JP2003279015A - Biomass thermally-decomposed gas combusting method - Google Patents

Biomass thermally-decomposed gas combusting method

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Publication number
JP2003279015A
JP2003279015A JP2002085554A JP2002085554A JP2003279015A JP 2003279015 A JP2003279015 A JP 2003279015A JP 2002085554 A JP2002085554 A JP 2002085554A JP 2002085554 A JP2002085554 A JP 2002085554A JP 2003279015 A JP2003279015 A JP 2003279015A
Authority
JP
Japan
Prior art keywords
gas
biomass
drying
pyrolysis
zone
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
JP2002085554A
Other languages
Japanese (ja)
Inventor
Takeshi Suzuki
鈴木  剛
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.)
Mitsui Engineering and Shipbuilding Co Ltd
Original Assignee
Mitsui Engineering and Shipbuilding Co Ltd
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 Mitsui Engineering and Shipbuilding Co Ltd filed Critical Mitsui Engineering and Shipbuilding Co Ltd
Priority to JP2002085554A priority Critical patent/JP2003279015A/en
Publication of JP2003279015A publication Critical patent/JP2003279015A/en
Pending legal-status Critical Current

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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
    • Y02E50/10Biofuels, e.g. bio-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
    • 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
    • Y02PCLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P20/00Technologies relating to chemical industry
    • Y02P20/10Process efficiency
    • 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
    • Y02W30/78Recycling of wood or furniture waste

Abstract

<P>PROBLEM TO BE SOLVED: To obtain a clean produced gas of high calorie by drying and thermally decomposing biomass of high wetness to be effectively utilized as a heat source for drying and thermally decomposing the biomass in a system, and to extract the char of little water content as a valuable resource. <P>SOLUTION: A drying furnace (drying zone) 2 and thermal decomposition furnaces (thermal-decomposition gasifying zone) 3a-3c located at the back of the drying furnace are mounted inside of a hot air furnace 1, a generated vapor passage 4 from the drying zone 1 and a produced gas passage 5 from the thermal decomposition gasifying zone 3 are separated from each other, and the produced gas passage 5 is connected to a combustion part 6 of the hot air furnace. By compensating the shortage of calories of a gas turbine waste gas by the thermally decomposed gas of high calorific power not diluted by the dry vapor as the hot air furnace heat source, the energy is saved on. The dried water content taken out from the drying zone is deodorized in the hot air furnace, and further the char of low water content is extracted as the valuable resource. <P>COPYRIGHT: (C)2004,JPO

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】本発明はバイオマス熱分解ガ
ス燃焼方法に係り、特に、高湿潤のバイオマス(例え
ば、木質系、汚泥、糞尿、食物残渣、食品廃棄物、籾
殻、ビールかす等の有機性廃棄物)の熱分解ガスの効率
的な燃焼技術に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a biomass pyrolysis gas combustion method, and more particularly to a highly moist biomass (for example, woody matter, sludge, manure, food residues, food waste, rice husks, beer residue, etc.). Waste) pyrolysis gas efficient combustion technology.

【0002】[0002]

【従来の技術】例えば家畜糞尿は、従来の野積みや海洋
投棄などによる環境悪化が顕在化してきたことにより、
家畜糞尿等の処理に関する規制や、また、食品残渣等は
食品廃棄物リサイクル法などの法整備がなされ、これら
バイオマスの適正処理が義務付けられつつある。
2. Description of the Related Art For example, livestock excrement has been exposed to environmental deterioration due to conventional field loading and ocean dumping.
Regulations on the treatment of livestock manure, etc., and the establishment of legislation such as the Food Waste Recycling Law for food residues, etc. are required to properly treat these biomasses.

【0003】従来、バイオマスを熱分解すると、熱分解
ガス、チャー、およびタールなどが発生することが知ら
れている。これらは、加熱に基づくガス化装置の操作温
度によって、それぞれの生成量や成分が異なる。
[0003] It has been conventionally known that pyrolysis of biomass produces pyrolysis gas, char, tar and the like. The amount and composition of each of these differ depending on the operating temperature of the gasifier based on heating.

