JPH0441588A - Increase of cog recovery - Google Patents
Increase of cog recoveryInfo
- Publication number
- JPH0441588A JPH0441588A JP14738990A JP14738990A JPH0441588A JP H0441588 A JPH0441588 A JP H0441588A JP 14738990 A JP14738990 A JP 14738990A JP 14738990 A JP14738990 A JP 14738990A JP H0441588 A JPH0441588 A JP H0441588A
- Authority
- JP
- Japan
- Prior art keywords
- gas
- coke oven
- coke
- coal
- polymer waste
- 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
Links
Landscapes
- Coke Industry (AREA)
Abstract
Description
【発明の詳細な説明】
産業上の利用分野
本発明は高分子(プラスチック)廃棄物をコークス炉に
導入して高分子廃棄物を還元雰囲気下で分解し、製造さ
れるコークスの品質を損なうことなくコークス炉発生ガ
ス(COGという)の回収量を増加する方法に関する。DETAILED DESCRIPTION OF THE INVENTION Field of Industrial Application The present invention introduces polymeric (plastic) waste into a coke oven and decomposes the polymeric waste in a reducing atmosphere, impairing the quality of the coke produced. The present invention relates to a method for increasing the amount of coke oven gas (COG) recovered.
従来の技術
プラスチックは現代社会において欠くべからざるもので
あり、プラスチックの成形性の良さが現代のニーズの多
様化にマツチして大量のプラスチックが生産・消費され
ている(ポリエチレン、ポリプロピレン、スチレン系、
塩ビ系だけで382年には約700万tを生産)。Conventional technology Plastics are indispensable in modern society, and the good moldability of plastics matches the diversification of modern needs, resulting in the production and consumption of large quantities of plastics (polyethylene, polypropylene, styrene,
Approximately 7 million tons of PVC products were produced in 2012).
一方、これらのプラスチックは同時に産業廃棄物として
排出されており、現状では埋め立てや一部焼却処理され
ているが、土中の細菌、バクテリアで分解されない点、
焼却した場合、排気ガスの処理、発熱量が大きく焼却炉
に悪影響を及ぼす等の点から問題となっている。On the other hand, these plastics are also discharged as industrial waste, and currently they are disposed of in landfills or partially incinerated, but they are not decomposed by bacteria in the soil.
When incinerated, it poses problems in terms of exhaust gas treatment and the large calorific value that adversely affects the incinerator.
その他の対策として、高分子廃棄物をコークス乾式消火
設置I (CDQという)の移動層内へ投入して加熱分
解して、加熱分解ガスを燃焼させ蒸気発生量の増加を図
るCDQガスのカロリー富化方法が特開昭63−273
Ell1号公報に開示されている。しかしながら、この
方法では得られたCDQ循環ガスのカロリーが低い(E
loo 〜800kcal/Nm3) 。As another measure, polymer waste is thermally decomposed by injecting it into the moving bed of coke dry fire extinguishing installation I (CDQ), and the pyrolyzed gas is combusted to increase the amount of steam generated. The method of conversion was published in JP-A-63-273
It is disclosed in Ell1 publication. However, with this method, the resulting CDQ circulating gas has a low calorie (E
~800kcal/Nm3).
また、古タイヤなどを微粉化して、これを石炭と共に乾
留する方法も特開昭48−28002号公報に開示され
ているが、この方法は古タイヤ中に含有する約32%の
固定炭素を新しい炭素原料として使用するものである。Additionally, JP-A-48-28002 discloses a method of pulverizing old tires and carbonizing them together with coal, but this method converts about 32% of the fixed carbon contained in old tires into new It is used as a carbon raw material.
発明が解決しようとする課題
本発明は、コークス炉の還元雰囲気下で高分子廃棄物を
分解し、製造されるコークスの品質を損なうことなく、
高カロリーガス(4400〜4800kcal/N層3
)として回収しようとするものである。Problems to be Solved by the Invention The present invention decomposes polymer waste in the reducing atmosphere of a coke oven, without impairing the quality of the coke produced.
