JPH11244645A - Treatment of generated gas of waste drying apparatus - Google Patents

Treatment of generated gas of waste drying apparatus

Info

Publication number
JPH11244645A
JPH11244645A JP5373198A JP5373198A JPH11244645A JP H11244645 A JPH11244645 A JP H11244645A JP 5373198 A JP5373198 A JP 5373198A JP 5373198 A JP5373198 A JP 5373198A JP H11244645 A JPH11244645 A JP H11244645A
Authority
JP
Japan
Prior art keywords
gas
combustion
waste
generated
drying
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.)
Withdrawn
Application number
JP5373198A
Other languages
Japanese (ja)
Inventor
Katsuyuki Nakanishi
克之 中西
Masayuki Sumi
誠之 角
Tsuneo Aihara
恒雄 相原
Fumihiro Miyoshi
史洋 三好
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.)
JFE Steel Corp
Original Assignee
Kawasaki Steel Corp
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Kawasaki Steel Corp filed Critical Kawasaki Steel Corp
Priority to JP5373198A priority Critical patent/JPH11244645A/en
Publication of JPH11244645A publication Critical patent/JPH11244645A/en
Withdrawn legal-status Critical Current

Links

Classifications

    • 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
    • Y02EREDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
    • Y02E50/00Technologies for the production of fuel of non-fossil origin
    • Y02E50/30Fuel from waste, e.g. synthetic alcohol or diesel
    • 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
    • Y02W30/20Waste processing or separation

Landscapes

  • Incineration Of Waste (AREA)
  • Treating Waste Gases (AREA)
  • Processing Of Solid Wastes (AREA)
  • Heat Treatment Of Water, Waste Water Or Sewage (AREA)
  • Drying Of Gases (AREA)
  • Water Treatment By Sorption (AREA)

Abstract

PROBLEM TO BE SOLVED: To drastically reduce the consumption of kerosene necessary for deodorization and non-pollution without requiring deodorization equipment by kerosene by subjecting generated gas to gas-liquid sepn. and feeding the gas after the sepn. to the combustion chamber of a combustion device and the liquid into the waste combustion gas of the combustion device. SOLUTION: Waste 26 and vapor 28 of a heat source medium for drying are supplied to a drying apparatus 20 and the dried matter 27 of the waste 26 dried by heating is sent to the ensuing stage. In the combustion device 21, the waste combustion gas 35 generated by the combustion of the kerosene 34 is subjected to heat recovery by a waste heat boiler 22 and the generated vapor 28 is used as a heat source for drying. The waste 26 is used as a drain 29 after heating in the drying apparatus 20 and is circulated to the waste heat boiler 22. The generated gas 30 from the waste 26 in the drying apparatus 20 is cooled by cooling water 33 in a condenser 25 and is subjected to the gas-liquid sepn. The dry generated gas 32 after the sepn. is subjected to the deodorization and non-pollution in a combustion chamber of the combustion device 21. The separated condensed water 31 is injected and supplied as a cooling medium for diluting the combustion gas to the combustion chamber of the combustion device 21, by which the condensed water is subjected to the deodorization and non-pollution. The need for a deodorization furnace, or the like, using the kerosene is eliminated and the rationalization and cost reduction of the process are made possible.

Description

【発明の詳細な説明】DETAILED DESCRIPTION OF THE INVENTION

【0001】[0001]

【発明の属する技術分野】本発明は、廃棄物乾燥装置の
発生ガス処理方法に係るものである。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method for treating generated gas in a waste drying apparatus.

【0002】[0002]

【従来の技術】近年、廃棄物の処理技術に関し、 (1)都市ごみ焼却炉から排出されるダイオキシン類を
筆頭とする微量有害物質の排出基準の強化、また廃棄物
循環型社会の創出が求められている昨今の社会情勢の中
で導入の気運が高まっている都市ごみの固形燃料化施設 (2)新しい廃棄物の処理形態として、廃棄物の高カロ
リー化、及び品質安定化を目的とした都市ごみの乾燥フ
ラフ製造施設等の主要な工程である乾燥工程の最適化に
対する要求が日増しに高まっている。
2. Description of the Related Art In recent years, regarding waste treatment technology, (1) It has been required to strengthen emission standards for trace toxic substances such as dioxins emitted from municipal solid waste incinerators and to create a waste recycling society. Solid waste conversion facility for municipal solid waste, which has been increasing in the recent social situation (2) The purpose of new waste disposal is to increase the calories of waste and stabilize its quality The demand for optimizing the drying process, which is the main process of a dry fluff manufacturing facility for municipal solid waste, is increasing day by day.

