JP2006071131A - Carbonizing device - Google Patents

Carbonizing device Download PDF

Info

Publication number
JP2006071131A
JP2006071131A JP2004252156A JP2004252156A JP2006071131A JP 2006071131 A JP2006071131 A JP 2006071131A JP 2004252156 A JP2004252156 A JP 2004252156A JP 2004252156 A JP2004252156 A JP 2004252156A JP 2006071131 A JP2006071131 A JP 2006071131A
Authority
JP
Japan
Prior art keywords
carbonization
furnace
heating
heat
sludge
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
Application number
JP2004252156A
Other languages
Japanese (ja)
Inventor
Keijiro Yasumura
恵二朗 安村
Koji Hayashi
幸司 林
Kyotaro Iyasu
巨太郎 居安
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.)
Toshiba Corp
Original Assignee
Toshiba 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
Application filed by Toshiba Corp filed Critical Toshiba Corp
Priority to JP2004252156A priority Critical patent/JP2006071131A/en
Publication of JP2006071131A publication Critical patent/JP2006071131A/en
Pending legal-status Critical Current

Links

Images

Landscapes

  • Incineration Of Waste (AREA)
  • Gasification And Melting Of Waste (AREA)
  • Treatment Of Sludge (AREA)
  • Coke Industry (AREA)

Abstract

<P>PROBLEM TO BE SOLVED: To provide a carbonizing device for giving effective carbonizing treatment while reducing heat loss by improving the utilizing efficiency of combustion heat. <P>SOLUTION: A heat exchanger 14 is provided in a heating combustion furnace 13 which supplies heat to a carbonizing furnace 12 and burns dry distilled gas E produced in the carbonizing furnace 12 following the carbonizing treatment. Heat medium B is heated and supplied via the heat exchanger 14 to a dryer 11. Thus, the utilizing efficiency of the combustion heat is improved to give effective carbonizing treatment while reducing the heat loss in the whole device. <P>COPYRIGHT: (C)2006,JPO&NCIPI

Description

本発明は、例えば、農業集落排水処理汚泥などを処理対象とし、その利用のための炭化を行う炭化装置に関する。   The present invention relates to a carbonization apparatus that treats, for example, agricultural settlement wastewater treatment sludge and performs carbonization for its use.

一般に、農業集落で生じる排水の処理汚泥は、重金属物質があまり含まれていないので、遠心脱水機で濃縮・脱水後、遠心薄膜乾燥機等により乾燥して、農地施肥や、コンポスト堆肥として農地還元等に利用されている。しかし、農地施肥やコンポスト堆肥は使用時期が偏っている為に、貯蔵中に汚泥の変質が生じたり、臭気が発生する等の問題が発生する。   In general, wastewater treatment sludge generated in agricultural villages does not contain much heavy metal substances, so it is concentrated and dehydrated with a centrifugal dehydrator and then dried with a centrifugal thin film dryer, etc., and then returned to agricultural land as compost compost or compost compost. Etc. are used. However, since farmland fertilization and compost compost are unevenly used, problems such as sludge alteration during storage and odor generation occur.

このため、近年は汚泥を炭化して土壌改良材として利用する試みがなされている。有機性廃棄物を炭化する方法は、これまでにも提案されている(例えば、特許文献1参照)。このような炭化方法において、汚泥を炭化するには乾燥機により汚泥を乾燥する前処理が必要となる。上記特許文献1の方法では、脱臭炉から排出される高温排気熱を利用して、熱交換器により熱媒体を加熱し、この熱媒体を乾燥炉の加熱手段に使用し、有機性廃棄物の乾燥処理を行っている。   For this reason, in recent years, attempts have been made to carbonize sludge and use it as a soil improvement material. A method of carbonizing organic waste has been proposed so far (see, for example, Patent Document 1). In such a carbonization method, in order to carbonize the sludge, a pretreatment for drying the sludge with a dryer is required. In the method of Patent Document 1, the high temperature exhaust heat discharged from the deodorization furnace is used to heat the heat medium with a heat exchanger, and this heat medium is used as a heating means of the drying furnace, A drying process is performed.

