1220℃の条
件で操業している時、石炭装入後、装入炭上の炉頂空間
部に廃ポリエチレンを1トン装入し乾留した。この時の
乾留生成物の収量を第2表に示す。石炭のみを乾留した
場合に比べ、タール、軽油、およびガスを多く回収でき
た。
Example 1 Furnace width 430 mm, furnace height 6.5 m, furnace length 1
In a 5.7 m coke oven, 24 tons of 5% water and 27% of volatile matter on a dry basis were charged, and when operating at a furnace temperature of 1220 ° C, after charging coal, charging 1 ton of waste polyethylene was charged into the space on the top of the charcoal and dried. The yield of dry-distilled products at this time is shown in Table 2. More tar, light oil, and gas could be recovered than when only coal was carbonized.

【0023】[0023]

【実施例2】炉幅480mm、炉高6.5m、炉長1
5.7mのコークス炉に水分5%、無水基準の揮発分が
27%の装入炭を24トン装入し、1220℃で操業し
ている時、装入炭上の炉頂空間部に廃ポリエチレンを石
炭装入後より1t/hrの供給速度で19時間供給し
た。この時の乾留生成物の収量を第3表に示す。石炭の
みを乾留した場合に比べタール、軽油、およびガスを多
く回収できた。
[Example 2] Furnace width 480 mm, furnace height 6.5 m, furnace length 1
A 5.7 m coke oven was charged with 24 tons of 5% moisture and 27% volatile matter on a dry basis, and when operating at 1220 ° C, wasted in the furnace top space above the charging coal. Polyethylene was fed at a feed rate of 1 t / hr for 19 hours after charging the coal. The yield of the dry-distilled product at this time is shown in Table 3. More tar, light oil, and gas could be recovered than when only coal was carbonized.

【0024】[0024]

【表1】 [Table 1]

【0025】[0025]

【表2】 [Table 2]

【0026】[0026]

【表3】 [Table 3]

【0027】[0027]

【発明の効果】本発明の廃プラスチックの処理方法によ
り廃プラスチックを処理し、かつ付加価値の高いター
ル、軽油、ガスを回収できるため、工業的価値が大き
い。
Industrial Applicability Since the waste plastic treatment method of the present invention can treat waste plastic and recover tar, gas oil, and gas with high added value, it has great industrial value.

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

【図1】コークス強度と廃プラスチック配合率の関係を
示す図である。
FIG. 1 is a diagram showing the relationship between coke strength and waste plastic compounding ratio.

【図2】廃プラスチックを供給する装置を示す図であ
る。
FIG. 2 is a diagram showing an apparatus for supplying waste plastic.

【符号の説明】[Explanation of symbols]

1 上昇管 2 ドライメーン 3 炉頂空間部 4 装入炭(またはコークス) 5 バルブ 6 中継ホッパー 7 供給ホッパー 1 Rise pipe 2 Dry main 3 Top space 4 Charging (or coke) 5 Valve 6 Relay hopper 7 Supply hopper

───────────────────────────────────────────────────── フロントページの続き (51)Int.Cl.6 識別記号 庁内整理番号 FI 技術表示箇所 C10B 57/06 ─────────────────────────────────────────────────── ─── Continuation of the front page (51) Int.Cl. 6 Identification code Internal reference number FI technical display location C10B 57/06

Claims (2)

【特許請求の範囲】[Claims] 【請求項1】 コークス製造用装入炭、または廃プラス
チックを0.1〜1.0wt%配合したコークス製造用
装入炭をコークス炉に装入後、装入口から前記装入炭の
上の炉頂空間部に、廃プラスチックを装入し、乾留中に
廃プラスチックを熱分解してタール、軽油、ガスとして
回収する事を特徴とする廃プラスチックの処理方法。
1. A charging coal for producing coke, or a charging coal for producing coke containing 0.1 to 1.0 wt% of waste plastic is charged into a coke oven, and then above the charging coal from an inlet. A method for treating waste plastic, which comprises charging waste plastic into the furnace top space and thermally decomposing the waste plastic during carbonization to recover it as tar, light oil, or gas.
【請求項2】 コークス製造用装入炭、または廃プラス
チックを0.1〜1.0wt%配合したコークス製造用
装入炭をコークス炉に装入後から乾留終了まで、コーク
ス炉の炉頂空間部へ通じる供給装置より廃プラスチック
を供給し、乾留中に廃プラスチックを熱分解してター
ル、軽油、ガスとして回収する事を特徴とする廃プラス
チックの処理方法。
2. A coke oven top space from after the coke producing charge coal or the coke producing charge coal containing 0.1 to 1.0 wt% of waste plastic is charged into the coke oven until the end of the carbonization. A method for treating waste plastic, characterized in that waste plastic is supplied from a supply device leading to the section and is thermally decomposed during carbonization to be recovered as tar, light oil, and gas.
JP6321170A 1994-12-01 1994-12-01 Waste plastic treatment method Expired - Lifetime JP2967329B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP6321170A JP2967329B2 (en) 1994-12-01 1994-12-01 Waste plastic treatment method

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP6321170A JP2967329B2 (en) 1994-12-01 1994-12-01 Waste plastic treatment method

Publications (2)

Publication Number Publication Date
JPH08157834A true JPH08157834A (en) 1996-06-18
JP2967329B2 JP2967329B2 (en) 1999-10-25

Family

ID=18129582

Family Applications (1)

Application Number Title Priority Date Filing Date
JP6321170A Expired - Lifetime JP2967329B2 (en) 1994-12-01 1994-12-01 Waste plastic treatment method

Country Status (1)

Country Link
JP (1) JP2967329B2 (en)

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1069680C (en) * 1998-01-23 2001-08-15 中国科学院山西煤炭化学研究所 Tar-increasing and water-reducing method during coal cracking and coking
US6329496B1 (en) 1998-07-29 2001-12-11 Nippon Steel Corporation Method for processing chlorine-containing organic compounds
US6436168B1 (en) 1998-08-28 2002-08-20 Nippon Steel Corporation Treatment process for resins or organic compounds, or waste plastics containing them
JP2008115395A (en) * 1998-07-29 2008-05-22 Nippon Steel Corp Method for producing tar and/or gas oil while carrying out coking of coal in parallel with waste plastic treatment
US7695669B2 (en) 2003-10-21 2010-04-13 Nippon Steel Corporation Method of reutilization and method of shaping of waste plastic

Cited By (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1069680C (en) * 1998-01-23 2001-08-15 中国科学院山西煤炭化学研究所 Tar-increasing and water-reducing method during coal cracking and coking
US6329496B1 (en) 1998-07-29 2001-12-11 Nippon Steel Corporation Method for processing chlorine-containing organic compounds
JP2008115395A (en) * 1998-07-29 2008-05-22 Nippon Steel Corp Method for producing tar and/or gas oil while carrying out coking of coal in parallel with waste plastic treatment
JP4486672B2 (en) * 1998-07-29 2010-06-23 新日本製鐵株式会社 Method for producing tar and / or light oil while coking coal and treating waste plastics in parallel
US6436168B1 (en) 1998-08-28 2002-08-20 Nippon Steel Corporation Treatment process for resins or organic compounds, or waste plastics containing them
US7695669B2 (en) 2003-10-21 2010-04-13 Nippon Steel Corporation Method of reutilization and method of shaping of waste plastic

Also Published As

Publication number Publication date
JP2967329B2 (en) 1999-10-25

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