【0003】特に、前記固形燃料製造の主要な工程であ
る廃棄物の乾燥工程では、乾燥用熱源、及び乾燥装置の
廃棄物から発生するガスの脱臭及び無害化処理用の熱源
として、灯油を使用する乾燥プロセスが従来より実用化
されてきた。図4は、これを示すフローシートである。
乾燥ドラム1に供給された廃棄物2は、灯油3を熱源と
した熱風炉4で加熱された熱媒体5によって加熱乾燥さ
れ、乾燥品6として乾燥ドラム1から排出される。廃棄
物2を乾燥させた熱媒体5は、サイクロン7を経て脱塵
された後に循環ファン8を経て、一部は熱風炉4に送入
され熱媒体5として循環使用される。残りは熱交換器9
で加熱された後、灯油3を熱源とした脱臭炉10に送入
され、800℃程度まで加熱され、脱臭無害化処理され
る。その後、熱交換器9において高温熱源として熱媒体
5と熱交換後、熱交換器11に送入され、燃焼用空気フ
ァン12から送入された燃焼用空気13と熱交換後、排
気ファン14を経て、煙突15から排出される。燃焼空
気13は熱風炉4、脱臭炉10の灯油バーナの燃焼用に
用いられる。
In particular, in the waste drying process, which is a main process of the solid fuel production, kerosene is used as a heat source for drying and a heat source for deodorizing and detoxifying gas generated from waste in a drying device. Drying processes have been put to practical use. FIG. 4 is a flow sheet showing this.
The waste 2 supplied to the drying drum 1 is heated and dried by a heating medium 5 heated by a hot blast stove 4 using kerosene 3 as a heat source, and is discharged from the drying drum 1 as a dried product 6. The heat medium 5 obtained by drying the waste 2 is dust-removed through the cyclone 7, passes through the circulation fan 8, and is partially sent to the hot blast stove 4 to be circulated and used as the heat medium 5. The rest is heat exchanger 9
After being heated in, it is sent to a deodorizing furnace 10 using kerosene 3 as a heat source, heated to about 800 ° C, and deodorized and made harmless. Then, after exchanging heat with the heat medium 5 as a high-temperature heat source in the heat exchanger 9, the heat is exchanged with the combustion air 13 sent from the combustion air fan 12 to the exhaust fan 14. After that, it is discharged from the chimney 15. The combustion air 13 is used for burning a kerosene burner of the hot blast stove 4 and the deodorization furnace 10.

【0004】また、近年ではこうした乾燥プロセスにお
ける乾燥熱源として、例えば特開平6−82023号公
報には廃棄物から製造した固形燃料を利用する技術も提
案されている。
[0004] In recent years, as a drying heat source in such a drying process, for example, Japanese Patent Application Laid-Open No. 6-82023 has proposed a technique using solid fuel produced from waste.

【0005】[0005]

【発明が解決しようとする課題】ところが、近年 (1)前記固形燃料製造設備の需要家側の省エネルギー
に対する要求 (2)地球温暖化対策の一環として化石燃料より排出さ
れるCO2 排出量削減に対する要求 等の周辺環境の変化により、廃棄物の固形燃料製造の各
工程の中でエネルギー消費量の最も多い乾燥工程の高効
率化が求められている。
However, in recent years, (1) the demand for energy saving on the consumer side of the solid fuel production equipment, and (2) the reduction of CO 2 emissions from fossil fuels as part of measures against global warming. Due to changes in the surrounding environment, such as demands, the efficiency of the drying process, which consumes the largest amount of energy, in each process of solid fuel production of waste is required.