【0004】この種の技術として、特開平10−330
760号公報に有機物の連続炭化装置が記載されてい
る。本例は、乾燥炉、炭火炉、脱臭ドラム、ホッパー、
およびスクリューフィーダ等で構成され、乾燥炉で発生
する蒸気はそのまま乾燥物と一緒になって炭化炉ヘ送給
され、炭化炉で生成するガスと混合されて低カロリーな
熱分解生成ガスとなり脱臭ドラムへ送られていた。
As a technique of this kind, Japanese Patent Laid-Open No. 10-330 is known.
Japanese Unexamined Patent Publication No. 760 describes a continuous carbonization device for organic substances. This example is a drying furnace, charcoal furnace, deodorizing drum, hopper,
The steam generated in the drying furnace is sent to the carbonization furnace together with the dry matter as it is, and mixed with the gas generated in the carbonization furnace to become a low-calorie pyrolysis product gas to become a deodorizing drum. Was sent to.

【0005】[0005]

【発明が解決しようとする課題】本発明者らは、上記熱
分解生成ガスの有効利用のために、高含水のバイオマス
を乾燥工程で一定時間乾燥させた後、熱分解工程で熱分
解してガスを生成し、このガスと乾燥工程で蒸発した蒸
気とが一緒になった熱分解ガスを、ガスタービンの排ガ
ス(廃熱温度は約500℃)と混合して、熱分解ガスに
よる助燃(約500℃をさらに昇温)を行なう技術を開
発した(特願2002−030815号参照)。
DISCLOSURE OF THE INVENTION In order to effectively utilize the above-mentioned pyrolysis product gas, the present inventors dry biomass having a high water content for a certain period of time in a drying step, and then pyrolyze it in the pyrolysis step. The pyrolysis gas that produces gas and combines this gas with the vapor evaporated in the drying process is mixed with the exhaust gas of the gas turbine (waste heat temperature is about 500 ° C.) to support combustion (about A technique for performing further heating at 500 ° C. has been developed (see Japanese Patent Application No. 2002-030815).

【0006】ところで、家畜糞尿(牛糞)を原料とした
場合、その組成は、C(52.4%)、H(7.1%)、
N(2.8%)、O(37.7%)となる。また、アッシ
ュはこれらの元素成分の16.9%、含水率88.3%で
ある。
By the way, when livestock manure (cow dung) is used as a raw material, its composition is C (52.4%), H (7.1%),
It becomes N (2.8%) and O (37.7%). Ash has 16.9% of these elemental components and a water content of 88.3%.

【0007】この組成(一般的な牛糞の場合の組成)で
の熱分解(外熱温度約800℃で加熱)後の熱分解ガス
の発熱量は、乾燥工程での蒸発水分が混在するため、極
めて低く、燃焼性に問題があった。
The calorific value of the thermal decomposition gas after thermal decomposition (heating at an external heat temperature of about 800 ° C.) in this composition (composition in the case of general cow dung) is due to the presence of water vapor evaporated in the drying process. It was extremely low and had a problem with flammability.

【0008】この蒸発水分が混在する従来の分解ガスの
組成(vol.比)および発熱量を次に示す。例えば一
般的な都市ガスの約9900kcalに比較しても、極
めて低カロリーであることがわかる。
The composition (vol. Ratio) and heat generation amount of the conventional decomposition gas in which this evaporated water is mixed are shown below. For example, it can be seen that the calorie content is extremely low even when compared with about 9900 kcal of general city gas.

【0009】可燃成分:0.02766 COおよびその他の非可燃分:0.0181 HO:0.95423 発熱量(LHV):237kcal/Nm Combustible components: 0.02766 CO 2 and other non-combustible components: 0.0181 H 2 O: 0.95423 Calorific value (LHV): 237 kcal / Nm 3

【0010】この問題の解決方法としては、乾燥蒸気の
混在する生成ガスをガス通路から取り出し、水洗浄して
過剰な水分を除去する手段があるが、熱損失を余儀なく
され得策ではない。
As a solution to this problem, there is a means for taking out the produced gas mixed with dry steam from the gas passage and washing it with water to remove excess water, but this is not a good idea because it causes heat loss.