しかし、上述の方法では、熱交換器を脱臭炉の外部に設置している。 このため熱損失が大きく、熱交換の効率が低く、熱利用が不十分である。
特開平10−330760号公報
However, in the above-described method, the heat exchanger is installed outside the deodorizing furnace. For this reason, heat loss is large, heat exchange efficiency is low, and heat utilization is insufficient.
JP-A-10-330760

このように、これまでの技術では、燃焼熱の利用効率が低く、熱損失も大きいため、炭化処理を効率的に行うことが困難であった。   As described above, in the conventional techniques, it is difficult to efficiently perform the carbonization treatment because the utilization efficiency of the combustion heat is low and the heat loss is large.

本発明の目的は、燃焼熱の利用効率を高めることにより、熱損失を低減させ、効果的な炭化処理を行うことができる炭化装置を提供することにある。   The objective of this invention is providing the carbonization apparatus which can reduce heat loss and can perform an effective carbonization process by improving the utilization efficiency of combustion heat.

本発明の炭化装置は、濃縮汚泥を導入し、熱媒体による加熱により乾燥汚泥を得る乾燥機と、この乾燥汚泥を導入し、この乾燥汚泥を低酸素状態で加熱して炭化を行う炭化炉と、補助燃料を導入し、この補助燃料を初期燃焼させ、この燃焼ガスを前記炭化炉に供給し、この炭化炉で生じる乾留ガスを導入して燃料として燃焼させる加熱燃焼炉と、この加熱燃焼炉内に設けられ、その燃焼熱により前記乾燥機に供給される前記熱媒体を加熱する熱交換器とを備えたことを特徴とする。   The carbonization apparatus of the present invention includes a dryer that introduces concentrated sludge and obtains dried sludge by heating with a heat medium, and a carbonization furnace that introduces the dried sludge and heats the dried sludge in a low oxygen state to perform carbonization. A heating combustion furnace that introduces auxiliary fuel, initially burns the auxiliary fuel, supplies the combustion gas to the carbonization furnace, introduces dry distillation gas generated in the carbonization furnace, and burns it as fuel; and the heating combustion furnace And a heat exchanger that heats the heat medium supplied to the dryer by the combustion heat.

また、本発明では、乾燥機から生じる悪臭ガスを加熱燃焼炉内に導入し、加熱燃焼炉内の高温により、悪臭ガスを熱分解してもよい。   Further, in the present invention, malodorous gas generated from the dryer may be introduced into the heating combustion furnace, and the malodorous gas may be pyrolyzed at a high temperature in the heating combustion furnace.

また、本発明では、炭化炉を加熱した後の排ガスを、乾燥機への導入される脱水汚泥の予熱器に供給するように構成してもよい。   Moreover, in this invention, you may comprise so that the waste gas after heating a carbonization furnace may be supplied to the preheater of the dewatered sludge introduced into a dryer.

さらに、本発明では、乾燥機は熱媒体を加熱する予備ボイラーを有し、炭化炉及び加熱燃焼炉に対して単独運転可能としてもよい。   Further, in the present invention, the dryer may have a preliminary boiler for heating the heat medium, and may be operated independently for the carbonization furnace and the heating combustion furnace.

本発明によれば、炭化炉に熱供給を行と共に炭化炉で炭化処理に伴って生じる乾留ガスを燃焼させる加熱燃焼炉内に熱交換器を設け、この熱交換器により乾燥機に供給される熱媒体を加熱するようにしたので、燃焼熱の利用効率が向上し、装置全体における熱損失が少なく、効果的な炭化処理を行うことができる。   According to the present invention, a heat exchanger is provided in the heating and combustion furnace for supplying heat to the carbonization furnace and combusting the dry distillation gas generated by the carbonization process in the carbonization furnace, and the heat exchanger supplies the heat to the dryer. Since the heat medium is heated, the use efficiency of the combustion heat is improved, the heat loss in the entire apparatus is small, and an effective carbonization treatment can be performed.

以下、本発明による炭化装置の一実施の形態について図面を用いて詳細に説明する。   Hereinafter, an embodiment of a carbonization apparatus according to the present invention will be described in detail with reference to the drawings.

