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JP2008032299A - Tar removing method of external heating type rotary kiln - Google Patents

Tar removing method of external heating type rotary kiln Download PDF

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Publication number
JP2008032299A
JP2008032299A JP2006205236A JP2006205236A JP2008032299A JP 2008032299 A JP2008032299 A JP 2008032299A JP 2006205236 A JP2006205236 A JP 2006205236A JP 2006205236 A JP2006205236 A JP 2006205236A JP 2008032299 A JP2008032299 A JP 2008032299A
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Japan
Prior art keywords
retort
temperature
tar
rotary kiln
temporarily
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JP2006205236A
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Japanese (ja)
Inventor
Masao Shimada
正夫 島田
Hirohide Yamamoto
博英 山本
Hiromasa Inoki
博雅 猪木
Shigehito Kado
重仁 嘉戸
Kenji Shimizu
健司 清水
Susumu Shimura
進 志村
Tadatoshi Kabuto
忠敏 甲
Makoto Kitabayashi
誠 北林
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Daido Steel Co Ltd
Japan Sewage Works Agency
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Daido Steel Co Ltd
Japan Sewage Works Agency
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Priority to JP2006205236A priority Critical patent/JP2008032299A/en
Publication of JP2008032299A publication Critical patent/JP2008032299A/en
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  • Treatment Of Sludge (AREA)
  • Coke Industry (AREA)
  • Waste-Gas Treatment And Other Accessory Devices For Furnaces (AREA)
  • Muffle Furnaces And Rotary Kilns (AREA)

Abstract

<P>PROBLEM TO BE SOLVED: To improve efficiency in furnace operation by dispensing with periodical tar scraping-off work. <P>SOLUTION: Sludge M is supplied into a rotating cylindrical retort 2, and the carbonized by heating from an external heating chamber 11 receiving the retort 2. By temporarily raising a temperature of the external heating chamber 11, a temperature in the retort 2 is temporarily raised to a temperature necessary for separating tar over a normal operation temperature for inhibiting volatilization elimination of an organic flammable component. The separated tar is discharged from the retort 2 with the carbonized sludge M. <P>COPYRIGHT: (C)2008,JPO&INPIT

Description

本発明は、回転するレトルトを外部から加熱する外熱室を設けた外熱式ロータリキルンのタール除去方法に関するものである。   The present invention relates to a tar removal method for an external heating rotary kiln provided with an external heat chamber for heating a rotating retort from the outside.

下水の乾燥汚泥等の有機性廃棄物を無酸素ないし低酸素状態で熱分解(炭化)して、バイオマス燃料に使用できる有用な炭化物にする等の用途に外熱式ロータリキルンが使用されており、その一例を図3に示す。図3において、外熱式ロータリキルンの炉体1内の上半に形成された外熱室11にはこれを貫通して筒状のレトルト2が設けてある。レトルト2は一端部25と他端部26の外周に設けたリング体21がそれぞれ図略のロ−ラに支持されるとともに、一端部25の外周に設けたスプロケット22に駆動チェーンが懸架されて回転させられている。   Externally heated rotary kilns are used for applications such as the thermal decomposition (carbonization) of organic waste such as dried sludge from sewage in an oxygen-free or low-oxygen state to produce useful carbides that can be used for biomass fuel. An example thereof is shown in FIG. In FIG. 3, an external heat chamber 11 formed in the upper half of the furnace body 1 of the external heat type rotary kiln is provided with a cylindrical retort 2 penetrating therethrough. In the retort 2, ring bodies 21 provided on the outer periphery of the one end portion 25 and the other end portion 26 are respectively supported by a roller (not shown), and a drive chain is suspended on a sprocket 22 provided on the outer periphery of the one end portion 25. It is rotated.