【0006】そこで本発明は、廃棄物の固形燃料製造の
主要な工程である乾燥工程における廃棄物から発生する
ガスを脱臭及び無害化するための灯油による脱臭設備を
必要とせず、さらには前記発生ガスを脱臭及び無害化に
必要な灯油の使用量を大幅に削減することを目的とす
る。
Accordingly, the present invention does not require a deodorizing facility using kerosene for deodorizing and detoxifying gas generated from waste in a drying process which is a main process of producing solid fuel for waste, and furthermore, the above-mentioned generation is not required. The purpose is to significantly reduce the amount of kerosene used to deodorize and detoxify gas.

【0007】[0007]

【課題を解決するための手段】本発明は、上記目的を達
成するためになされたもので、次の技術手段を特徴とす
る。すなわち、燃焼装置から発生する燃焼排ガスを熱源
とする廃棄物乾燥装置の発生ガス処理方法において、発
生ガスを気液分離し、分離後の気体は前記燃焼装置の燃
焼室に供給し、分離後の液体は前記燃焼装置の燃焼排ガ
ス中へ送入することを特徴とする廃棄物乾燥装置の発生
ガス処理方法である。
SUMMARY OF THE INVENTION The present invention has been made to achieve the above object, and has the following technical means. That is, in the generated gas treatment method of the waste drying device using the combustion exhaust gas generated from the combustion device as a heat source, the generated gas is separated into gas and liquid, the separated gas is supplied to the combustion chamber of the combustion device, A method for treating a generated gas in a waste drying device, wherein the liquid is fed into the combustion exhaust gas of the combustion device.

【0008】この場合に前記分離後の液体は、前記燃焼
装置の燃焼排ガス中へ送入することに代えて水処理手段
で処理し排出することとしてもよく前記燃焼装置に流動
層燃焼炉を使用し、前記流動層に送入することとしても
よい。
In this case, the separated liquid may be treated and discharged by water treatment means instead of being sent into the combustion exhaust gas of the combustion device, and a fluidized bed combustion furnace may be used in the combustion device. Then, it may be sent to the fluidized bed.

【0009】[0009]

【発明の実施の形態】本発明は、灯油を燃料とする燃焼
装置の燃焼排ガスを廃熱ボイラで熱回収し、発生した蒸
気を乾燥用熱源とする廃棄物の乾燥方法において、廃棄
物から発生するガスを凝縮器、あるいはスクラバ等によ
り気液分離し、分離後の気体を燃焼装置の燃焼室に供給
し、脱臭及び無害化処理する。また分離後の液体(凝縮
水)は、 (1)燃焼装置の燃焼ガスの希釈冷却媒体として、燃焼
装置の燃焼排ガスに混入する。
DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a method for drying wastes by using a waste heat boiler to recover heat of combustion exhaust gas from a combustion device using kerosene as fuel, and using generated steam as a heat source for drying. The gas to be separated is separated into gas and liquid by a condenser or a scrubber, and the separated gas is supplied to a combustion chamber of a combustion device for deodorization and detoxification. Further, the liquid (condensed water) after separation is mixed with the combustion exhaust gas of the combustion device as a cooling medium for diluting the combustion gas of the combustion device.

【0010】(2)活性炭、活性汚泥処理等の水処理手
段で処理して脱臭及び無害化し、河川等へ放流する。 (3)燃焼装置を自家製固形燃料を燃料とした流動層燃
焼炉とした場合、流動層温度調節用冷却媒体として流動
層に投入する。 のいずれかにより、脱臭及び無害化処理する。
(2) Deodorize and detoxify by treating with water treatment means such as activated carbon and activated sludge, and discharge to rivers and the like. (3) When the combustion device is a fluidized bed combustion furnace using a self-made solid fuel as a fuel, it is charged into the fluidized bed as a cooling medium for controlling the fluidized bed temperature. Deodorization and detoxification treatment