図1はこの実施の形態における炭化装置の全体構成を示している。11は汚泥の乾燥機で、例えば、遠心薄膜式乾燥機を用いる。この乾燥機11は、前段に設けられた図示しないデカンター方式の遠心脱水機で脱水処理した含水率85%程度の濃縮汚泥Hを導入し、これを円筒状の加熱筒の内壁に薄膜状に引き伸ばして乾燥させるもので、その処理能力は、含水率50%程度の乾燥汚泥Gを30〜40 kg/h製造する。   FIG. 1 shows the overall configuration of the carbonization apparatus in this embodiment. 11 is a sludge dryer, for example, a centrifugal thin film dryer. This dryer 11 introduces concentrated sludge H having a water content of about 85% dehydrated by a decanter-type centrifugal dehydrator (not shown) provided in the preceding stage, and stretches it into a thin film on the inner wall of a cylindrical heating cylinder. The processing capacity is 30 to 40 kg / h of dry sludge G having a water content of about 50%.

12は炭化炉で、乾燥汚泥Gを導入し、この乾燥汚泥Gを低酸素状態で加熱して炭化を行う。この炭化炉12としては、例えば、連続式の間接加熱ロ−タリキルン方式のものを用いる。この方式の炭化炉は、外周部分に加熱ジャケットが設けられたロータリキルンを有し、このロータリキルン内に供給された乾燥汚泥Gを加熱ジャケットからの熱により低酸素状態で加熱し、炭化させる。この炭化炉12の処理能力は、含水率50%程度の乾燥汚泥Gを20〜50 kg/hで炭化を行う。   12 is a carbonization furnace which introduce | transduces the dry sludge G and heats this dry sludge G in a low oxygen state, and carbonizes. As the carbonization furnace 12, for example, a continuous indirect heating rotary kiln type is used. This type of carbonization furnace has a rotary kiln provided with a heating jacket in the outer peripheral portion, and the dried sludge G supplied into the rotary kiln is heated and carbonized by heat from the heating jacket. The treatment capacity of the carbonization furnace 12 is to carbonize dry sludge G having a water content of about 50% at 20 to 50 kg / h.

13は加熱燃焼炉で、補助燃料のプロパンガスFや、汚泥炭化時に炭化炉12で発生する乾留ガスEを燃焼させて高温に保ち、その高温の燃焼ガスDを炭化炉12の加熱ジャケット内に供給し、この加熱ジャケットを介してロータリキルン内の乾燥汚泥を間接的に加熱し、炭化させる。すなわち、この加熱燃焼炉13は、補助燃料のプロパンガスFを導入して初期燃焼させ、高温の燃焼ガスDを前記炭化炉12に供給して加熱する。また、この炭化炉12での炭化処理に伴って生じる乾留ガス(主に炭化水素)Eを導入し、燃料として燃焼させ、高温状態を維持している。   Reference numeral 13 denotes a heating combustion furnace, which burns auxiliary fuel propane gas F and dry distillation gas E generated in the carbonization furnace 12 during carbonization of sludge and keeps it at a high temperature. The dried sludge in the rotary kiln is indirectly heated and carbonized through this heating jacket. That is, the heating and combustion furnace 13 introduces the propane gas F as an auxiliary fuel to cause initial combustion, supplies the high-temperature combustion gas D to the carbonization furnace 12 and heats it. In addition, dry distillation gas (mainly hydrocarbon) E generated along with the carbonization treatment in the carbonization furnace 12 is introduced and burned as fuel to maintain a high temperature state.

この加熱燃焼炉13には、乾燥機11から発生する悪臭ガスCが導入される。また、炭化炉12での炭化は低酸素状態で行われるため微量のダイオキシンが発生するが、このダイオキシンは乾留ガスEと共に加熱燃焼炉13内に導入される。加熱燃焼炉13は、これら悪臭ガスやダイオキシンを高温の燃焼熱により熱分解し、無害化する。   A malodorous gas C generated from the dryer 11 is introduced into the heating and combustion furnace 13. Further, since carbonization in the carbonization furnace 12 is performed in a low oxygen state, a small amount of dioxin is generated. This dioxin is introduced into the heating combustion furnace 13 together with the dry distillation gas E. The heating and combustion furnace 13 thermally decomposes these malodorous gases and dioxins with high-temperature combustion heat and renders them harmless.