炉体1内に位置するレトルト2の上流端部23内にはホッパ13の底部から延びるスクリューコンベア14が位置して、ホッパ13内に貯留された汚泥Mがレトルト2内に搬入される。レトルト2内に搬入された汚泥Mはやや傾斜させたレトルト2の回転に伴ってその他端部26方向へ移送され、この過程で外熱室11の高温により加熱炭化されて、排出筒15内に開口するレトルト排出口16へ至り、排出される。レトルト2の筒壁には長手方向の複数位置にガス噴出管4が設けられており、炭化の過程で汚泥Mから放出される乾留ガスが、ガス噴出管4を経て外熱室11へ噴出させられて、外熱室11の炉床17上に配設された助燃バーナ51によって着火させられる。以後、ガス噴出管4から噴出させられた乾留ガスは自燃状態となり、助燃バーナは消火され、あるいは燃焼状態が絞られる。なお、燃焼排ガスは、レトルト2の下流端部24に対向する外熱室11の炉床17部に設けた通気口18を経て、バーナ52を備えた二次燃焼室12に至り、開口19から排煙ダクト(図示略)を経て煙突に向かう。   A screw conveyor 14 extending from the bottom of the hopper 13 is located in the upstream end 23 of the retort 2 located in the furnace body 1, and the sludge M stored in the hopper 13 is carried into the retort 2. The sludge M carried into the retort 2 is transferred toward the other end 26 along with the rotation of the slightly inclined retort 2, and is heated and carbonized by the high temperature of the external heat chamber 11 in this process. The retort discharge port 16 that opens is discharged. Gas jet pipes 4 are provided on the cylindrical wall of the retort 2 at a plurality of positions in the longitudinal direction, and dry distillation gas released from the sludge M during the carbonization process is jetted to the external heat chamber 11 through the gas jet pipe 4. And is ignited by the auxiliary burner 51 disposed on the hearth 17 of the external heat chamber 11. Thereafter, the dry distillation gas ejected from the gas ejection pipe 4 is in a self-combustion state, and the auxiliary burner is extinguished or the combustion state is reduced. The combustion exhaust gas reaches the secondary combustion chamber 12 provided with the burner 52 through the vent 18 provided in the hearth 17 portion of the external heat chamber 11 facing the downstream end portion 24 of the retort 2, and from the opening 19. It goes to the chimney through a smoke exhaust duct (not shown).

ところで、有機性廃棄物中には低温分解性の有機可燃成分が多く含まれているが、上記従来のロータリキルンでは800℃程度の高温になる外熱室の熱がレトルト2内に及んで、上記有機可燃成分の大部分がガス化揮発して消失し、生成された炭化物の燃料価値が低下してしまうという問題があった。   By the way, the organic waste contains a lot of low-temperature decomposable organic combustible components, but in the conventional rotary kiln, the heat of the external heat chamber that reaches a high temperature of about 800 ° C. reaches the retort 2, There was a problem that most of the organic combustible component was gasified and volatilized and disappeared, and the fuel value of the generated carbide was reduced.

そこで、例えば特許文献1に示されたロータリキルンでは、レトルトの筒壁全体に断熱材を敷設してレトルト内の温度上昇を450℃以下に留め、低温分解性の有機可燃成分の揮発消失を抑制している。
特開平11−304364
Therefore, for example, in the rotary kiln disclosed in Patent Document 1, a heat insulating material is laid on the entire tubular wall of the retort to keep the temperature rise in the retort below 450 ° C., thereby suppressing the loss of volatilization of the low temperature decomposable organic combustible component is doing.
JP-A-11-304364

しかし、発明者等の実験によると、レトルト内温度を400℃程度の低温にして有機可燃成分の揮発消失を抑制すると、レトルトの内壁にタール分が付着して成長し、特に、レトルトの下流端部内壁に、定常的な空気侵入を防止し炭化材の定量的な排出を可能にするスパイラル突起を設けた場合等には、ここにタール分が付着して炭化材の排出ができなくなるおそれがあった。このため、定期的に炉の操業を停止して、レトルト内に付着したタールを掻き出す等の作業が必要であった。   However, according to experiments by the inventors, when the internal temperature of the retort is set to a low temperature of about 400 ° C. and the volatilization disappearance of the organic combustible component is suppressed, tar content adheres to the inner wall of the retort, If the inner wall is provided with spiral protrusions that prevent steady air intrusion and allow quantitative discharge of the carbonized material, there is a risk that tar will adhere to it and carbonized material cannot be discharged. there were. For this reason, operations such as periodically stopping the operation of the furnace and scraping off the tar adhered in the retort are necessary.

