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JP3845773B2 - Waste rubber carbonization method and apparatus - Google Patents
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JP3845773B2 - Waste rubber carbonization method and apparatus - Google Patents

Waste rubber carbonization method and apparatus Download PDF

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Publication number
JP3845773B2
JP3845773B2 JP24194297A JP24194297A JP3845773B2 JP 3845773 B2 JP3845773 B2 JP 3845773B2 JP 24194297 A JP24194297 A JP 24194297A JP 24194297 A JP24194297 A JP 24194297A JP 3845773 B2 JP3845773 B2 JP 3845773B2
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gas
dry distillation
combustion
carbonization
heat
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JPH10310775A (en
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暁 横田
健也 梶谷
武史 網田
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Nishikawa Rubber Co Ltd
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Nishikawa Rubber Co Ltd
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    • 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
    • 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

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  • Production Of Liquid Hydrocarbon Mixture For Refining Petroleum (AREA)
  • Processing Of Solid Wastes (AREA)
  • Manufacture Of Porous Articles, And Recovery And Treatment Of Waste Products (AREA)
  • Separation, Recovery Or Treatment Of Waste Materials Containing Plastics (AREA)
  • Coke Industry (AREA)

Description

【0001】
【発明の属する技術分野】
本発明は屑ゴムの炭化方法及びその装置に関するものである。
【0002】
【従来の技術】
ゴム製品を製造する工場では、多量の屑ゴムが発生する。その屑ゴムは、そのままで再利用困難であるため、通常焼却炉で焼却している。しかしながら屑ゴムを焼却すると、黒煙・有害成分・悪臭成分を放出し、周囲の環境を汚染すると言う問題点がある。また、焼却によって生じた焼却灰は再利用困難であって、地中に埋める以外有効な手段がなく、その負担も少なくない。
【0003】
【発明が解決しようとする課題】
解決しようとする課題は、上記従来の屑ゴムを焼却する方法は、黒煙・有害成分・悪臭成分を放出し、周囲の環境を汚染する他、焼却によって生じた焼却灰は、再利用困難であって、地中に埋める以外有効な手段がないことであって、本発明は上記問題を解決した、屑ゴムの炭化方法及びその装置を提供するものである。
【0004】
【問題を解決するための手段】
第1の発明の屑ゴムの炭化方法は、図1及び図2に示す如く、屑ゴムDを間接加熱により乾留し、炭化物C及び乾留ガスG1を得る乾留工程1、乾留工程1の乾留ガスG1の少なくとも一部を燃焼し、前記乾留工程1に必要な熱を発生させる第1燃焼工程2、その第1燃焼工程2の排ガスG2中の未燃分・有害成分・悪臭成分を燃焼させる第2燃焼工程3、及びその第2燃焼工程3の排ガスG3の保有する熱を利用して、水蒸気Sを発生させる水蒸気発生工程4より構成されており、図4及び図5に示す如く、第1の発明の第1燃焼工程2において、乾留工程1の乾留ガスG1の少なくとも 一部を燃焼する過程で、スチームSTを添加し、乾留ガスG1との間に水性ガス反応を生起させることを特徴とするものである。
【0005】