14は熱交換器で、加熱燃焼炉13内に設けられ、その燃焼熱により、前記乾燥機11に供給される熱媒体Bを加熱する。ここで、熱媒体Bとしては、例えば、水蒸気を用いる。このために、熱交換器14には、水道水を軟水器で硬度を低下させた軟水Aがポンプで供給されており、この軟水Aを加熱燃焼炉13の燃焼熱により加熱して、熱媒体Bとしての水蒸気を発生させる。この水蒸気Bは、遠心薄膜乾燥機11の外周部に設けられた加熱ジャケットに供給され、内筒部の内周面に引き伸ばされる濃縮汚泥を加熱し乾燥させる。   A heat exchanger 14 is provided in the heating combustion furnace 13 and heats the heat medium B supplied to the dryer 11 with the combustion heat. Here, as the heat medium B, for example, water vapor is used. For this purpose, the heat exchanger 14 is supplied with soft water A whose tap water has been reduced in hardness by a water softener by means of a pump, and the soft water A is heated by the combustion heat of the heating combustion furnace 13 to produce a heat medium. Water vapor as B is generated. The water vapor B is supplied to a heating jacket provided on the outer peripheral portion of the centrifugal thin film dryer 11 to heat and dry the concentrated sludge stretched on the inner peripheral surface of the inner cylinder portion.

15は予熱器で、炭化炉12を加熱した排ガスを熱源として導入し、遠心薄膜乾燥機11に供給される濃縮汚泥Hを予熱する。   Reference numeral 15 denotes a preheater, which introduces exhaust gas that has heated the carbonization furnace 12 as a heat source, and preheats the concentrated sludge H supplied to the centrifugal thin film dryer 11.

次に、農業集落排水処理濃縮汚泥を例として、その乾燥処理と炭化を行う場合を説明する。この場合、先ず、加熱燃焼炉13に補助燃料のプロパンガスFを自動供給する。このプロパンガスFは図示しないバ−ナ−により点火・燃焼され、加熱燃焼炉13の温度を設定温度850℃に上昇させる。このときの燃焼ガスDを炭化炉12に供給して、炭化炉12内を昇温する。ここで、プロパンガスの供給量は4m/hであった。 Next, the case where the drying treatment and carbonization are performed will be described by taking the agricultural settlement drainage treatment concentrated sludge as an example. In this case, first, the auxiliary fuel propane gas F is automatically supplied to the heating combustion furnace 13. The propane gas F is ignited and burned by a burner (not shown), and the temperature of the heating combustion furnace 13 is raised to a set temperature of 850 ° C. The combustion gas D at this time is supplied to the carbonization furnace 12 to raise the temperature in the carbonization furnace 12. Here, the supply amount of propane gas was 4 m 3 / h.

燃焼ガスDは、上述のように炭化炉12に供給され、炭化炉12の温度を設定温度800℃に上昇させる。この場合、炭化炉12の温度が800℃に達するまで2時間要した。   The combustion gas D is supplied to the carbonization furnace 12 as described above, and raises the temperature of the carbonization furnace 12 to a set temperature of 800 ° C. In this case, it took 2 hours until the temperature of the carbonization furnace 12 reached 800 ° C.

一方、加熱燃焼炉13内の熱交換器14に軟水Aを15リットル/時間で供給し、加熱燃焼炉13内の燃焼熱により、175℃の水蒸気Bを熱媒体として発生させ、遠心薄膜乾燥機11に供給する。遠心薄膜乾燥機11には、前段において図示しないデカンター方式の遠心脱水機で脱水処理した濃縮汚泥H(含水率85%程度)が、予熱器15を経て90リットル/時間で供給されている。遠心薄膜乾燥機11は、この濃縮汚泥を熱媒体(水蒸気)Bにより加熱・乾燥し、乾燥汚泥G(含水率50%)を30kg/hで製造する。   On the other hand, soft water A is supplied to the heat exchanger 14 in the heating combustion furnace 13 at a rate of 15 liters / hour, steam 175 ° C. is generated as a heat medium by the combustion heat in the heating combustion furnace 13, and the centrifugal thin film dryer 11 is supplied. The centrifugal thin film dryer 11 is supplied with concentrated sludge H (water content of about 85%) dehydrated by a decanter type centrifugal dehydrator (not shown) in the previous stage through a preheater 15 at 90 liters / hour. The centrifugal thin film dryer 11 heats and dries this concentrated sludge with a heat medium (water vapor) B to produce a dried sludge G (water content 50%) at 30 kg / h.