そこで、本発明はこのような課題を解決するもので、有機可燃成分の揮発消失を最小限に抑制しつつ定期的なタール掻出し作業を不要として炉操業の効率化を図った外熱式ロータリキルンのタール除去方法を提供することを目的とする。   Accordingly, the present invention solves such a problem, and an externally heated rotary shaft that improves the efficiency of the furnace operation by minimizing the volatilization loss of organic combustible components and eliminating the need for periodic tar scraping work. It aims at providing the tar removal method of a kiln.

上記目的を達成するために、本発明は、回転する筒状レトルト(2)内へ被処理材(M)を供給し、当該レトルト(2)を収容する外熱室(11)からの加熱によって被処理材(M)を炭化するようにした外熱式ロータリキルンのタール除去方法であって、レトルト(2)内の温度を有機可燃成分の揮発消失を抑制する通常操業温度を越えてタールの剥離に必要な温度まで一時的に上昇させることを特徴としている。ここで、上記レトルト内温度の上昇は、外熱室(11)の室温を一時的に上昇させることにより行うことができ、あるいはレトルト(2)内に一時的に空気を吹き込むことにより行うことができ、さらには被処理材(M)の含水率を一時的に低下させることにより行うことができる。本発明においては、レトルト内温度をタールの剥離に必要な温度まで一時的に上昇させることで、レトルト内壁からのタールの剥離が促進される。剥離したタールは炭化された被処理材とともにレトルトから排出される。これにより、定期的なタール掻出し作業は不要となる。   In order to achieve the above-mentioned object, the present invention supplies the material to be treated (M) into the rotating cylindrical retort (2) and heats it from the external heat chamber (11) that houses the retort (2). A tar removal method for an externally heated rotary kiln that carbonizes a material to be treated (M), wherein the temperature in the retort (2) exceeds the normal operating temperature that suppresses the volatilization loss of organic combustible components. It is characterized by being temporarily raised to a temperature necessary for peeling. Here, the temperature increase in the retort can be performed by temporarily increasing the room temperature of the external heat chamber (11), or can be performed by temporarily blowing air into the retort (2). Furthermore, it can be performed by temporarily reducing the moisture content of the material to be treated (M). In the present invention, the peeling of tar from the inner wall of the retort is promoted by temporarily raising the temperature inside the retort to a temperature necessary for peeling of the tar. The peeled tar is discharged from the retort together with the carbonized workpiece. This eliminates the need for periodic tar scraping work.

以上のように、本発明の外熱式ロータリキルンによれば、有機可燃成分の揮発消失を抑制しつつ、しかも定期的なタール掻出し作業が不要であるから炉操業の効率化を実現することができる。   As described above, according to the externally heated rotary kiln of the present invention, it is possible to suppress the volatilization and disappearance of the organic combustible component, and to realize the efficiency of the furnace operation because the periodic tar scraping work is unnecessary. Can do.