【0011】本発明の目的は、高湿潤のバイオマスを乾
燥および熱分解して、高カロリーでかつクリーンな生成
ガスを得て、系内でバイオマス乾燥および熱分解の熱源
として有効利用するとともに、含水量の少ないチャーを
有価物として採取することである。
The object of the present invention is to dry and pyrolyze highly moist biomass to obtain a high calorie and clean product gas, which is effectively used as a heat source for biomass drying and pyrolysis in the system, and which is also included. It is to collect char with a small amount of water as a valuable resource.

【0012】[0012]

【課題を解決するための手段】上記目的は、バイオマス
を乾燥させる乾燥ゾーンと、該乾燥ゾーンで乾燥したバ
イオマスを熱分解して熱分解ガスおよびチャーを生成す
る熱分解ガス化ゾーンと、該乾燥ゾーンおよび該熱分解
ガス化ゾーンを加熱するための燃焼ガスを生成する熱風
炉とを備え、前記乾燥ゾーンからバイオマスの乾燥蒸気
を取り出して前記熱風炉に送給する乾燥蒸気通路と、前
記熱分解ガス化ゾーンから前記熱分解ガスを取り出して
前記熱風炉に供給する熱分解ガス通路とをそれぞれ別々
に配置し、前記熱分解ガスは前記熱風炉の燃焼部に供給
し、前記乾燥蒸気は前記熱風炉内の該燃焼部とは異なる
場所に送給して脱臭処理することを特徴とするバイオマ
ス熱分解ガス燃焼方法によって達成される。
[Means for Solving the Problems] The above objects are a drying zone for drying biomass, a pyrolysis gasification zone for pyrolyzing the biomass dried in the drying zone to produce pyrolysis gas and char, and the drying. A zone and a hot air stove that generates combustion gas for heating the pyrolysis gasification zone, a dry steam passage for taking out dry steam of biomass from the drying zone and feeding it to the hot air stove, and the pyrolysis The pyrolysis gas passages for taking out the pyrolysis gas from the gasification zone and supplying it to the hot blast stove are separately arranged, the pyrolysis gas is supplied to the combustion section of the hot blast stove, and the dry steam is the hot air blast. This is achieved by a biomass pyrolysis gas combustion method, which is characterized in that the biomass is fed to a place different from the combustion part to perform deodorizing treatment.

【0013】本発明によれば、バイオマスの乾燥ゾーン
で生成した蒸気を予め取り出し、この蒸気の混在しない
乾燥したバイオマスを熱分解ガス化ゾーンに送給するの
で、熱分解ガス化ゾーンで生成される熱分解ガスおよび
チャーは、乾燥ゾーンでの蒸発水分を含まないため、高
カロリーな燃料として有効利用できる。本発明では、こ
の熱分解ガスを、乾燥ゾーンおよび熱分解ガス化ゾーン
を加熱する熱風炉の熱源に利用した。さらに、乾燥ゾー
ンで別途取り出した乾燥蒸気は、熱風炉内の燃焼部とは
異なる後流側に供給して脱臭するようにした。
According to the present invention, the steam generated in the biomass drying zone is taken out in advance, and the dry biomass in which the steam is not mixed is fed to the pyrolysis gasification zone, so that it is generated in the pyrolysis gasification zone. Pyrolysis gas and char do not contain evaporated water in the drying zone, and can be effectively used as a high-calorie fuel. In the present invention, this pyrolysis gas was used as the heat source of the hot stove that heats the drying zone and the pyrolysis gasification zone. Further, the dry steam separately taken out in the drying zone was supplied to a wake side different from the combustion part in the hot air stove to deodorize.