この乾燥処理時に発生するアンモニア性の悪臭ガスCは、加熱燃焼炉13に通気し、850℃の高温により加熱分解して、脱臭した。   The ammoniacal malodorous gas C generated during the drying treatment was passed through the heating combustion furnace 13 and thermally decomposed at a high temperature of 850 ° C. to deodorize it.

この乾燥汚泥Gの製造を継続しながら、製造した乾燥汚泥Gを、設定温度800℃に温度上昇した炭化炉12に供給し、炭化を開始した。   While continuing the production of the dried sludge G, the produced dried sludge G was supplied to the carbonization furnace 12 whose temperature was increased to a set temperature of 800 ° C., and carbonization was started.

炭化条件は以下の通り。   Carbonization conditions are as follows.

・乾燥汚泥供給量 : 30(kg/h)
・炭化温度 : 800(℃)
・炭化時間 : 20(分)
・ロ−タリキルン回転数 : 5 (rpm)
炭化炉12に乾燥汚泥Gを供給開始してから10分経過後に、乾燥汚泥より乾留ガスEが発生した。この乾留ガスEは炭化水素を主成分としており、燃焼加熱炉12に供給され、燃料として燃焼させる。なお、炭化炉12内で発生したダイオキシンは、乾留ガスと共に加熱燃焼炉13内に導入され、加熱燃焼炉13内の高温(850℃)で熱分解する。
・ Dry sludge supply amount: 30 (kg / h)
-Carbonization temperature: 800 (° C)
Carbonization time: 20 (minutes)
・ Rotary kiln rotation speed: 5 (rpm)
After 10 minutes from the start of supplying the dried sludge G to the carbonization furnace 12, dry distillation gas E was generated from the dried sludge. The dry distillation gas E is mainly composed of hydrocarbons, and is supplied to the combustion heating furnace 12 to be burned as fuel. The dioxins generated in the carbonization furnace 12 are introduced into the heating combustion furnace 13 together with the dry distillation gas and thermally decomposed at a high temperature (850 ° C.) in the heating combustion furnace 13.

このようにして炭化炉12内に乾燥汚泥を5時間継続して供給し、乾燥汚泥150kgの炭化処理を行い、炭化物60kgを製造した。   Thus, dry sludge was continuously supplied into the carbonization furnace 12 for 5 hours, and 150 kg of dry sludge was carbonized to produce 60 kg of carbide.

上記炭化処理を行っている期間(5時間)に、遠心薄膜乾燥機11には450リットルの濃縮汚泥が供給され、乾燥汚泥150kgを継続して製造する。製造された乾燥汚泥Gは、同様に炭化炉12に供給され、炭化処理される。   During the carbonization process (5 hours), 450 liters of concentrated sludge is supplied to the centrifugal thin film dryer 11, and 150 kg of dried sludge is continuously produced. The produced dried sludge G is similarly supplied to the carbonization furnace 12 and carbonized.