High calorie gas (4400-4800kcal/N layer 3
).
ここで、コークス炉はプラスチックよりも高分子量であ
る石炭の熱分解e重合設備であり、2次処理設備も有し
ている点から、プラスチックの焼却処理の代替に成りう
る設備である。このため、コークス炉におけるプラスチ
ックの焼却(熱分解)処理を検討し、本発明を完成した
ものである。Here, the coke oven is an equipment for thermal decomposition and e-polymerization of coal, which has a higher molecular weight than plastics, and also has secondary treatment equipment, so it can be used as an alternative to the incineration treatment of plastics. For this reason, we investigated the incineration (pyrolysis) treatment of plastics in coke ovens and completed the present invention.
課題を解決するための手段
本発明は、装入炭に1mm月下の高分子廃棄物を最大2
0%まで配合・混合し、混合物をコークス炉へ装入し乾
留を行うことにより、還元分解ガスを得ることを特徴と
するCOG回収量増加方法、コークス炉で石炭乾留後、
2〜400m層Φの高分子廃棄物を大気遮断下で、発生
ガス吸引系を停止させることなく炭化室上部空間部に投
入し、還元分解ガスを得ることを特徴とするCOG回収
量増加方法、である。Means for Solving the Problems The present invention incorporates a maximum of 2 mm of polymer waste into charging coal.
A method for increasing COG recovery characterized by obtaining reduced decomposition gas by blending and mixing to 0%, charging the mixture into a coke oven and carbonizing it, and after carbonizing coal in a coke oven,
A method for increasing the amount of COG recovered, characterized in that polymeric waste with a layer Φ of 2 to 400 m is injected into the upper space of the carbonization chamber without stopping the generated gas suction system under the exclusion of the atmosphere to obtain reduced decomposition gas. It is.
作用
本発明で高分子廃棄物とは、特に限定するものではない
が、高カロリーを達成し、有害なガス(CQ、N系等)
の発生を避けるためには、炭化水素系の高分子が好まし
い9例えばポリエチレン。Function In the present invention, polymeric waste is not particularly limited to, but includes high-calorie and harmful gases (CQ, N-based, etc.).
In order to avoid the generation of carbon dioxide, hydrocarbon-based polymers are preferred.9 For example, polyethylene.
ポリプロピレン等のポリオレフィン系、スチレン系、ア
クリル系等が挙げられる。Examples include polyolefins such as polypropylene, styrenes, acrylics, and the like.
また、高分子廃棄物の形状としては、成形品が代表的で
ある。Moreover, molded products are a typical form of polymer waste.
コークス炉は還元性雰囲気であり、炉内は900〜11
00℃の高温であるため、高分子廃棄物は燃焼せず、分
解して水素、メタン、エタン、プロパン、エチレン、プ
ロピレン等の高カロリーな還元分解ガスとなる。A coke oven is a reducing atmosphere, and the temperature inside the oven is 900 to 11
Because the temperature is as high as 00°C, the polymer waste is not combusted but decomposed into high-calorie reduced decomposition gases such as hydrogen, methane, ethane, propane, ethylene, and propylene.
第1の発明におけるコークス炉への装入方法としては、
高分子廃棄物を粉砕し、その所定量を石炭と混合し、混
合物を通常の原料炭装入と同様にコークス炉へ装入し、
そのまま通常の操業に準じて乾留を行う。The method of charging into a coke oven in the first invention is as follows:
Pulverize polymer waste, mix a predetermined amount of it with coal, charge the mixture into a coke oven in the same way as normal coking coal charge,
Carry out carbonization according to normal operation.