【0014】さらに、熱風炉の熱源として、熱分解ガス
とともに外部燃料を供給することにより、安定した燃焼
を維持できる。また、ガスタービンもしくはガスエンジ
ンの排ガスを燃焼用空気として熱風炉ヘ送給することに
より、これら高効率熱機関の廃熱を有効利用できる。し
かも、熱分解ガス化ゾーンからは、バイオマス乾燥蒸気
を含まない高カロリーのチャーを有価物として取り出す
ことができる。
Further, stable combustion can be maintained by supplying the external fuel together with the pyrolysis gas as the heat source of the hot stove. Further, by sending the exhaust gas of the gas turbine or the gas engine to the hot stove as combustion air, the waste heat of these high efficiency heat engines can be effectively used. Moreover, high-calorie char containing no biomass dry steam can be taken out as valuables from the pyrolysis gasification zone.

【0015】図1に、バイオマスの熱分解の経時変化の
グラフを示す。15分までは急速な減量があるが、これ
はもっぱら乾燥ゾーンでの水蒸気の発生に伴うもので、
バイオマス重量の約70%が蒸発水分として低減し、そ
れを経過後、徐々に水蒸気に代わって可燃性ガスの発生
があることがわかる。
FIG. 1 is a graph showing the change over time in the thermal decomposition of biomass. There is a rapid weight loss up to 15 minutes, but this is mostly due to the generation of steam in the drying zone,
It can be seen that about 70% of the weight of biomass is reduced as evaporated water, and after passing through it, combustible gas is gradually generated instead of steam.

【0016】すなわち、上記グラフから乾燥ゾーンと熱
分解ゾーンとを区別し、乾燥ゾーンでの水蒸気を別途取
り出すことによって、熱分解ガス化ゾーンにおける生成
ガスの発熱量の低下を防止できることが示唆される。
That is, from the above graph, it is suggested that it is possible to prevent a decrease in the calorific value of the produced gas in the pyrolysis gasification zone by distinguishing the drying zone from the pyrolysis zone and taking out the steam in the drying zone separately. .

【0017】[0017]

【発明の実施の形態】本発明の実施形態の概要は、バイ
オマスの熱分解ガスを高カロリーな燃料として有効利用
し、同時に熱分解によって生成するチャーを有価物とし
て採取するため、予め乾燥ゾーンで発生する蒸発水分を
別途取りだし、後流側の熱分解ガス化ゾーンではこの乾
燥水分を含まないバイオマスを熱分解することによっ
て、含水量の極めて少ない熱分解ガスおよびチャーを生
成するようにしたものである。
BEST MODE FOR CARRYING OUT THE INVENTION The outline of the embodiment of the present invention is that the pyrolysis gas of biomass is effectively used as a high-calorie fuel, and at the same time, the char produced by the pyrolysis is collected as a valuable resource. Evaporated moisture generated is taken out separately, and in the pyrolysis gasification zone on the downstream side, the biomass that does not contain dry moisture is pyrolyzed to generate pyrolysis gas and char with extremely low water content. is there.

【0018】そして、この高カロリーな熱分解ガスを系
内の乾燥ゾーンおよび熱分解ガス化ゾーンを加熱する熱
風炉の熱源に有効利用し、乾燥ゾーンで取り出した乾燥
水分は熱風炉で脱臭するようにした。
The high-calorie pyrolysis gas is effectively used as a heat source for a hot-blast stove that heats the drying zone and the pyrolysis-gasification zone in the system, and the dry water taken out in the drying zone is deodorized in the hot-blast stove. I chose

【0019】図2は、本発明のバイオマス熱分解ガス燃
焼方法を採用した熱分解ガス化装置の一例を示す構成図
である。熱風炉1内に乾燥炉(乾燥ゾーン)2とその後
段に熱分解ガス化ゾーン3として加熱分解炉3a〜3c
が設置されている。
FIG. 2 is a constitutional view showing an example of a pyrolysis gasification apparatus adopting the biomass pyrolysis gas combustion method of the present invention. Drying furnace (drying zone) 2 in hot blast stove 1 and thermal decomposition furnaces 3a to 3c as pyrolysis gasification zone 3 in the subsequent stage.
Is installed.