このように、加熱燃焼炉13を補助燃料Fで初期燃焼させ、その燃焼ガスDを炭化炉12に供給して加熱し、汚泥の炭化を行わせ、炭化処理に伴って発生する乾留ガスを加熱燃焼炉13に導入して燃料として燃焼させる。また、熱交換器14を加熱燃焼炉13内に設け、その燃焼熱により直接的に加熱することにより効率よく加熱することができる。これらのことから、装置全体における燃焼熱の利用効率を高めることができ、熱損失を低減させ、効果的な炭化処理を行うことができる
なお、本発明は上記構成に限定されるものではなく、種々変形して実施してもよい。例えば、乾燥機11に図示しないが熱媒体Bを加熱する予備ボイラーを設け、炭化炉12及び加熱燃焼炉13に対して単独運転可能に構成してもよい。この場合、予備ボイラーとしては、灯油ボイラーを用い、熱媒体としての水蒸気を加熱する。すなわち、灯油ボイラーを燃焼運転して170℃の水蒸気を発生させ、遠心薄膜乾燥機11に供給する。遠心薄膜乾燥機11には、濃縮汚泥H(含水率85%)を90リットル/時間で供給し、乾燥汚泥G(含水率50%)を30kg/hで製造した。
In this manner, the heating combustion furnace 13 is initially burned with the auxiliary fuel F, the combustion gas D is supplied to the carbonization furnace 12 and heated, the sludge is carbonized, and the dry distillation gas generated with the carbonization treatment is heated. It introduces into the combustion furnace 13 and burns it as fuel. Moreover, it can heat efficiently by providing the heat exchanger 14 in the heating combustion furnace 13, and heating directly with the combustion heat. From these things, the utilization efficiency of the combustion heat in the whole apparatus can be improved, heat loss can be reduced, and an effective carbonization treatment can be performed.The present invention is not limited to the above configuration, Various modifications may be made. For example, although not shown, the dryer 11 may be provided with a preliminary boiler for heating the heat medium B so that the carbonization furnace 12 and the heating combustion furnace 13 can be operated independently. In this case, a kerosene boiler is used as a spare boiler, and water vapor as a heat medium is heated. That is, the kerosene boiler is burned to generate 170 ° C. water vapor and supplied to the centrifugal thin film dryer 11. Concentrated sludge H (water content 85%) was supplied to the centrifugal thin film dryer 11 at 90 liter / hour, and dry sludge G (water content 50%) was produced at 30 kg / h.

このようにして濃縮汚泥450リットルを遠心薄膜乾燥機11に連続5時間供給し、乾燥汚泥150kgを製造した。この乾燥処理に使用した灯油量は60リットルであった。製造した汚泥150kgは、前述と同様に炭化炉12に供給し、同条件で炭化処理しることで炭化物60kgを製造した。
このように、乾燥機11に予備ボイラーを設けて単独運転可能にすると、炭化炉12が点検などのために運転しない場合(この場合は加熱燃焼炉13も運転されない)でも、乾燥機11を独自に運転し、乾燥汚泥Gを製造しておくことができる。
In this way, 450 liters of concentrated sludge was supplied to the centrifugal thin film dryer 11 continuously for 5 hours to produce 150 kg of dried sludge. The amount of kerosene used for this drying treatment was 60 liters. 150 kg of the produced sludge was supplied to the carbonization furnace 12 in the same manner as described above, and carbonized under the same conditions to produce 60 kg of carbide.
As described above, when the dryer 11 is provided with a spare boiler so that it can be operated independently, even if the carbonization furnace 12 is not operated for inspection or the like (in this case, the heating combustion furnace 13 is not also operated), the dryer 11 is made uniquely The dried sludge G can be manufactured in advance.

本発明による炭化装置の一実施の形態を示す全体構成図である。It is a whole lineblock diagram showing one embodiment of a carbonization device by the present invention.

符号の説明Explanation of symbols

11 乾燥機
12 炭化炉
13 加熱燃焼装置
14 熱交換器
15 予熱器
A 軟水
B 熱媒体(水蒸気)
C 悪臭ガス
D 燃焼ガス
E 乾留ガス
F 補助燃料
G 乾燥汚泥
H 濃縮汚泥
DESCRIPTION OF SYMBOLS 11 Dryer 12 Carbonization furnace 13 Heating combustion apparatus 14 Heat exchanger 15 Preheater A Soft water B Heat medium (steam)
C Odor gas D Combustion gas E Distillation gas F Auxiliary fuel G Dry sludge H Concentrated sludge

Claims (4)