この方法において、高分子廃棄物の粒径としては、81
図に示すように、粒度の大きいものを石炭と混合し乾留
すると、ガス化後の生成コークス中に形成される気孔が
大となる。従って、高炉要コークスとして要求されてい
る強度、例えば、DI : 83%以上、C9R:54
%以上を満足するために、11以下に粉砕処理するもの
である。In this method, the particle size of the polymeric waste is 81
As shown in the figure, when coke with a large particle size is mixed with coal and carbonized, the pores formed in the coke produced after gasification become large. Therefore, the strength required for blast furnace coke, for example, DI: 83% or more, C9R: 54
In order to satisfy % or more, it is pulverized to 11 or less.
また、高分子廃棄物の配合量としては、第2図及び第3
図に示すように、コークス強度、気孔率から20%以下
、好ましくは10%以下とすることが好ましい、配合量
の下限は特に限定されるものでないが、第2図のガス発
生量に示されているように、余り少量では回収量増加効
果に対して作業が煩雑となるので本発明の効果が少ない
、よって5%以上とすることが好ましい。In addition, as for the blended amount of polymer waste, see Figures 2 and 3.
As shown in the figure, it is preferably 20% or less, preferably 10% or less based on the coke strength and porosity.The lower limit of the blending amount is not particularly limited, but as shown in the gas generation amount in Figure 2. As shown in the figure, if the amount is too small, the work will be complicated and the effect of the present invention will be small compared to the effect of increasing the recovery amount.Therefore, it is preferable to set the amount to 5% or more.
第2の発明におけるコークス炉への装入方法としては、
石炭乾留後に炭化室内乾留された赤熱コークス上に高分
子廃棄物を大気遮断下で、発生ガス吸引系を停止させる
ことなく炭化室上部空間部に投入する。The method of charging into a coke oven in the second invention is as follows:
After carbonization of coal, polymeric waste is placed on top of the carbonized red hot coke in the carbonization chamber while blocking the atmosphere and without stopping the generated gas suction system.
この高分子廃棄物を大気遮断下で投入する手段としては
、第5図に示すように、コークス炉l上を走行する移動
車、例えば装入車等(図示せず)にホッパー2を設ける
。このホッパー2の下部には上下2段にシールバルブ4
.5を有するホッパー3を設ける。このホッパー3には
不活性ガス供給管6及びガス放出管7を設ける。9は筒
状シュートである。As a means for charging the polymer waste while blocking the atmosphere, as shown in FIG. 5, a hopper 2 is provided in a moving vehicle, such as a charging vehicle (not shown), which runs above the coke oven I. At the bottom of this hopper 2 there are seal valves 4 in two stages, upper and lower.
.. A hopper 3 having 5 is provided. This hopper 3 is provided with an inert gas supply pipe 6 and a gas discharge pipe 7. 9 is a cylindrical chute.
かかる装入装置によると、まず、コークス炉lの装炭口
10に筒状シュート9をセットしておき、次いで、バル
ブ4を開くとホッパー2内の所定の粒度の高分子廃棄物
粒子8はホッパー3内に導入される。所定量の受入れが
完了すると、バルブ4を閉じ、一方、不活性ガス供給管
6から不活性ガス、例えば、窒素ガスを導入しながらバ
ルブ5を開くと、高分子廃棄物粒子8は筒状シュート9
を介して炭化室内の乾留された赤熱コークス11上に大
気遮断下で装入できる。According to this charging device, first, the cylindrical chute 9 is set in the charging port 10 of the coke oven l, and then, when the valve 4 is opened, the polymer waste particles 8 of a predetermined particle size in the hopper 2 are charged. It is introduced into the hopper 3. When the reception of a predetermined amount is completed, the valve 4 is closed, and when the valve 5 is opened while introducing an inert gas, such as nitrogen gas, from the inert gas supply pipe 6, the polymer waste particles 8 are transferred to a cylindrical chute. 9
The coke can be charged onto the carbonized red hot coke 11 in the carbonization chamber under exclusion of the atmosphere.
尚、図示していないが、所定の粒度の高分子廃棄物粒子
を収納したホッパーを直接不活性ガスで加圧して圧送し
、大気遮断下で装入する手段であってもよい。Although not shown, a hopper containing polymeric waste particles of a predetermined particle size may be directly pressurized with an inert gas and fed under pressure, and then charged under exclusion of the atmosphere.