【0020】熱風炉1内には仕切板11が設けられ、乾
燥炉1および加熱分解炉3a〜3cを外部から加熱する
ための燃焼ガス12の通路が形成される。燃焼ガス12
は、この通路を通りながら熱分解ガス化ゾーン3および
乾燥ゾーン2を順次外側から加熱した後、排出口13か
ら排出される。
A partition plate 11 is provided in the hot-air stove 1, and a passage for a combustion gas 12 for heating the drying furnace 1 and the thermal decomposition furnaces 3a to 3c from the outside is formed. Combustion gas 12
Is sequentially discharged from the outside through the pyrolysis gasification zone 3 and the drying zone 2 while passing through this passage, and then discharged from the discharge port 13.

【0021】本例では乾燥炉1からの発生蒸気通路4
と、加熱分解炉3a〜3bからの生成ガス(熱分解ガ
ス)通路5とを分離し、熱分解ガス通路5は熱風炉の燃
焼部6に接続してある。これにより、熱分解ガスは蒸気
で希釈されないため、発熱量を高く維持することが可能
で、燃焼が容易となった。
In this example, the steam generation passage 4 from the drying furnace 1
And the generated gas (pyrolysis gas) passage 5 from the thermal decomposition furnaces 3a to 3b are separated, and the pyrolysis gas passage 5 is connected to the combustion part 6 of the hot stove. As a result, since the pyrolysis gas is not diluted with steam, it is possible to maintain a high calorific value and facilitate combustion.

【0022】また、本例ではガスタービンの排ガス7を
利用して熱風炉の燃焼ガスを生成するが、バイオマスが
熱分解される熱分解温度は通常600〜800℃であ
る。これに対して、ガスタービン排ガス7は500℃程
度であるため、排ガス7の熱量だけでは熱分解温度まで
昇温できない。
In this example, the exhaust gas 7 of the gas turbine is used to generate the combustion gas in the hot stove, but the pyrolysis temperature at which the biomass is pyrolyzed is usually 600 to 800 ° C. On the other hand, since the gas turbine exhaust gas 7 has a temperature of about 500 ° C., it is not possible to raise the temperature to the thermal decomposition temperature only by the amount of heat of the exhaust gas 7.

【0023】そこで、ガスタービン排ガス7を加熱する
追焚バーナ8を設けることにより、排ガスの熱量不足を
補う。この場合、加熱分解炉で生成した乾燥水分の混在
しない高カロリーな生成ガスを燃焼してガスタービン排
ガスを熱分解温度に昇温させ、エネルギの節約を図って
いる。
Therefore, an additional heating burner 8 for heating the gas turbine exhaust gas 7 is provided to compensate for the insufficient heat quantity of the exhaust gas. In this case, energy is saved by burning a high-calorie generated gas that does not contain dry water generated in the thermal decomposition furnace to raise the temperature of the gas turbine exhaust gas to the thermal decomposition temperature.

【0024】また、熱風炉の追焚バーナ8に、灯油など
の化石燃料や都市ガス等の外部燃料を補完することによ
り、熱風炉の燃焼をさらに安定維持できる。なお、必要
に応じて熱風炉の燃焼を外部燃料のみで行ない、高カロ
リーの熱分解ガスを他の用途に有効利用することも可能
である。
Further, by supplementing the additional burner 8 of the hot stove with fossil fuel such as kerosene or external fuel such as city gas, the combustion of the hot stove can be further stably maintained. If necessary, it is possible to burn the hot stove using only the external fuel and effectively use the high-calorie pyrolysis gas for other purposes.

【0025】また、乾燥炉から別途取り出した乾燥蒸気
は、空気(本例ではガスタービン排ガス)と共に、熱風
炉内の熱分解ガス燃焼部6とは異なる場所(乾燥蒸気お
よび空気15として図示)に投入して脱臭する。さら
に、熱分解ガス化ゾーン3から排出されるチャー16
も、乾燥ゾーン2でバイオマスの乾燥水分が予め取り除
かれているので、含水量の低い高カロリーのチャーを有
価物として採取できる。
Further, the dry steam separately taken out from the drying furnace is placed together with the air (gas turbine exhaust gas in this example) in a place different from the pyrolysis gas combustion section 6 in the hot stove (shown as dry steam and air 15). Add to deodorize. Further, the char 16 discharged from the pyrolysis gasification zone 3
Also, since the dry water content of the biomass has been removed in advance in the drying zone 2, high-calorie char with a low water content can be collected as a valuable resource.