濃縮汚泥を導入し、熱媒体による加熱により乾燥汚泥を得る乾燥機と、
この乾燥汚泥を導入し、この乾燥汚泥を低酸素状態で加熱して炭化を行う炭化炉と、
補助燃料を導入し、この補助燃料を初期燃焼させ、この燃焼ガスを前記炭化炉に供給し、この炭化炉で生じる乾留ガスを導入して燃料として燃焼させる加熱燃焼炉と、
この加熱燃焼炉内に設けられ、その燃焼熱により前記乾燥機に供給される前記熱媒体を加熱する熱交換器と、
を備えたことを特徴とする炭化装置。
A dryer that introduces concentrated sludge and obtains dried sludge by heating with a heat medium;
A carbonization furnace for introducing the dry sludge and heating the dry sludge in a low oxygen state to perform carbonization;
A heating combustion furnace that introduces auxiliary fuel, initially burns the auxiliary fuel, supplies the combustion gas to the carbonization furnace, introduces dry distillation gas generated in the carbonization furnace, and burns it as fuel;
A heat exchanger that is provided in the heating combustion furnace and heats the heat medium supplied to the dryer by the combustion heat;
A carbonization apparatus comprising:
乾燥機から生じる悪臭ガスを加熱燃焼炉内に導入し、この悪臭ガスを熱分解することを特徴とする請求項1に記載の炭化装置。   The carbonization apparatus according to claim 1, wherein malodorous gas generated from the dryer is introduced into a heating combustion furnace, and the malodorous gas is thermally decomposed. 炭化炉を加熱した後の排ガスを、乾燥機へ導入される濃縮汚泥の予熱器に供給することを特徴とする請求項1に記載の炭化装置。   The carbonization apparatus according to claim 1, wherein the exhaust gas after heating the carbonization furnace is supplied to a preheater for concentrated sludge introduced into a dryer. 乾燥機は熱媒体を加熱する予備ボイラーを有し、炭化炉及び加熱燃焼炉に対して単独運転可能であることを特徴とする請求項1に記載の炭化装置。   The carbonization apparatus according to claim 1, wherein the dryer has a preliminary boiler for heating the heat medium, and can be operated independently for the carbonization furnace and the heating combustion furnace.
JP2004252156A 2004-08-31 2004-08-31 Carbonizing device Pending JP2006071131A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP2004252156A JP2006071131A (en) 2004-08-31 2004-08-31 Carbonizing device

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP2004252156A JP2006071131A (en) 2004-08-31 2004-08-31 Carbonizing device

Publications (1)

Publication Number Publication Date
JP2006071131A true JP2006071131A (en) 2006-03-16

Family

ID=36151957

Family Applications (1)

Application Number Title Priority Date Filing Date
JP2004252156A Pending JP2006071131A (en) 2004-08-31 2004-08-31 Carbonizing device

Country Status (1)

Country Link
JP (1) JP2006071131A (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2009091496A (en) * 2007-10-10 2009-04-30 Toshiba Corp Apparatus for converting sludge into fuel

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2009091496A (en) * 2007-10-10 2009-04-30 Toshiba Corp Apparatus for converting sludge into fuel

Similar Documents

Publication Publication Date Title
JP5148809B2 (en) Method and apparatus for converting sludge into fuel
JP3861093B2 (en) Method and apparatus for converting sludge into fuel
KR101945401B1 (en) Organic waste disposal device
JP2006348302A (en) Method and apparatus for converting sludge into fuel
JP2007302777A (en) Method and apparatus for carbonization treatment of highly hydrous organic matter
JP2008063362A (en) Method and apparatus for treating chlorine-containing organic waste
JP2006071131A (en) Carbonizing device
KR100856677B1 (en) Treatment apparatus of food rubbish
JP2007083217A (en) Method for dehydrating and carbonizing wet organic substance, and apparatus therefor
JP3506893B2 (en) Method for producing carbide from waste solid fuel
JP2004358371A (en) Processing method and processing system of watery organic waste
JP2005200522A (en) Method and system for carbonizing treatment of highly hydrous organic material and method for preventing white smoke
JP4231739B2 (en) Sludge recycling method
CN101125271A (en) Method for regenerating filtering absorbing material used for water treatment
JPH115100A (en) Sewage sludge treatment system
JP2004123992A (en) Carbonization treatment method and carbonization treatment system
JP6270206B2 (en) Organic waste processing apparatus and organic waste processing method
JP2002194362A (en) Method for carbonizing with overheated steam
JP2006224047A (en) Carbonization system of sewage sludge
KR20020005918A (en) Sludge dry system using waste tire pyrolysis device
JPH11323345A (en) Carbide preparation apparatus
JP2007238946A (en) Carbonization treatment apparatus for high water content organic material
JP3501925B2 (en) Method for producing carbide from waste solid fuel
JP5173263B2 (en) Solid fuel mainly composed of sewage sludge and its production equipment
JPH0224597B2 (en)