【0011】図1は、本発明の第1の実施例を示してい
る。廃棄物の乾燥装置20には、廃棄物26が供給さ
れ、乾燥用熱源媒体として蒸気28が供給される。蒸気
28により加熱乾燥された廃棄物26は、乾燥品27と
して排出され、次の工程に送られる。次に、燃焼装置2
1には灯油34が供給され、発生した燃焼排ガス35は
廃熱ボイラ22で熱回収され、蒸気28を発生する。こ
の蒸気28は廃棄物26の乾燥用熱源として乾燥装置2
0に供給され、廃棄物26を加熱してドレン29とな
り、廃熱ボイラ22に循環される。廃熱ボイラ22を出
た燃焼排ガスは、集塵機23で脱塵され、煙突24を経
て排出される。
FIG. 1 shows a first embodiment of the present invention. The waste 26 is supplied to the waste drying device 20, and steam 28 is supplied as a heat source for drying. The waste 26 heated and dried by the steam 28 is discharged as a dried product 27 and sent to the next step. Next, the combustion device 2
1 is supplied with kerosene 34, and the generated combustion exhaust gas 35 is recovered by the waste heat boiler 22 to generate steam 28. The steam 28 is used as a heat source for drying the waste 26 by the drying device 2.
The waste 26 is heated to become a drain 29 by heating the waste 26 and circulated to the waste heat boiler 22. The flue gas discharged from the waste heat boiler 22 is removed by a dust collector 23 and discharged through a chimney 24.

【0012】また、乾燥装置20内で廃棄物から発生し
た発生ガス30は、凝縮器25で冷却水33により冷却
され気液分離される。気液分離された乾き発生ガス32
は、燃焼装置21の燃焼室に供給され、脱臭及び無害化
処理される。また気液分離された凝縮水31は、燃焼装
置21の燃焼室に燃焼ガスの希釈用冷却媒体として噴射
供給され、脱臭及び無害化処理される。
Further, the generated gas 30 generated from the waste in the drying device 20 is cooled by the cooling water 33 in the condenser 25 and separated into gas and liquid. Gas-liquid separated dry generated gas 32
Is supplied to the combustion chamber of the combustion device 21 to be deodorized and made harmless. The gas-liquid separated condensed water 31 is injected and supplied to a combustion chamber of the combustion device 21 as a cooling medium for diluting combustion gas, and is subjected to deodorization and detoxification processing.

【0013】ここで、乾燥装置20に供給される乾燥用
熱源としての蒸気供給については、前述のように固形燃
料製造装置内に燃焼装置、廃熱ボイラ等の蒸気発生装置
を設置し供給するのが一般的である。若し、本発明の対
象となる固形燃料製造装置に対し、固形燃料を主燃料源
とする火力発電所や蒸気を熱源として大量使用する各種
生産工場、又はコージェネレーション設備を有する高層
ビル等が隣接する場合、これらの蒸気発生装置から余剰
な低圧蒸気を受給することができれば、固形燃料製造装
置内の蒸気発生装置は不要となり、固形燃料製造装置の
建設コストを低減することができる。
Here, as for the supply of steam as a heat source for drying to be supplied to the drying device 20, as described above, a steam generating device such as a combustion device and a waste heat boiler is installed and supplied in the solid fuel production device. Is common. However, the solid fuel production equipment that is the object of the present invention is adjacent to a thermal power plant that uses solid fuel as a main fuel source, various production plants that use a large amount of steam as a heat source, or a high-rise building that has cogeneration equipment. In such a case, if excess low-pressure steam can be received from these steam generators, the steam generator in the solid fuel production device becomes unnecessary, and the construction cost of the solid fuel production device can be reduced.