第2の発明の屑ゴムの炭化装置は、図2及び図3に示す如く、屑ゴムDを回転円筒21の一端から供給し、他端から排出させる間に、屑ゴムDを間接加熱により乾留し、炭化物C及び乾留ガスG1を得ると共に、その乾留ガスG1の少なくとも一部を燃焼させることによって生じた熱を回転円筒21の壁面を介して屑ゴムDに伝達させるよう構成した乾留炉20、その乾留炉20の排ガスG2の未燃分・有害成分・悪臭成分を燃焼させる燃焼炉30、及びその燃焼炉30の排ガスG3の保有する熱を利用して、水蒸気Sを発生させる廃熱回収ボイラ40を備えており、図3に示す如く、第2の発明の乾留炉20が、屑ゴムDを転動させるよう回転すると共に、発生した乾留ガスG1を排出させる複数のガス排出孔Hを有する回転円筒21と、その回転円筒21を包囲する乾留ガス燃焼室25と、を備え、前記回転円筒21からガス排出孔Hを経て導入された乾留ガスG1の少なくとも一部を燃焼させることによって生じた熱を回転円筒21の壁面を介して屑ゴムDに伝達するよう構成した炭化装置において、当該炭化装置は、図5に示す如く、第1の発明の乾留ガス燃焼室25において、乾留ガスG1との間に水性ガス反応を生起させるよう、乾留ガス燃焼室25の中にスチームSTを吹き込むスチームノズルSNを設けたことを特徴とするものである。
【0009】
第1又は第2の発明によれば、屑ゴムDから保温材その他に有効利用可能な炭化物Cが得られる。その炭化物Cによって、硫黄、塩素のかなりの割合と殆ど全てのカーボンブラック及び灰分が固定されると共に、排ガスG3から黒煙・有害成分・悪臭成分が燃焼除去されるため、灰分及び排ガスによる環境汚染の問題も一挙に解消される。さらに屑ゴムDの乾留の熱源の大半が、その乾留時に発生する乾留ガスG1の燃焼熱によって供給されると共に、工場の各種熱源又は動力源として利用可能な水蒸気が得られる等、屑ゴムDが熱源として有効活用される。
【0010】
記作用効果に加えて、屑ゴムDの乾留時に発生する乾留ガスG1が何等の処理精製を経ずにそのまま燃焼され、その熱が屑ゴムDの乾留に利用されるため、処理精製に伴う熱損失が低減されると共に、装置が著しく簡略される。
【0011】
さらに、第1燃焼工程2又は乾留ガス燃焼室25において、乾留ガスG1との間に水性ガス反応が生起するため、黒煙の発生が抑制され、第2燃焼工程3又は燃焼炉30における未燃分・有害成分・悪臭成分の燃焼に当たっての装置及び運転条件が著しく緩和される。
【0012】
【発明の実施の形態】
本発明の実施の形態例について、図1乃至図5により説明すると、乾留工程1において、後述するように、補助燃料F1及び乾留ガスG1の少なくとも一部の燃焼熱により、屑ゴムDが間接加熱され、乾留されて、炭化物Cが得られる。乾留に当たっては、灰分及び硫黄分・塩素分のかなりの割合が乾留ガスG1に同伴されず、炭化物Cに固定される。
【0013】
第1燃焼工程2においては、上述するように、乾留工程1から導かれた乾留ガスG1の少なくとも一部と補助燃料F1とが燃焼する。なお、図4に示すように、乾留工程1の乾留ガスG1の少なくとも一部が燃焼される過程で、乾留ガスG1との間に水性ガス反応が生起するよう、スチームSTが添加されることは、後述するように極めて好ましいことである。
【0014】
第2燃焼工程3においては、乾留工程2で使われずに導かれた乾留ガスG1の残り及び第1燃焼工程2の排ガスG2中の未燃分・有害成分・悪臭成分が燃焼する。水蒸気発生工程4においては、第2燃焼工程3の高温の排ガスG3の保有する熱が回収され、工場の各種熱源又は動力源として利用可能な水蒸気Sが発生する。なお、5はその水蒸気発生工程4の排ガスG4に含まれるダストを捕集し、除去する集塵工程である。
【0015】
装置について図2、図3及び図5により説明すると、屑ゴムDを間接加熱により乾留し、炭化物Cを得るための回転円筒21を備えた乾留炉20、その乾留炉20の排ガスG2の未燃分・有害成分・悪臭成分及び乾留炉20で使われずに直接導かれた乾留ガスG1の残りを燃焼させる燃焼炉30、及びその燃焼炉30の排ガスG3の保有する熱を利用して、水蒸気Sを発生する廃熱回収ボイラ40の他に、屑ゴムDを20ミリ以下に破砕する破砕機10、乾留炉20から排出される炭化物Cを間接水冷する回転式クーラ50及び炭化物Cに含まれる鉄分を除去する磁選機60を備えている。
【0016】
また、乾留炉20は、図3及び図5に示すように、一端から供給された屑ゴムDを転動させて、他端から排出する前記回転円簡21の入口・出口に屑ゴムDを供給する供給室22及び炭化物C並びに乾留ガスG1を排出する排出室23が設けられている。さらに前記回転円筒21は乾留ガス燃焼室25によって囲まれており、しかも側面には乾留ガス燃焼室25に通じる多数のガス排出孔Hが穿けられている。
【0017】
なお、乾留ガス燃焼室25には、当然のことで図示されていないが、燃焼に必要な空気導入のための口を備えている。また図5に示すように、乾留ガスG1との間に水性ガス反応が生起するよう、乾留ガス燃焼室25の中にスチームSTが吹き込まれるスチームノズルSNが設けられることは、後述するように極めて好ましいことである。
【0018】
さらに、ガス排出孔Hから回転円筒21の固形分が燃焼室25に落下しないよう、図ではガス排出孔Hから回転円筒21内へ向かって直筒状のものが突設されているが、その他L字状に折り曲げられた筒状のもの等、乾留ガスG1が通過可能であり、且つ固形分が燃焼室25に落下しないよう構成されているものであれば、これに限定されるものではない。
【0019】
しかも、乾留ガス燃焼室25の圧力は、回転円筒21内で発生した乾留ガスG1の少なくとも一部が流出可能に、回転円筒21内の圧力よりも僅かに低く保持されており、その中では補助燃料F1及び乾留ガスG1の少なくとも一部が燃焼し、その燃焼熱が回転円筒21の壁面を介して屑ゴムDに伝達されるように構成されている。その他、70は廃熱回収ボイラ40の排ガスG4に含まれるダストを捕集し、除去するバッグフィルター等の集塵装置、80は排ガスG4を大気中に放出する煙突である。
【0020】
【実施例】以下に示すエチレンープロピレンージエンゴム(EPDM)、オイル、カーボンブラックを主成分とする屑ゴムを炭化した実施例について説明する。
【0021】
屑ゴムの工業分析結果

揮発分 59.3
全硫黄 1.17
塩素分 0.05
灰分 9.93
カーボンブラック 34.3
総発熱量 8,680Kcal/kg
【0022】