上記したように、高分子廃棄物の粒径は、装炭口10径
、使用する装入装置の仕様によって制限されるが、通常
、2〜200層曹Φの範囲のものが適用できる。As mentioned above, the particle size of the polymeric waste is limited by the diameter of the charging port 10 and the specifications of the charging device used, but it is generally applicable to a range of 2 to 200 layer carbon Φ.
また、投入時期は火落ち(乾留終了)からコークス押出
し迄の通常置き時間といわれる、コークス熟成時(約2
時間)に装入するのが好ましい。In addition, the timing of addition is during coke maturation (approximately 2
It is preferable to charge the battery at a certain time.
即ち、この時間内においては、第4図に示すように、通
常のコークス炉ガス発生量が少ないので、ガス発生量の
平線化にプラスとなる。また、置き時間中はコークス炉
からの放散熱が大きいが、放散している熱をガス分解熱
として利用できる。投入された高分子廃棄物は炭化室内
約1000℃の熱にて直ちに(約60程度度)でガス化
される。従って、高分子廃棄物の炭化室内投入はコーク
ス押出し前、遅くとも80分程度前迄に完了することが
望ましい、以下、実施例をもって具体的に説明する。That is, during this time, as shown in FIG. 4, the amount of gas generated in a normal coke oven is small, which is beneficial for flattening the amount of gas generated. Also, although a large amount of heat is radiated from the coke oven during the standing time, the radiated heat can be used as gas decomposition heat. The introduced polymeric waste is immediately gasified (about 60 degrees Celsius) at a temperature of about 1000 degrees Celsius in the carbonization chamber. Therefore, it is desirable that the introduction of the polymer waste into the carbonization chamber is completed at least 80 minutes before coke extrusion.Hereinafter, this will be explained in detail with reference to examples.
■平均粒径0.5層1のポリエチレンの破砕粒子を装入
炭に10wt%配合・混合した。この混合物を通常の装
入車を用いてコークス炉に装入し、乾留した。乾留ガス
は本来32ONm3/1−coalに対して375Mm
3/1−coalが得られた。また、得られたコークス
の品質はCSR:81.5%、Di : 84.5%で
あり、高炉用コークスとして遜色はない。(1) 10 wt % of crushed polyethylene particles with an average particle size of 0.5 layer 1 were added to the charged coal and mixed. This mixture was charged into a coke oven using a conventional charging car and carbonized. Carbonization gas is originally 375Mm for 32ONm3/1-coal
3/1-coal was obtained. Moreover, the quality of the obtained coke was CSR: 81.5% and Di: 84.5%, which is comparable to coke for blast furnaces.
■最大直径100m層のポリプロピレンを、コークス乾
留の完了した炭化室の上昇管(図示せず)に一番近い装
炭口より第5図に示す装入装置を用いて、100Kgを
大気遮断下で投入した。乾留ガスは本来23ONm3/
hrに対して29ONm3/hrの乾留ガスが得られた
。■ Using the charging device shown in Figure 5, 100 kg of polypropylene in a layer with a maximum diameter of 100 m is placed from the coal charging port closest to the riser pipe (not shown) of the carbonization chamber where coke carbonization has been completed, under exclusion of the atmosphere. I put it in. Carbonization gas is originally 23ONm3/
A carbonization gas of 29 ONm3/hr was obtained.
発明の効果
以上のように、本発明によると高分子廃棄物をコークス
炉に装入し、還元雰囲気下で分解し、製造されるコーク
スの品質を損なうことなくコークス炉ガスの回収量を#
I加出来るのでその産業上の効果は大きい。Effects of the Invention As described above, according to the present invention, polymer waste is charged into a coke oven, decomposed in a reducing atmosphere, and the amount of coke oven gas recovered can be increased without impairing the quality of the coke produced.
Since it can add I, its industrial effect is great.