【0014】図2は、本発明の第2の実施例であって、
符号20〜35は図1と同様である。図1の実施例と異
なる点は、気液分離した凝縮水31は、活性炭を使用し
た水処理装置36を介して処理され、脱臭及び無害化さ
れた後、河川等に放流される点である。図3は本発明の
第3の実施例であって、符号20〜35は図1と同様で
ある。図1と異なる点は、燃焼装置が固形燃料40を燃
料源とした流動層燃焼炉41であって、気液分離した凝
縮水31は、流動層温度調節用冷却媒体として、流動層
42に導入されている点である。このようにして、流動
層42の温度が適正に抑制される。
FIG. 2 shows a second embodiment of the present invention.
Reference numerals 20 to 35 are the same as those in FIG. The difference from the embodiment of FIG. 1 is that the condensed water 31 subjected to gas-liquid separation is treated via a water treatment device 36 using activated carbon, deodorized and rendered harmless, and then discharged to a river or the like. . FIG. 3 shows a third embodiment of the present invention. Reference numerals 20 to 35 are the same as those in FIG. The difference from FIG. 1 is that the combustion apparatus is a fluidized bed combustion furnace 41 using a solid fuel 40 as a fuel source, and the condensed water 31 subjected to gas-liquid separation is introduced into a fluidized bed 42 as a cooling medium for fluidized bed temperature control. That is the point. Thus, the temperature of the fluidized bed 42 is appropriately suppressed.

【0015】[0015]

【実施例】図1にフローを示す廃棄物乾燥装置を用いて
3トン/hの都市ごみ26(水分53%)の乾燥処理を
実施した。乾燥装置20は水蒸気28による間接加熱に
より廃棄物26を乾燥し、水分10%の乾燥品27を得
た。灯油34を熱風炉21で90リットル/h燃焼し、
発生したガスで、廃熱ボイラ22を用いて120℃の水
蒸気28を発生し、乾燥装置20へ熱供給した。乾燥装
置20で廃棄物より発生したガス(約2000Nm3
h)は凝縮器25で冷却され、気液分離した。分離した
乾き発生ガス32は廃棄物の臭気を含む臭気ガスである
が、熱風炉21の燃焼室へ投入することにより、高温の
燃焼ガスで臭気の元である微量な有機物は分解された。
また凝縮器25で凝縮した水分(約1.3t/h)は熱
風炉排ガスの流通経路中へ供給することにより、熱風炉
排ガスの温度調節に使用した。
EXAMPLE A 3 ton / h municipal waste 26 (53% moisture) was dried using a waste drying apparatus shown in the flow chart of FIG. The drying device 20 dries the waste 26 by indirect heating with steam 28 to obtain a dried product 27 having a water content of 10%. The kerosene 34 is burned in the hot stove 21 at 90 liters / h,
Using the generated gas, steam 28 at 120 ° C. was generated using the waste heat boiler 22, and heat was supplied to the drying device 20. Gas generated from waste in the drying device 20 (about 2000 Nm 3 /
h) was cooled in the condenser 25 and separated into gas and liquid. The separated dry generated gas 32 is an odor gas containing waste odor, but by being introduced into the combustion chamber of the hot blast stove 21, a trace amount of organic substances causing odor are decomposed by the high-temperature combustion gas.
The water condensed in the condenser 25 (about 1.3 t / h) was supplied into a hot-air stove exhaust gas flow path to be used for temperature control of the hot-air stove exhaust gas.

【0016】一方、図4にフローを示した従来法による
廃棄物乾燥処理においては、上記実施例と同様に3t/
hの都市ごみ2(水分53%)を乾燥ドラム1により乾
燥して水分10%の乾燥品6を得た。このとき乾燥ドラ
ム1からの発生ガスは熱風炉から供給した乾燥ガスと都
市ごみから発生した蒸気等との混合ガス(約13600
Nm3 /h)はその半量は熱風炉4に送られ500℃ま
で追い焚きされて再度乾燥ドラム1へ循環使用された。
この熱風炉4の追い焚きには灯油90リットル/hを使
用した。残りの半量は脱臭炉10により加熱処理されて
煙突15から放散されたが、この時脱臭炉10での加熱
処理のために灯油45リットル/hを使用した。すなわ
ち従来法では都市ごみ3t/hの乾燥処理にあたり、灯
油135リットル/hを必要とした。
On the other hand, in the waste drying treatment according to the conventional method shown in the flow chart of FIG.
h municipal solid waste 2 (water 53%) was dried by the drying drum 1 to obtain a dried product 6 having a water content of 10%. At this time, the gas generated from the drying drum 1 is a mixed gas of the dry gas supplied from the hot blast stove and steam generated from municipal solid waste (about 13600
The half of Nm 3 / h) was sent to the hot blast stove 4, reheated to 500 ° C., and circulated again to the drying drum 1.
For the reheating of the hot blast stove 4, kerosene 90 liter / h was used. The remaining half was heat-treated by the deodorizing furnace 10 and was emitted from the chimney 15. At this time, 45 liters / h of kerosene was used for the heat treatment in the deodorizing furnace 10. That is, in the conventional method, 135 l / h of kerosene was required for the drying treatment of the municipal waste at 3 t / h.