(第1実施形態)
図1には本発明に係る外熱式ロータリキルンの概略断面図を示し、従来技術と同一部分には同一符号を付してある。図1において、ロータリキルンの炉体1内には上半に外熱室11が形成され、炉床17で区画された炉体1の下半は二次燃焼室12となっている。外熱室11を貫通して筒状のレトルト2が設けてあり、レトルト2は一端部25と他端部26に設けたリング体21がそれぞれ図略のロ−ラに支持されるとともに、一端部25外周に設けたスプロケット22に駆動チェーンが懸架されて回転させられている。レトルト2の上流端部23内にはホッパ13の底部から延びるスクリューコンベア14が位置して、ホッパ13内に貯留された汚泥Mがレトルト2内に搬入される。レトルト2の他端部26は排出筒15内に至り、ここに排出口16が設けられている。
(First embodiment)
FIG. 1 is a schematic cross-sectional view of an externally heated rotary kiln according to the present invention. In FIG. 1, an external heat chamber 11 is formed in the upper half of a furnace body 1 of a rotary kiln, and a lower half of the furnace body 1 partitioned by a hearth 17 is a secondary combustion chamber 12. A cylindrical retort 2 is provided through the external heat chamber 11, and the retort 2 includes a ring body 21 provided at one end portion 25 and the other end portion 26, supported by a roller (not shown), and one end A drive chain is suspended and rotated by a sprocket 22 provided on the outer periphery of the portion 25. A screw conveyor 14 extending from the bottom of the hopper 13 is positioned in the upstream end 23 of the retort 2, and the sludge M stored in the hopper 13 is carried into the retort 2. The other end portion 26 of the retort 2 reaches the inside of the discharge cylinder 15, and the discharge port 16 is provided here.

レトルト2の筒壁には上流端部23のみに、内外方向へ貫通するガス噴出管4が設けられている。炉体1の頂壁にはレトルト長手方向の二箇所に熱電対61,62が設けられて、外熱室11の室内温度を二箇所で検出している。炉床17近くの炉壁にはレトルト長手方向の4箇所にバーナ7が設けられ、これらバーナ7は上流側の第1ゾーンZ1内に位置する一対が、熱電対61の検出信号をフィードバックした温度調節計(図示略)によってその燃焼を制御され、下流側の第2ゾーンZ2内に位置する一対は、熱電対62の検出信号をフィードバックした温度調節計(図示略)によってその燃焼を制御されている。炉床17には、レトルト2の上流端部23に対応する位置に二次燃焼室12へ連通する通気口18が設けられている。二次燃焼室12内にはバーナ52が設けられており、当該二次燃焼室12は下流側の炉壁に設けた開口19を経て排煙ダクトに連通している。   A gas jet pipe 4 penetrating inward and outward is provided only in the upstream end 23 on the cylindrical wall of the retort 2. Thermocouples 61 and 62 are provided at two locations in the retort longitudinal direction on the top wall of the furnace body 1 to detect the room temperature of the external heat chamber 11 at two locations. Burners 7 are provided at four locations in the longitudinal direction of the retort on the furnace wall near the hearth 17, and these burners 7 are temperatures at which a pair located in the first zone Z 1 on the upstream side feeds back a detection signal of the thermocouple 61. Combustion is controlled by a controller (not shown), and the pair located in the downstream second zone Z2 is controlled by a temperature controller (not shown) that feeds back a detection signal of the thermocouple 62. Yes. The hearth 17 is provided with a vent 18 that communicates with the secondary combustion chamber 12 at a position corresponding to the upstream end 23 of the retort 2. A burner 52 is provided in the secondary combustion chamber 12, and the secondary combustion chamber 12 communicates with the smoke exhaust duct through an opening 19 provided in the downstream furnace wall.