破砕機10により20ミリ以下に破砕され、運ばれた屑ゴムDは乾留炉20の回転円筒21の一端へ送られる。その回転円筒21の側面を囲む燃焼室25においては、後述するように補助燃料F1及び乾留ガスG1の少なくとも一部が燃焼される。その燃焼熱によって、回転円筒21内を転動する屑ゴムDが間接的に加熱され、乾留されて、炭化物Cとなって他端から排出される。
【0023】
炭化物Cの工業分析結果は以下の通りである。

収率 45
固定炭素 67.34
揮発分 10.66
灰分 22.0
P 0.005
S 1.89
C1 0.21
【0024】
回転円筒21内の圧力は、その側面に穿けられ複数のガス排出孔Hから、燃焼室25の燃焼ガスG2が回転円筒21内に入らないよう、また乾留ガスG1の少なくとも一部が燃焼室25へ流出し、燃焼可能に、燃焼室25の圧力よりも僅かに高く制御されている。屑ゴムDを例えば600〜700℃で低温乾留する場合、その必要熱量は乾留ガスG1全量の燃焼熱よりも少ないため、状況に応じて乾留ガスG1は次の3方法により燃焼される。
【0025】
その1つは、乾留ガスG1の一部が燃焼室25に導かれ、燃焼するが、残りは燃焼炉30に直接導かれ、後述する水蒸気発生の燃料として使用されるもので、乾留ガスG1に同伴されるタールによる煙道の閉塞トラブルの発生のおそれのない場合には熱効率が高く、好ましい方法である。この場合、さらに燃焼室25にスチームSTが吹き込まれると、乾留ガスG1との間に水性ガス反応が生起するため、黒煙の発生が抑制され、下流の第2燃焼工程3又は燃焼炉30における未燃分・有害成分・悪臭成分の燃焼に当たっての装置・運転条件が著しく緩和される。
【0026】
2番目は、タールトラブルの発生のおそれがある場合に採用される方法であって、燃焼室25に乾留ガスG1の全量が導かれ、燃焼される。その際、燃焼ガスの温度が過度に高くならないよう、大過剰の空気が供給される。従って、大過剰の空気を含むため、レベルは低いが、大量の熱を保有する燃焼ガスが燃焼炉30に送られることになる。なお、一般に補助燃料F1は起動時もしくは失火防止のためにしか使用されない。
【0026】
さらに3番目は、燃焼室25に乾留ガスG1の全量が導かれ、乾留ガスG1との間に水性ガス反応が生起するよう、スチームノズルSNから乾留ガス燃焼室25の中にスチームSTが吹込まれる。それによって、黒煙の発生が抑制されるため、第2燃焼工程3又は燃焼炉30における未燃分・有害成分・悪臭成分の燃焼に当たっての装置・運転条件が著しく緩和される。
【0027】
乾留ガスG1の一部が燃焼室25に導かれる場合は、燃焼炉30において、乾留炉20から直接導かれた残りの乾留ガスG1及び補助燃料F2が燃焼し、その燃焼熱によって、乾留炉20の排ガスG2が加熱され、高温に保持され、排ガスG2中に含まれる未燃分・有害成分・悪臭成分等はすべて燃焼し、無害化・無臭化される。
【0028】
乾留ガスG1の全量が燃焼室25に導かれる場合は、燃焼炉30において、上述の通り、燃焼室25の排ガスG2中に含まれる未燃分及び補助燃料F2が燃焼し、その燃焼熱によって、燃焼室25の排ガスG2が加熱され、高温に保持され、未燃分・有害成分・悪臭成分等はすべて燃焼し、無害化・無臭化される。
【0029】
廃熱回収ボイラ40においては、燃焼炉30の排ガスG3が導かれ、その保有する熱により工場で使用する水蒸気Sが回収される。そのうえ、廃熱回収ボイラ40の排ガスG4は、それに僅かに含まれるダストが集塵装置70で捕集、除去された後、煙突80より大気中に放出される。
【0030】
以上のように屑ゴムDが乾留されることにより、先ず保温材その他に有効利用可能な炭化物Cが得られる。さらに上述したように、硫黄、塩素のかなり割合と殆ど全てのカーボンブラック及び灰分が炭化物に固定されると共に、排ガスから黒煙・有害成分・悪臭成分が燃焼除去されるため、灰分及び排ガスによる環境汚染の問題も一挙に解消される。しかも、屑ゴムDの乾留の熱源の大半が、その乾留時に発生する乾留ガスG1の燃焼熱によって供給されると共に、工場の各種熱源又は動力源として利用可能な水蒸気が得られる等、屑ゴムDが熱源として有効活用される。
【0031】
そのうえ、屑ゴムDの乾留時に発生する乾留ガスG1が何等の処理精製を経ずにそのまま燃焼され、その熱が屑ゴムDの乾留に利用されるため、処理精製に伴う熱損失が低減されると共に、装置が著しく簡略される。
【0031】
【発明の効果】
本発明は以上のように構成されるため、次の効果を奏する。すなわち、第1及び第2の発明によれば、(ア)屑ゴムDから保温材・耐火材その他に有効利用可能な炭化物Cが得られる。
(イ)その炭化物Cにより屑ゴムD中の硫黄分・塩素分のかなりの割合及び殆ど全てのカーボンブラック及び灰分の全量が固定されると共に、排ガスから黒煙・有害成分・悪臭成分が燃焼除去されるため、灰分及び排ガスによる環境汚染の問題も一挙に解消される。
(ウ)従って、廃熱回収ボイラ40の伝熱面への灰の沈積量が減少し、高い伝熱性が長期間保持されると共に排ガスG3に含まれる黒煙・有害成分・悪臭成分の除去され、低温域においてアルカリ等の塩化物から生じる塩酸その他による下流側の装置の腐食が防止される。
【0032】
(エ)屑ゴムDの乾留の熱源の大半が、その乾留時に発生する乾留ガスG1の燃焼熱によって供給されると共に、工場の各種熱源又は動力源として利用可能な水蒸気が得られる等、屑ゴムDが熱源として有効活用される。
(オ)さらに第3の発明によれば、上記効果に加えて、屑ゴムDの乾留時に発生する乾留ガスG1が何等の処理精製を経ずにそのまま燃焼され、その熱が屑ゴムDの乾留に利用されるため、処理精製に伴う熱損失が低減されると共に、装置が著しく簡略される。
(カ)そのうえ第4又は第5の発明によれば、上記効果に加えて、第1燃焼工程2又は乾留ガス燃焼室25において、黒煙の発生が抑制され、第2燃焼工程3又は燃焼炉30における未燃分・有害成分・悪臭成分の燃焼に当たっての装置及び運転条件が著しく緩和される。
【図面の簡単な説明】
【図1】本発明の実施の形態例を示す工程構成図である。