【0026】次に、ガスタービン廃熱を有効利用し、前
述のように生成ガスの高カロリー対策を施した本発明方
法と、他の燃料を用いた糞尿炭化処理とを、エネルギー
コスト原単位で比較すると下記の表1に示すとおりとな
る。
Next, the method of the present invention in which the waste heat of the gas turbine is effectively used and the measures against high calorie of the produced gas are taken as described above, and the manure carbonization treatment using other fuels are carried out in terms of energy cost unit The comparison results are shown in Table 1 below.

【0027】すなわち、灯油を燃料として牛糞を乾燥し
炭化する従来のケースをケース1とし、本発明によるガ
スタービン廃熱を利用して牛糞を乾燥し炭化するケース
をケース2として比較する。
That is, the conventional case in which cow dung is dried and carbonized by using kerosene as fuel is referred to as case 1, and the case in which cow dung is dried and carbonized by utilizing the gas turbine waste heat according to the present invention is compared as case 2.

【0028】従来のケース1ではリッター30円の灯油
を使用して、年間92,880千円、糞尿1トン当り
2,300円となる。一方、本発明によるケース2で
は、灯油の使用経費は年間100,253千円である
が、発電メリットとして1000kWガスタービン(稼
動時間8000hr)では、96,000千円(電力単
価12円/kWh)が償却され、結局、糞尿1トン当り
110円で処理できる。
In case 1 of the conventional case, kerosene of 30 liters is used, and the annual cost is 92,880,000 yen, and the cost is 2,300 yen per ton of manure. On the other hand, in case 2 according to the present invention, the cost of using kerosene is 100,253,000 yen per year, but as a merit of power generation, with a 1000 kW gas turbine (operating time 8000 hr), 96,000,000 yen (electric power unit price 12 yen / kWh) Is amortized, and after all 110 tons of manure can be processed for 110 yen.

【0029】[0029]

【表1】 [Table 1]

【0030】以上のように、本発明方法によりガスター
ビン廃熱を用いて加熱する熱分解炭化(チャー化)処理
システムが極めて優れていることがわかる。この際、有
価物はチャーであり、燃料ないし肥料代替等に有効利用
される。また、この処理装置における系外への排出物は
熱風炉の燃焼ガスのみであり、環境への負荷の低減とな
る。
As described above, it is understood that the pyrolysis carbonization (charification) treatment system for heating by using the waste heat of the gas turbine by the method of the present invention is extremely excellent. At this time, the valuable material is char, which is effectively used as a substitute for fuel or fertilizer. In addition, the discharge to the outside of the system in this processing apparatus is only the combustion gas of the hot stove, which reduces the load on the environment.

【0031】[0031]

【発明の効果】上述のとおり、本発明によれば、乾燥ゾ
ーンで発生する乾燥水分を予め取り除くことにより、乾
燥水分の混在しない高カロリーな熱分解ガスを生成で
き、これをバイオマスの乾燥および熱分解の熱源として
利用することにより、高効率なバイオマス熱分解ガス燃
焼方法が得られる。また、乾燥ゾーンで予め取り出した
乾燥蒸気は、熱風炉で脱臭処理するので、単純な構成で
極めて効率的な燃焼の維持と、生成蒸気の脱臭処理を実
施できる。
As described above, according to the present invention, by removing the dry water generated in the drying zone in advance, it is possible to generate a high-calorie pyrolysis gas in which the dry water is not mixed. By utilizing it as a heat source for decomposition, a highly efficient biomass pyrolysis gas combustion method can be obtained. Further, since the dry steam taken out in advance in the drying zone is deodorized by the hot-air stove, it is possible to maintain extremely efficient combustion and deodorize the generated steam with a simple structure.