【0017】以上から本発明の利用により、3t/hの
都市ごみの乾燥処理にあたり、脱臭炉のおける灯油の使
用をなくすことができたことで、必要な灯油量を33%
低減することができた。
As described above, the use of the present invention has eliminated the use of kerosene in a deodorizing furnace in the drying treatment of 3 t / h of municipal solid waste.
Could be reduced.

【0018】[0018]

【発明の効果】本発明によれば、燃焼装置から発生する
燃焼排ガスを熱源として廃棄物を乾燥するにあたり、そ
の過程で廃棄物から発生した発生ガスを気液分離し、分
離後の気体は燃焼装置の燃焼室に供給することにより脱
臭及び無害化し、分離後の液体は燃焼装置の温度調節用
冷却媒体として燃焼装置に供給することにより脱臭及び
無害化するか、または水処理装置で処理して脱臭及び無
害化することとした。従って、従来の灯油の使用による
脱臭炉等は不要となり、工程の合理化とコスト低減に寄
与するところが大である。
According to the present invention, when drying wastes using flue gas generated from a combustion device as a heat source, gas generated from the wastes in the process is separated into gas and liquid, and the separated gas is burned. Deodorization and detoxification by supplying to the combustion chamber of the device, and the separated liquid is deodorized and detoxified by supplying to the combustion device as a cooling medium for controlling the temperature of the combustion device, or treated by a water treatment device. Deodorization and detoxification. Therefore, a conventional deodorizing furnace or the like by using kerosene is not required, which greatly contributes to streamlining of the process and cost reduction.

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

【図1】実施例のフローシートである。FIG. 1 is a flow sheet of an example.

【図2】実施例のフローシートである。FIG. 2 is a flow sheet of an example.

【図3】実施例のフローシートである。FIG. 3 is a flow sheet of an example.

【図4】従来例のフローシートである。FIG. 4 is a flow sheet of a conventional example.

【符号の説明】[Explanation of symbols]

1 乾燥ドラム 2 廃棄物 3 灯油 4 熱風炉 5 熱媒体 6 乾燥品 7 サイクロン 8 循環ファン 9 熱交換器 10 脱臭炉 11 熱交換器 12 燃焼空気ファン 13 燃焼空気 14 排気ファン 15 煙突 20 乾燥装置 21 燃焼装置 22 廃熱ボイラ 23 集塵機 24 煙突 25 凝縮器 26 廃棄物 27 乾燥品 28 蒸気 29 ドレン 30 乾燥排ガス 31 凝縮水 32 乾き発生ガス 33 冷却水 34 灯油 35 燃焼排ガス 36 水処理装置 40 固形燃料 41 流動層燃焼炉 42 流動層 DESCRIPTION OF SYMBOLS 1 Drying drum 2 Waste 3 Kerosene 4 Hot stove 5 Heat medium 6 Dry goods 7 Cyclone 8 Circulation fan 9 Heat exchanger 10 Deodorizing furnace 11 Heat exchanger 12 Combustion air fan 13 Combustion air 14 Exhaust fan 15 Chimney 20 Drying device 21 Combustion Apparatus 22 Waste heat boiler 23 Dust collector 24 Chimney 25 Condenser 26 Waste 27 Dry product 28 Steam 29 Drain 30 Dry exhaust gas 31 Condensed water 32 Dry generated gas 33 Cooling water 34 Kerosene 35 Combustion exhaust gas 36 Water treatment device 40 Solid fuel 41 Fluid bed Combustion furnace 42 Fluidized bed