【図2】本発明の実施の形態例を示す機器構成図である。
【図3】乾留炉を示す断面図である。
【図4】本発明の別の実施の形態例を示す工程構成図である。
【図5】別の乾留炉を示す断面図である。
【符号の説明】
1 乾留工程
2 第1燃焼工程
3 第2燃焼工程
4 水蒸気発生工程
5 集塵工程
10 破砕機
20 乾留炉
21 回転円筒
22 供給室
23 排出室
25 乾留ガス燃焼室
30 燃焼炉
40 廃熱回収ボイラ
50 回転式クーラー
60 磁選機
70 集塵装置
80 煙突
C 炭化物
D 屑ゴム
F1 補助燃料
F2 補助燃料
G1 乾留ガス
G2 排ガス
G3 排ガス
G4 排ガス
H ガス排出孔
S 水蒸気
SN スチームノズル
ST スチーム
[0001]
BACKGROUND OF THE INVENTION
The present invention relates to a method for carbonizing scrap rubber and an apparatus therefor.
[0002]
[Prior art]
In a factory that manufactures rubber products, a large amount of waste rubber is generated. Since the waste rubber is difficult to reuse as it is, it is usually incinerated in an incinerator. However, when scrap rubber is incinerated, there is a problem that black smoke, harmful components and malodorous components are released and the surrounding environment is polluted. Moreover, incineration ash generated by incineration is difficult to reuse, and there is no effective means other than burying in the ground, and the burden is not small.
[0003]
[Problems to be solved by the invention]
The problem to be solved is that the conventional method of incineration of scrap rubber emits black smoke, harmful components and malodorous components, pollutes the surrounding environment, and incineration ash generated by incineration is difficult to reuse. Therefore, there is no effective means other than embedding in the ground, and the present invention provides a method and apparatus for carbonizing scrap rubber that solves the above-mentioned problems.
[0004]
[Means for solving problems]
As shown in FIGS. 1 and 2, the carbonization method for waste rubber according to the first aspect of the invention comprises dry distillation of waste rubber D by indirect heating to obtain carbide C and dry distillation gas G1, dry distillation gas G1 of dry distillation step 1 A first combustion step 2 for burning at least a part of the gas to generate heat necessary for the dry distillation step 1, and a second combustion for burning unburned components, harmful components and malodorous components in the exhaust gas G2 of the first combustion step 2. The process comprises a combustion process 3 and a steam generation process 4 that generates steam S using the heat held by the exhaust gas G3 of the second combustion process 3. As shown in FIGS. In the first combustion step 2 of the invention , steam ST is added in the process of burning at least a part of the dry distillation gas G1 of the dry distillation step 1, and a water gas reaction is caused between the dry distillation gas G1. Is.