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

【図1】本発明におけるバイオマスの熱分解の経時変化
を示すグラフである。
FIG. 1 is a graph showing the change over time in the thermal decomposition of biomass in the present invention.

【図2】本発明のバイオマス熱分解ガス燃焼方法の一構
成例を示す図である。
FIG. 2 is a diagram showing an example of the configuration of the biomass pyrolysis gas combustion method of the present invention.

【符号の説明】[Explanation of symbols]

1 熱風炉 2 乾燥炉(乾燥ゾーン) 3、3a、3b、3c 加熱分解炉(熱分解ガス化ゾー
ン) 4 蒸気通路 5 生成ガス(熱分解ガス)通路 6 燃焼部 7 ガスタービン排ガス 8 バーナ 10 バイオマス 11 仕切板 12 熱風炉燃焼ガス 15 乾燥蒸気および空気 16 チャー
DESCRIPTION OF SYMBOLS 1 Hot-blast stove 2 Drying furnace (drying zone) 3, 3a, 3b, 3c Thermal decomposition furnace (pyrolysis gasification zone) 4 Steam passage 5 Product gas (pyrolysis gas) passage 6 Combustion part 7 Gas turbine exhaust gas 8 Burner 10 Biomass 11 Partition Plate 12 Hot Stove Combustion Gas 15 Dry Steam and Air 16 Char

フロントページの続き (51)Int.Cl.7 識別記号 FI テーマコート゛(参考) C10J 3/00 C10J 3/00 A 4H012 F23G 5/04 F23G 5/04 J 5/16 5/16 B Fターム(参考) 3K061 AA18 AB02 AC02 AC12 AC17 BA04 CA01 CA07 3K065 AA18 AB02 AC02 AC12 AC17 BA04 CA12 3K078 AA04 BA10 CA07 4D004 AA02 AA04 AA12 BA03 BA04 CA24 CA42 CA48 CB36 CC02 4D059 AA01 AA05 AA07 BB03 BB18 CA10 CA16 CC01 CC03 DA47 DA57 4H012 HA03 JA03 JA06 JA09 JA11Front page continuation (51) Int.Cl. 7 Identification code FI theme code (reference) C10J 3/00 C10J 3/00 A 4H012 F23G 5/04 F23G 5/04 J 5/16 5/16 B F term (reference) ) 3K061 AA18 AB02 AC02 AC12 AC17 BA04 CA01 CA07 3K065 AA18 AB02 AC02 AC12 AC17 BA04 CA12 3K078 AA04 BA10 CA07 4D004 AA02 AA04 AA12 BA03 BA04 CA24 CA42 CA48 JA57 JA07 CA01 CA07 CA01 CA01 CA01 CA01 CA07 CA01 CA07 CA47 CA02 CA16 CA02 CA16 CA02 CA16 CA02 CA16 CA02 CA16 CA02 CA16 CA02 CA16 CA02 CA16 CA02 CA01 CA07 CA07 CA01 JA11

Claims (4)