このような構造の外熱式ロータリキルンにおいて、ホッパ13内に貯留された汚泥Mがレトルト2内に搬入されて、やや傾斜させたレトルト2の回転に伴ってその下流方向へ移送され、この過程で外熱室11からの熱で炭化されて、排出筒15内に開口するレトルト排出口16へ至り、排出される。汚泥Mが炭化される特に初期には乾留ガスが多く生成するが、これはレトルト2筒壁の上流端部23に設けたガス噴出管4からレトルト2外へ排出されるとともに、この付近に開口する通気口18を経て、外熱室11内に滞留して自燃することなく速やかに二次燃焼室12内へ導入される。そして、バーナ52によって臭気成分が燃焼分解された後、開口19から排煙ダクトを経て、煙突から排出される。   In the externally heated rotary kiln having such a structure, the sludge M stored in the hopper 13 is carried into the retort 2 and transferred in the downstream direction as the retort 2 is slightly inclined. Then, it is carbonized by the heat from the external heat chamber 11, reaches the retort discharge port 16 opened in the discharge cylinder 15, and is discharged. Particularly in the initial stage when the sludge M is carbonized, a large amount of dry distillation gas is generated, which is discharged from the gas ejection pipe 4 provided at the upstream end 23 of the retort 2 cylindrical wall to the outside of the retort 2 and opened in the vicinity thereof. Through the vent 18, the air is quickly introduced into the secondary combustion chamber 12 without staying in the external heat chamber 11 and burning itself. Then, after the odor component is burned and decomposed by the burner 52, it is discharged from the chimney through the smoke exhaust duct from the opening 19.

一方、外熱室11は、レトルト内での水分蒸発が盛んで加熱熱量を必要とする上流側の第1ゾーンZ1と、水分蒸発は相対的に少ない第2ゾーンZ2とで個別に、バーナ7の燃焼制御によってそれぞれ410℃〜450℃、好ましくは420℃〜430℃に正確に維持される。これにより、レトルト内温度は390℃〜430℃、好ましくは390℃〜410℃に保たれて、炭化汚泥中の有機可燃成分の揮発消失が抑制される。ここで、本実施形態では、第1ゾーンZ1と第2ゾーンZ2の設定温度を1日1回程度、通常操業時の温度である上記420℃〜430℃から、例えば600℃程度まで一時的に上昇させ、その後、元の温度に戻す。これに伴ってレトルト2内の温度は400℃程度から470℃〜500℃まで上昇した後、再び元の温度に戻る。この時間は例えば20分〜40分とする。このようにして一時的にレトルト2内の温度を上昇させることにより、レトルト2の内壁に付着したタール分は剥離して、汚泥炭化物とともに排出口16からレトルト2外へ排出される。したがって、定期的なタール掻出し作業が不要となり、炉操業の効率化が実現される。なお、500℃程度までの昇温であれば、汚泥炭化物中の有機可燃成分の揮発消失は小さく抑えられる。なお、本発明のタール除去作業の間隔は、炉の運転形態(24時間連続運転か、昼間だけのバッチ式運転か)によって異なり、24時間連続運転の場合は、上記のように1日1回程度で良く、昼間だけの運転の場合には3日に1回程度でも良い。   On the other hand, the external heat chamber 11 is divided into a burner 7 in the first zone Z1 on the upstream side where the evaporation of water in the retort is active and the amount of heating is required, and in the second zone Z2 where the evaporation of water is relatively small. The combustion temperature control is accurately maintained at 410 to 450 ° C., preferably 420 to 430 ° C., respectively. Thereby, the retort internal temperature is maintained at 390 ° C. to 430 ° C., preferably 390 ° C. to 410 ° C., and volatilization loss of the organic combustible component in the carbonized sludge is suppressed. Here, in the present embodiment, the set temperature of the first zone Z1 and the second zone Z2 is temporarily once a day, from the above-mentioned 420 ° C. to 430 ° C., which is the temperature during normal operation, to, for example, about 600 ° C. temporarily. Increase and then return to the original temperature. Accordingly, the temperature in the retort 2 rises from about 400 ° C. to 470 ° C. to 500 ° C., and then returns to the original temperature again. This time is, for example, 20 minutes to 40 minutes. By temporarily raising the temperature in the retort 2 in this manner, the tar content adhering to the inner wall of the retort 2 is peeled off and discharged out of the retort 2 from the discharge port 16 together with the sludge carbide. Therefore, periodic tar scraping work becomes unnecessary, and the efficiency of the furnace operation is realized. If the temperature is raised to about 500 ° C., the volatilization and disappearance of the organic combustible component in the sludge carbide can be kept small. In addition, the interval of the tar removal work of the present invention differs depending on the operation mode of the furnace (whether it is a continuous operation for 24 hours or a batch operation for only daytime), and in the case of a continuous operation for 24 hours, once a day as described above. If it is only daytime driving, it may be about once every three days.