[0005]
As shown in FIGS. 2 and 3, the scrap rubber carbonization apparatus according to the second aspect of the present invention dry-distills the scrap rubber D by indirect heating while the scrap rubber D is supplied from one end of the rotating cylinder 21 and discharged from the other end. A carbonization furnace 20 configured to obtain the carbide C and the carbonization gas G1 and to transmit heat generated by burning at least a part of the carbonization gas G1 to the scrap rubber D through the wall surface of the rotating cylinder 21; A waste heat recovery boiler that generates steam S using the combustion furnace 30 that burns unburned components, harmful components, and malodorous components of the exhaust gas G2 of the carbonization furnace 20 and the exhaust gas G3 of the combustion furnace 30 As shown in FIG. 3, the dry distillation furnace 20 of the second invention rotates to roll the scrap rubber D and has a plurality of gas discharge holes H for discharging the generated dry distillation gas G1. A rotating cylinder 21; A dry distillation gas combustion chamber 25 surrounding the rotary cylinder 21, and heat generated by burning at least part of the dry distillation gas G 1 introduced from the rotary cylinder 21 through the gas discharge hole H. In the carbonizing apparatus configured to transmit to the scrap rubber D through the wall surface of the gas, the carbonizing apparatus is a water gas between the dry distillation gas G1 in the dry distillation gas combustion chamber 25 of the first invention as shown in FIG. A steam nozzle SN that blows steam ST into the dry distillation gas combustion chamber 25 is provided so as to cause a reaction .
[0009]
According to the 1st or 2nd invention, the carbide | carbonized_material C which can be effectively utilized for a heat insulating material etc. from the waste rubber D is obtained. The carbide C fixes a significant proportion of sulfur and chlorine and almost all carbon black and ash, and burns and removes black smoke, harmful components, and offensive odor components from the exhaust gas G3. This problem is solved at once. Furthermore, most of the heat source of the dry distillation of the waste rubber D is supplied by the combustion heat of the dry distillation gas G1 generated during the dry distillation, and water vapor that can be used as various heat sources or power sources of the factory is obtained. Effectively used as a heat source.
[0010]
In addition to the above Symbol operational effects, since the carbonization gas G1 generated during dry distillation of waste rubber D is directly combusted without going through the process purification of what such, its heat is utilized to dry distillation of waste rubber D, due to processing purification The heat loss is reduced and the device is greatly simplified.
[0011]
Furthermore, in the 1st combustion process 2 or the dry distillation gas combustion chamber 25, since water gas reaction arises between dry distillation gas G1, generation | occurrence | production of black smoke is suppressed and the unburned in the 2nd combustion process 3 or the combustion furnace 30 Equipment and operating conditions for the combustion of components, harmful components, and malodorous components are remarkably eased.
[0012]
DETAILED DESCRIPTION OF THE INVENTION
The embodiment of the present invention will be described with reference to FIGS. 1 to 5. In the dry distillation step 1, the waste rubber D is indirectly heated by the combustion heat of at least a part of the auxiliary fuel F1 and the dry distillation gas G1, as will be described later. And carbonized to obtain carbide C. In dry distillation, a considerable proportion of ash, sulfur, and chlorine is not accompanied by the dry distillation gas G1, and is fixed to the carbide C.
[0013]
In the first combustion process 2, as described above, at least a part of the dry distillation gas G1 derived from the dry distillation process 1 and the auxiliary fuel F1 are combusted. In addition, as shown in FIG. 4, in the process in which at least a part of the dry distillation gas G1 in the dry distillation process 1 is combusted, the steam ST is added so that a water gas reaction occurs with the dry distillation gas G1. As described later, this is extremely preferable.
[0014]
In the second combustion process 3, the remainder of the dry distillation gas G 1 that is introduced without being used in the dry distillation process 2 and unburned components, harmful components, and malodorous components in the exhaust gas G 2 of the first combustion process 2 are combusted. In the steam generation step 4, the heat held by the high-temperature exhaust gas G3 in the second combustion step 3 is recovered, and steam S that can be used as various heat sources or power sources in the factory is generated. In addition, 5 is a dust collection process which collects and removes the dust contained in the waste gas G4 of the water vapor generation process 4.
[0015]
The apparatus will be described with reference to FIGS. 2, 3, and 5. A dry distillation furnace 20 having a rotating cylinder 21 for carbonizing scrap rubber D by indirect heating to obtain carbide C, and an unburned exhaust gas G <b> 2 from the dry distillation furnace 20. The steam S is generated using the combustion furnace 30 that burns the remaining part of the dry distillation gas G1 not directly used in the dry distillation furnace 20 and the exhaust gas G3 of the combustion furnace 30 by using the minute, harmful component, malodorous component, and the remainder of the dry distillation gas G1. In addition to the waste heat recovery boiler 40 that generates slag, the crusher 10 that crushes the waste rubber D to 20 mm or less, the rotary cooler 50 that indirectly cools the carbide C discharged from the dry distillation furnace 20, and the iron content in the carbide C The magnetic separator 60 is removed.