───────────────────────────────────────────────────── フロントページの続き (51)Int.Cl.6 識別記号 FI C02F 1/28 F23G 5/14 ZABF F23G 5/04 ZAB 5/30 ZABD 5/14 ZAB B09B 3/00 303H 5/30 ZAB (72)発明者 相原 恒雄 東京都千代田区内幸町2丁目2番3号 川 崎製鉄株式会社内 (72)発明者 三好 史洋 東京都千代田区内幸町2丁目2番3号 川 崎製鉄株式会社内──────────────────────────────────────────────────続 き Continued on the front page (51) Int.Cl. 6 Identification code FI C02F 1/28 F23G 5/14 ZABF F23G 5/04 ZAB 5/30 ZABD 5/14 ZAB B09B 3/00 303H 5/30 ZAB ( 72) Inventor Tsuneo Aihara 2-3-2 Uchisaiwaicho, Chiyoda-ku, Tokyo Inside Kawasaki Steel Corporation (72) Inventor Fumihiro Miyoshi 2-3-2 Uchisaiwaicho, Chiyoda-ku, Tokyo Inside Kawasaki Steel Corporation

Claims (3)

【特許請求の範囲】[Claims] 【請求項1】 燃焼装置から発生する燃焼排ガスを熱源
とする廃棄物乾燥装置の発生ガス処理方法において、該
発生ガスを気液分離し、分離後の気体は前記燃焼装置の
燃焼室に供給し、分離後の液体は前記燃焼装置の燃焼排
ガス中へ送入することを特徴とする廃棄物乾燥装置の発
生ガス処理方法。
In a method for treating a generated gas of a waste drying device using a combustion exhaust gas generated from a combustion device as a heat source, the generated gas is separated into gas and liquid, and the separated gas is supplied to a combustion chamber of the combustion device. Wherein the separated liquid is sent into the flue gas of the combustion device.
【請求項2】 前記分離後の液体は前記燃焼装置の燃焼
排ガス中へ送入することに代えて水処理手段で処理し排
出することを特徴とする請求項1記載の廃棄物乾燥装置
の発生ガス処理方法。
2. The waste drying apparatus according to claim 1, wherein the separated liquid is treated and discharged by water treatment means instead of being sent into the combustion exhaust gas of the combustion apparatus. Gas treatment method.
【請求項3】 前記燃焼装置に流動層燃焼炉を使用し、
前記分離後の液体は前記燃焼装置の燃焼排ガス中へ送入
することに代えて前記流動層に送入することを特徴とす
る請求項1記載の廃棄物乾燥装置の発生ガス処理方法。
3. A fluidized bed combustion furnace is used for the combustion device,
The generated gas treatment method for a waste drying device according to claim 1, wherein the separated liquid is sent to the fluidized bed instead of being sent to the combustion exhaust gas of the combustion device.
JP5373198A 1998-03-05 1998-03-05 Treatment of generated gas of waste drying apparatus Withdrawn JPH11244645A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP5373198A JPH11244645A (en) 1998-03-05 1998-03-05 Treatment of generated gas of waste drying apparatus

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP5373198A JPH11244645A (en) 1998-03-05 1998-03-05 Treatment of generated gas of waste drying apparatus

Publications (1)

Publication Number Publication Date
JPH11244645A true JPH11244645A (en) 1999-09-14

Family

ID=12950986

Family Applications (1)

Application Number Title Priority Date Filing Date
JP5373198A Withdrawn JPH11244645A (en) 1998-03-05 1998-03-05 Treatment of generated gas of waste drying apparatus

Country Status (1)

Country Link
JP (1) JPH11244645A (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR20010064951A (en) * 1999-12-20 2001-07-11 강신탁 Removal method and device of bad gas with dry in a organic waste matter
KR101703870B1 (en) * 2016-02-16 2017-02-09 주식회사 동양보일러 System for removing highly concentrated bad smell and saving fuel for resource recovery plant

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR20010064951A (en) * 1999-12-20 2001-07-11 강신탁 Removal method and device of bad gas with dry in a organic waste matter
KR101703870B1 (en) * 2016-02-16 2017-02-09 주식회사 동양보일러 System for removing highly concentrated bad smell and saving fuel for resource recovery plant

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