(第2実施形態)
本実施形態では図2に示すように、レトルト2の他端部26が位置させられた排出筒15のシュートに、スライド式扉71で開閉可能な空気導入口72を設ける。他の構成は第1実施形態と同様である。
(Second Embodiment)
In the present embodiment, as shown in FIG. 2, an air inlet 72 that can be opened and closed by a sliding door 71 is provided in the chute of the discharge cylinder 15 in which the other end portion 26 of the retort 2 is positioned. Other configurations are the same as those of the first embodiment.

このような構成において、操業中に適当間隔で10秒〜20秒間、上記空気導入口72を開けて、外部空気をレトルト2内へ送給する。こうすると、レトルト2内で発生している乾留ガスが燃焼を開始し、その燃焼熱によって一時的にレトルト内温度が480℃〜550℃に上昇する。これにより、レトルト2の内壁に付着したタール分が剥離して、汚泥炭化物とともに排出口16からレトルト2外へ排出される。本実施形態によっても、第1実施形態と同様の効果がある。なお、10秒〜20秒の短時間であるから、汚泥炭化物中の有機可燃成分の揮発消失は、処理される汚泥炭化物全体の限られた部分に抑えられる。   In such a configuration, the air inlet 72 is opened at an appropriate interval for 10 to 20 seconds during operation, and external air is fed into the retort 2. If it carries out like this, the dry distillation gas currently generate | occur | produced in the retort 2 will start combustion, and the temperature in a retort will rise temporarily to 480 degreeC-550 degreeC with the combustion heat. Thereby, the tar part adhering to the inner wall of the retort 2 peels off, and is discharged out of the retort 2 from the discharge port 16 together with the sludge carbide. This embodiment also has the same effect as the first embodiment. In addition, since it is a short time of 10 seconds-20 seconds, the volatilization loss of the organic combustible component in sludge carbide is suppressed to the limited part of the whole sludge carbide processed.

(第3実施形態)
第1実施形態と同様の構成で、レトルト2内へ供給する汚泥Mの含水率を通常操業時の値(例えば50%程度)から一時的に7%〜15%下げる。これにより、レトルト2内での水分蒸発量が減ってレトルト2内の温度が一時的に480℃〜550℃に上昇し、レトルト2の内壁に付着したタール分が剥離して汚泥炭化物とともに排出口16からレトルト2外へ排出される。これにより第1実施形態と同様の効果が得られる。この場合も、汚泥炭化物中の有機可燃成分の揮発消失は、処理される汚泥炭化物全体の限られた部分に抑えられる。
(Third embodiment)
With the same configuration as in the first embodiment, the moisture content of the sludge M supplied into the retort 2 is temporarily reduced by 7% to 15% from the value during normal operation (for example, about 50%). As a result, the amount of water evaporation in the retort 2 decreases and the temperature in the retort 2 temporarily rises to 480 ° C. to 550 ° C., and the tar content adhering to the inner wall of the retort 2 is peeled off and discharged together with sludge carbide. 16 is discharged out of the retort 2. Thereby, the same effect as the first embodiment can be obtained. Also in this case, the volatilization and disappearance of the organic combustible component in the sludge carbide is suppressed to a limited portion of the entire sludge carbide to be treated.