[0016]
Moreover, as shown in FIG.3 and FIG.5, the carbonization furnace 20 rolls the waste rubber D supplied from one end, and puts the waste rubber D into the inlet / outlet of the rotary circle 21 discharged from the other end. A supply chamber 22 to be supplied and a discharge chamber 23 for discharging the carbide C and the dry distillation gas G1 are provided. Further, the rotating cylinder 21 is surrounded by a dry distillation gas combustion chamber 25, and a large number of gas discharge holes H communicating with the dry distillation gas combustion chamber 25 are formed in the side surface.
[0017]
Although not shown in the drawing, the dry distillation gas combustion chamber 25 is provided with a port for introducing air necessary for combustion. Further, as shown in FIG. 5, the steam nozzle SN into which the steam ST is blown into the dry distillation gas combustion chamber 25 is provided so as to cause a water gas reaction with the dry distillation gas G1, as described later. This is preferable.
[0018]
Further, in order to prevent the solid content of the rotating cylinder 21 from falling into the combustion chamber 25 from the gas discharge hole H, a straight cylinder is projected from the gas discharge hole H into the rotating cylinder 21 in the figure. It is not limited to this as long as it is configured so that the dry distillation gas G1 can pass therethrough and the solid content does not fall into the combustion chamber 25, such as a cylindrical shape bent in a letter shape.
[0019]
Moreover, the pressure in the dry distillation gas combustion chamber 25 is kept slightly lower than the pressure in the rotary cylinder 21 so that at least a part of the dry distillation gas G1 generated in the rotary cylinder 21 can flow out. At least a part of the fuel F1 and the dry distillation gas G1 is combusted, and the combustion heat is transmitted to the scrap rubber D through the wall surface of the rotating cylinder 21. In addition, 70 is a dust collector such as a bag filter that collects and removes dust contained in the exhaust gas G4 of the waste heat recovery boiler 40, and 80 is a chimney that releases the exhaust gas G4 into the atmosphere.
[0020]
EXAMPLE An example in which scrap rubber mainly composed of ethylene-propylene-diene rubber (EPDM), oil, and carbon black is carbonized will be described below.
[0021]
Industrial analysis results of waste rubber
%
Volatile content 59.3
Total sulfur 1.17
Chlorine content 0.05
Ash content 9.93
Carbon black 34.3
Total calorific value 8,680Kcal / kg
[0022]
The scrap rubber D crushed and carried by the crusher 10 to 20 mm or less is sent to one end of the rotating cylinder 21 of the dry distillation furnace 20. In the combustion chamber 25 surrounding the side surface of the rotating cylinder 21, at least a part of the auxiliary fuel F1 and the dry distillation gas G1 is burned as will be described later. By the combustion heat, the scrap rubber D that rolls in the rotating cylinder 21 is indirectly heated, dry-distilled, and becomes carbide C, which is discharged from the other end.
[0023]
The industrial analysis results of carbide C are as follows.
%
Yield 45
Fixed carbon 67.34
Volatile content 10.66
Ash 22.0
P 0.005
S 1.89
C1 0.21
[0024]
The pressure in the rotary cylinder 21 is pierced on the side surface so that the combustion gas G2 in the combustion chamber 25 does not enter the rotary cylinder 21 from the plurality of gas discharge holes H, and at least a part of the dry distillation gas G1 is in the combustion chamber 25. The pressure is controlled to be slightly higher than the pressure in the combustion chamber 25 so as to be combustible. When scrap rubber D is subjected to low temperature dry distillation at, for example, 600 to 700 ° C., the necessary heat amount is less than the combustion heat of the total amount of dry distillation gas G1, so that dry distillation gas G1 is combusted according to the following three methods.
[0025]
One of them is that a part of the dry distillation gas G1 is led to the combustion chamber 25 and burns, but the rest is directly led to the combustion furnace 30 and used as fuel for generating steam, which will be described later. This is a preferable method because the thermal efficiency is high when there is no risk of trouble of flue blockage due to the accompanying tar. In this case, when steam ST is further blown into the combustion chamber 25, a water gas reaction occurs with the dry distillation gas G <b> 1, so that the generation of black smoke is suppressed and the downstream second combustion step 3 or the combustion furnace 30 Equipment and operating conditions for burning unburned components, harmful components, and offensive odor components are significantly reduced.
[0026]
The second method is employed when there is a possibility of occurrence of tar trouble, and the entire amount of dry distillation gas G1 is introduced into the combustion chamber 25 and burned. At that time, a large excess of air is supplied so that the temperature of the combustion gas does not become excessively high. Accordingly, the combustion gas containing a large amount of heat is sent to the combustion furnace 30 although the level is low because it contains a large excess of air. In general, the auxiliary fuel F1 is used only for starting or for preventing misfire.
[0026]
Third, steam ST is blown from the steam nozzle SN into the dry distillation gas combustion chamber 25 so that the entire amount of the dry distillation gas G1 is introduced into the combustion chamber 25 and a water gas reaction occurs with the dry distillation gas G1. It is. Thereby, since the generation of black smoke is suppressed, the apparatus and operating conditions for burning unburned components, harmful components, and malodorous components in the second combustion step 3 or the combustion furnace 30 are remarkably eased.