第1図は高分子廃棄物粒径とコークス強度の関係を示す
説明図、第2図は高分子廃棄物粒の添加量とコークス強
度およびガス発生量の関係を示す説明図、第3図は高分
子廃棄物粒の添加量とコークス気孔率との関係を示す説
明図、第4図は乾留終了後経過時間とCOG発生量の関
係を示す説明図、第5図は高分子廃棄物を大気遮断下で
コークス炉に装入する装置に一例を示す説明図。Figure 1 is an explanatory diagram showing the relationship between polymer waste particle size and coke strength, Figure 2 is an explanatory diagram showing the relationship between the amount of polymer waste particles added, coke strength, and gas generation amount. An explanatory diagram showing the relationship between the amount of polymer waste grains added and coke porosity, Figure 4 is an explanatory diagram showing the relationship between the elapsed time after carbonization and the amount of COG generated, and Figure 5 is an explanatory diagram showing the relationship between the amount of polymer waste particles added and the coke porosity. An explanatory diagram showing an example of a device for charging a coke oven under shut-off.
Claims (1)
で配合・混合し、混合物をコークス炉へ装入し乾留を行
うことにより、還元分解ガスを得ることを特徴とするC
OG回収量増加方法。 2、コークス炉で石炭乾留後、2〜400mmΦの高分
子廃棄物を大気遮断下で、発生ガス吸引系を停止させる
ことなく炭化室上部空間部に投入し、還元分解ガスを得
ることを特徴とするCOG回収量増加方法。[Claims] 1. A method of obtaining reduced decomposition gas by blending and mixing up to 20% of polymeric waste of 1 mm or less in charging coal, charging the mixture into a coke oven, and performing carbonization. Characteristic C
How to increase the amount of OG recovered. 2. After coal carbonization in a coke oven, polymeric waste with a diameter of 2 to 400 mm is charged into the upper space of the carbonization chamber under atmospheric exclusion without stopping the generated gas suction system to obtain reduced decomposition gas. How to increase COG recovery amount.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP14738990A JPH0441588A (en) | 1990-06-07 | 1990-06-07 | Increase of cog recovery |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP14738990A JPH0441588A (en) | 1990-06-07 | 1990-06-07 | Increase of cog recovery |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| JPH0441588A true JPH0441588A (en) | 1992-02-12 |
Family
ID=15429158
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP14738990A Pending JPH0441588A (en) | 1990-06-07 | 1990-06-07 | Increase of cog recovery |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPH0441588A (en) |
Cited By (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| 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 |
| WO2026009787A1 (en) * | 2024-07-05 | 2026-01-08 | 日本製鉄株式会社 | Waste plastic processing method |
Citations (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS4834901A (en) * | 1971-09-08 | 1973-05-23 | ||
| JPS59120682A (en) * | 1982-12-22 | 1984-07-12 | ヴエ−・エス・ヴエ−・プラ−ヌングス−ゲゼルシヤフト・ミツト・ベシユレンクテル・ハフツング | Method and device for obtaining raw material from plastic waste |
| JPS624783A (en) * | 1985-06-29 | 1987-01-10 | Nippon Steel Chem Co Ltd | Coal carbonization method |
-
1990
- 1990-06-07 JP JP14738990A patent/JPH0441588A/en active Pending
Patent Citations (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS4834901A (en) * | 1971-09-08 | 1973-05-23 | ||
| JPS59120682A (en) * | 1982-12-22 | 1984-07-12 | ヴエ−・エス・ヴエ−・プラ−ヌングス−ゲゼルシヤフト・ミツト・ベシユレンクテル・ハフツング | Method and device for obtaining raw material from plastic waste |
| JPS624783A (en) * | 1985-06-29 | 1987-01-10 | Nippon Steel Chem Co Ltd | Coal carbonization method |
Cited By (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| 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 |
| WO2026009787A1 (en) * | 2024-07-05 | 2026-01-08 | 日本製鉄株式会社 | Waste plastic processing method |
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