(他の実施形態)
なお、本発明のタール除去方法は、上記実施形態で示した構造の外熱式ロータリキルンに限られず、レトルトの筒壁全体に断熱材を敷設した、従来例で示した構造の外熱式ロータリキルンにも適用可能である。
(Other embodiments)
The tar removal method of the present invention is not limited to the externally heated rotary kiln having the structure shown in the above embodiment, and an externally heated rotary having the structure shown in the conventional example in which a heat insulating material is laid on the entire cylindrical wall of the retort. Applicable to kilns.

本発明の第1実施形態における、外熱式ロータリキルンの概略断面図である。It is a schematic sectional drawing of the external heating type rotary kiln in 1st Embodiment of this invention. 本発明の第2実施形態における、外熱式ロータリキルンの概略断面図である。It is a schematic sectional drawing of the external heating type rotary kiln in 2nd Embodiment of this invention. 従来の外熱式ロータリキルンの概略断面図である。It is a schematic sectional drawing of the conventional external heating type rotary kiln.

符号の説明Explanation of symbols

1…炉体、11…外熱室、18…通気口、2…レトルト、23…上流端部、25…一端部、26…他端部、4…ガス噴出管、7…バーナ、M…汚泥、Z1,Z2…ゾーン。 DESCRIPTION OF SYMBOLS 1 ... Furnace body, 11 ... External heat chamber, 18 ... Vent, 2 ... Retort, 23 ... Upstream end part, 25 ... One end part, 26 ... Other end part, 4 ... Gas ejection pipe, 7 ... Burner, M ... Sludge , Z1, Z2 ... zones.

Claims (4)

回転する筒状レトルト内へ被処理材を供給し、当該レトルトが収容される外熱室からの加熱によって被処理材を炭化するようにした外熱式ロータリキルンのタール除去方法であって、レトルト内の温度を有機可燃成分の揮発消失を抑制する通常操業温度を越えてタールの剥離に必要な温度まで一時的に上昇させることを特徴とする外熱式ロータリキルンのタール除去方法。 A tar removal method for an externally heated rotary kiln in which a material to be treated is supplied into a rotating cylindrical retort, and the material to be treated is carbonized by heating from an external heat chamber in which the retort is accommodated. A method for removing tar from an externally heated rotary kiln, characterized in that the temperature inside the chamber is temporarily raised to a temperature necessary for tar separation, exceeding a normal operating temperature at which volatilization of organic combustible components is suppressed. 前記レトルト内温度の上昇を、前記外熱室の室温を一時的に上昇させることにより行う請求項1に記載の外熱式ロータリキルンのタール除去方法。 The method for removing tar from an externally heated rotary kiln according to claim 1, wherein the temperature inside the retort is increased by temporarily increasing the room temperature of the external heat chamber. 前記レトルト内温度の上昇を、前記レトルト内に一時的に空気を吹き込むことにより行う請求項1に記載の外熱式ロータリキルンのタール除去方法。 The method for removing tar from an externally heated rotary kiln according to claim 1, wherein the temperature inside the retort is increased by temporarily blowing air into the retort. 前記レトルト内温度の上昇を、前記被処理材の含水率を一時的に低下させることにより行う請求項1に記載の外熱式ロータリキルンのタール除去方法。 The method for removing tar from an externally heated rotary kiln according to claim 1, wherein the temperature inside the retort is increased by temporarily reducing the moisture content of the material to be treated.
JP2006205236A 2006-07-27 2006-07-27 Tar removing method of external heating type rotary kiln Pending JP2008032299A (en)

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Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN104830359A (en) * 2015-05-06 2015-08-12 徐州曹氏化工机械制造有限公司 External heating type coal dry distillation rotary furnace
CN114686246A (en) * 2020-12-31 2022-07-01 湖南万容科技股份有限公司 Horizontal rotary furnace coke cleaning mechanism

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN104830359A (en) * 2015-05-06 2015-08-12 徐州曹氏化工机械制造有限公司 External heating type coal dry distillation rotary furnace
CN114686246A (en) * 2020-12-31 2022-07-01 湖南万容科技股份有限公司 Horizontal rotary furnace coke cleaning mechanism

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