[0027]
When a part of the dry distillation gas G1 is introduced into the combustion chamber 25, the remaining dry distillation gas G1 and the auxiliary fuel F2 directly introduced from the dry distillation furnace 20 are combusted in the combustion furnace 30, and the dry heat of the dry distillation gas G1 is obtained by the combustion heat. The exhaust gas G2 is heated and maintained at a high temperature, and all unburned components, harmful components, malodorous components, etc. contained in the exhaust gas G2 are combusted and rendered harmless and non-brominated.
[0028]
When the total amount of the dry distillation gas G1 is led to the combustion chamber 25, in the combustion furnace 30, as described above, the unburned fuel and the auxiliary fuel F2 contained in the exhaust gas G2 of the combustion chamber 25 are combusted, and by the combustion heat, The exhaust gas G2 in the combustion chamber 25 is heated and maintained at a high temperature, and all unburned components, harmful components, malodorous components, etc. are burned and rendered harmless and non-brominated.
[0029]
In the waste heat recovery boiler 40, the exhaust gas G3 of the combustion furnace 30 is guided, and the steam S used in the factory is recovered by the heat held therein. In addition, the exhaust gas G4 of the waste heat recovery boiler 40 is discharged from the chimney 80 into the atmosphere after dust contained in the exhaust gas G4 is collected and removed by the dust collector 70.
[0030]
As the waste rubber D is dry-distilled as described above, first, the carbide C that can be effectively used for the heat insulating material and the like is obtained. Furthermore, as described above, a considerable proportion of sulfur and chlorine and almost all carbon black and ash are fixed to the carbide, and black smoke, harmful components and malodorous components are burned and removed from the exhaust gas. The problem of contamination is solved all at once. In addition, most of the heat source for the carbonization of the scrap rubber D is supplied by the combustion heat of the dry distillation gas G1 generated during the carbonization, and the steam rubber that can be used as various heat sources or power sources in the factory is obtained. Is effectively used as a heat source.
[0031]
In addition, the dry distillation gas G1 generated during the dry distillation of the waste rubber D is burned as it is without undergoing any treatment purification, and the heat is used for the dry distillation of the waste rubber D, so that heat loss associated with the treatment purification is reduced. At the same time, the device is significantly simplified.
[0031]
【The invention's effect】
Since this invention is comprised as mentioned above, there exists the following effect. That is, according to the first and second inventions, (a) the carbide C that can be effectively used for the heat insulating material, the refractory material and the like from the scrap rubber D is obtained.
(B) The carbon C fixes a considerable proportion of sulfur and chlorine in the scrap rubber D and almost all of the carbon black and ash, and burns and removes black smoke, harmful components and malodorous components from the exhaust gas. Therefore, the problem of environmental pollution due to ash and exhaust gas is solved at once.
(C) Accordingly, the amount of ash deposited on the heat transfer surface of the waste heat recovery boiler 40 is reduced, high heat transfer is maintained for a long period of time, and black smoke, harmful components and malodorous components contained in the exhaust gas G3 are removed. Corrosion of the downstream apparatus due to hydrochloric acid or the like generated from chloride such as alkali in the low temperature range is prevented.
[0032]
(D) Most of the heat source of dry distillation of the waste rubber D is supplied by the combustion heat of the dry distillation gas G1 generated during the dry distillation, and steam that can be used as various heat sources or power sources of the factory is obtained. D is effectively used as a heat source.
(E) Further, according to the third invention, in addition to the above-described effects, the dry distillation gas G1 generated during the dry distillation of the waste rubber D is burned as it is without undergoing any treatment purification, and the heat thereof is the dry distillation of the waste rubber D. Therefore, the heat loss accompanying the process purification is reduced and the apparatus is remarkably simplified.
(F) Moreover, according to the fourth or fifth invention, in addition to the above effects, the generation of black smoke is suppressed in the first combustion step 2 or the dry distillation gas combustion chamber 25, and the second combustion step 3 or the combustion furnace. The apparatus and operating conditions for burning unburned components, harmful components, and malodorous components at 30 are remarkably eased.
[Brief description of the drawings]
FIG. 1 is a process configuration diagram showing an embodiment of the present invention.
FIG. 2 is a device configuration diagram showing an embodiment of the present invention.
FIG. 3 is a cross-sectional view showing a carbonization furnace.
FIG. 4 is a process configuration diagram showing another embodiment of the present invention.
FIG. 5 is a cross-sectional view showing another dry distillation furnace.
[Explanation of symbols]
DESCRIPTION OF SYMBOLS 1 Carbonization process 2 1st combustion process 3 2nd combustion process 4 Water vapor generation process 5 Dust collection process 10 Crusher 20 Dry distillation furnace 21 Rotating cylinder 22 Supply chamber 23 Discharge chamber 25 Dry distillation gas combustion chamber 30 Combustion furnace 40 Waste heat recovery boiler 50 Rotary cooler 60 Magnetic separator 70 Dust collector 80 Chimney C Carbide D Waste rubber F1 Auxiliary fuel F2 Auxiliary fuel G1 Dry distillation gas G2 Exhaust gas G3 Exhaust gas G4 Exhaust gas H Gas exhaust hole S Steam SN Steam nozzle ST Steam

Claims (2)

屑ゴム(D)を間接加熱により乾留し、炭化物(C)及び乾留ガス(G1)を得る乾留工程(1)、乾留工程(1)の乾留ガス(G1)の少なくとも一部を燃焼し、前記乾留工程(1)に必要な熱を発生させる第1燃焼工程(2)、前記第1燃焼工程(2)の排ガス(G2)中の未燃分・有害成分・悪臭成分を燃焼する第2燃焼工程(3)、及びその第2燃焼工程(3)の排ガス(G3)の保有する熱を利用して、水蒸気(S)を発生させる水蒸気発生工程(4)より構成されており、第1燃焼工程(2)において、乾留工程(1)の乾留ガス(G1)の少なくとも一部を燃焼する過程で、スチーム(ST)を添加し、乾留ガス(G1)との間に水性ガス反応を生起させることを特徴とする屑ゴムの炭化方法。The waste rubber (D) is carbonized by indirect heating to obtain a carbide (C) and a carbonized gas (G1), the carbonization process (1), combusting at least a part of the carbonization gas (G1) of the carbonization process (1), A first combustion step (2) for generating heat necessary for the carbonization step (1), and a second combustion for burning unburned components, harmful components and malodorous components in the exhaust gas (G2) of the first combustion step (2). It is composed of a steam generation step (4) that generates steam (S) using the heat held in the exhaust gas (G3) of the step (3) and the second combustion step (3), and the first combustion In the step (2), steam (ST) is added in the process of burning at least a part of the dry distillation gas (G1) in the dry distillation step (1) to cause a water gas reaction with the dry distillation gas (G1). A method for carbonizing waste rubber, characterized in that: 屑ゴム(D)を回転円筒(21)の一端から供給し、他端から排出させる間に、屑ゴム(D)を間接加熱により乾留し、炭化物(C)及び乾留ガス(G1)を得ると共に、その乾留ガス(G1)の少なくとも一部を燃焼させることによって生じた熱を回転円筒(21)の壁面を介して屑ゴム(D)に伝達させるよう構成した乾留炉(20)、その乾留炉(20)の排ガス(G2)の未燃分・有害成分・悪臭成分を燃焼させる燃焼炉(30)、及びその燃焼炉(30)の排ガス(G3)の保有する熱を利用して、水蒸気(S)を発生させる廃熱回収ボイラ(40)を備えており、当該乾留炉(20)が、屑ゴム(D)を転動させるよう回転すると共に、発生した乾留ガス(G1)を排出させる複数のガス排出孔(H)を有する回転円筒(21)と、その回転円筒(21)を包囲する乾留ガス燃焼室(25)と、を備え、前記回転円筒(21)からガス排出孔(H)を経て導入された乾留ガス(G1)を燃焼させることによって生じた熱を回転円筒(21)の壁面を介して屑ゴム(D)に伝達するよう構成した炭化装置において、当該乾留ガス燃焼室(25)に、乾留ガス(G1)との間に水性ガス反応を生起させるよう、乾留ガス燃焼室(25)にスチ−ム(ST)を吹き込むスチームノズル(SN)を設けたことを特徴とする屑ゴムの炭化装置。While the waste rubber (D) is supplied from one end of the rotating cylinder (21) and discharged from the other end, the waste rubber (D) is dry-distilled by indirect heating to obtain carbide (C) and dry-distilled gas (G1). A dry distillation furnace (20) configured to transmit heat generated by burning at least a part of the dry distillation gas (G1) to the scrap rubber (D) through the wall surface of the rotating cylinder (21), and the dry distillation furnace (20) Combustion furnace (30) for burning unburned components, harmful components, and offensive odor components of exhaust gas (G2) of (20), and using heat stored in the exhaust gas (G3) of the combustion furnace (30), steam ( A waste heat recovery boiler (40) that generates S), and the carbonization furnace (20) rotates to roll the scrap rubber (D) and discharges the generated carbonization gas (G1). Rotating cylinder (21) with a gas exhaust hole (H) A dry distillation gas combustion chamber (25) surrounding the rotary cylinder (21), and burning the dry distillation gas (G1) introduced from the rotary cylinder (21) through the gas discharge hole (H). In the carbonization apparatus configured to transmit the generated heat to the scrap rubber (D) through the wall surface of the rotating cylinder (21), water gas is provided between the dry distillation gas combustion chamber (25) and the dry distillation gas (G1). A scrap rubber carbonization device provided with a steam nozzle (SN) for blowing steam (ST) into a dry distillation gas combustion chamber (25) so as to cause a reaction .
JP24194297A 1997-03-11 1997-08-22 Waste rubber carbonization method and apparatus Expired - Fee Related JP3845773B2 (en)

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