【特許請求の範囲】[Claims] 【請求項1】 バイオマスを乾燥させる乾燥ゾーンと、
該乾燥ゾーンで乾燥したバイオマスを熱分解して熱分解
ガスおよびチャーを生成する熱分解ガス化ゾーンと、該
乾燥ゾーンおよび該熱分解ガス化ゾーンを加熱するため
の燃焼ガスを生成する熱風炉とを備え、前記乾燥ゾーン
からバイオマスの乾燥蒸気を取り出して前記熱風炉に送
給する乾燥蒸気通路と、前記熱分解ガス化ゾーンから前
記熱分解ガスを取り出して前記熱風炉に供給する熱分解
ガス通路とをそれぞれ別々に配置し、前記熱分解ガスは
前記熱風炉の燃焼部に供給し、前記乾燥蒸気は前記熱風
炉内の該燃焼部とは異なる場所に送給して脱臭処理する
ことを特徴とするバイオマス熱分解ガス燃焼方法。
1. A drying zone for drying biomass,
A pyrolysis gasification zone for pyrolyzing the biomass dried in the drying zone to produce pyrolysis gas and char, and a hot stove producing a combustion gas for heating the drying zone and the pyrolysis gasification zone. A dry steam passage for taking out dry steam of biomass from the drying zone and feeding it to the hot stove, and a pyrolysis gas passage for taking out the pyrolysis gas from the pyrolysis gasification zone and supplying it to the hot stove. And separately disposed, the pyrolysis gas is supplied to the combustion part of the hot stove, and the dry steam is sent to a place different from the combustion part in the hot stove to perform deodorizing treatment. And biomass pyrolysis gas combustion method.
【請求項2】 前記熱風炉へ、ガスタービンもしくはガ
スエンジンの排ガスを燃焼用空気として送給することを
特徴とする請求項1に記載のバイオマス熱分解ガス燃焼
方法。
2. The biomass pyrolysis gas combustion method according to claim 1, wherein exhaust gas from a gas turbine or a gas engine is fed to the hot stoves as combustion air.
【請求項3】 前記熱風炉の燃焼部に、外部燃料を供給
することを特徴とする請求項1〜2のうちいずれか1項
に記載のバイオマス熱分解ガス燃焼方法。
3. The biomass pyrolysis gas combustion method according to claim 1, wherein external fuel is supplied to the combustion section of the hot stove.
【請求項4】 前記熱分解ガス化ゾーンから、前記チャ
ーを有価物として取り出すことを特徴とする請求項1〜
3のうちいずれか1項に記載のバイオマス熱分解ガス燃
焼方法。
4. The char is taken out as valuables from the pyrolysis gasification zone.
3. The biomass pyrolysis gas combustion method according to any one of 3 above.
JP2002085554A 2002-03-26 2002-03-26 Biomass thermally-decomposed gas combusting method Pending JP2003279015A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
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Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP2002085554A JP2003279015A (en) 2002-03-26 2002-03-26 Biomass thermally-decomposed gas combusting method

Publications (1)

Publication Number Publication Date
JP2003279015A true JP2003279015A (en) 2003-10-02

Family

ID=29232476

Family Applications (1)

Application Number Title Priority Date Filing Date
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Country Status (1)

Country Link
JP (1) JP2003279015A (en)

Cited By (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2008506529A (en) * 2004-07-19 2008-03-06 アースリニュー・アイピー・ホールディングズ・リミテッド・ライアビリティ・カンパニー Method and apparatus for drying and heat treating materials
JP2011068824A (en) * 2009-09-28 2011-04-07 Maywa Co Ltd Carbonization facility for organic water-containing waste
CN105737390A (en) * 2016-03-11 2016-07-06 安徽新生力生物科技有限公司 Control device of biomass hot blast stove
CN105843153A (en) * 2016-03-11 2016-08-10 安徽新生力生物科技有限公司 Biomass hot blast stove control method
CN106196992A (en) * 2016-08-22 2016-12-07 北京神雾环境能源科技集团股份有限公司 The water vapour that refuse pyrolysis produces is used for the system and method for garbage drying after heating up
CN107388267A (en) * 2017-09-01 2017-11-24 嵊州市科灵机械有限公司 A kind of gasification furnace
CN109825319A (en) * 2019-01-31 2019-05-31 辽宁金和福农业科技股份有限公司 A kind of biomass carbon, gas intensive flue-cured tobacco complete set of equipments
CN110358558A (en) * 2019-07-12 2019-10-22 江苏常泓城市绿岛环保科技有限公司 The useless solid resource conversion processing system of environmental protection

Cited By (9)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2008506529A (en) * 2004-07-19 2008-03-06 アースリニュー・アイピー・ホールディングズ・リミテッド・ライアビリティ・カンパニー Method and apparatus for drying and heat treating materials
JP2011068824A (en) * 2009-09-28 2011-04-07 Maywa Co Ltd Carbonization facility for organic water-containing waste
CN105737390A (en) * 2016-03-11 2016-07-06 安徽新生力生物科技有限公司 Control device of biomass hot blast stove
CN105843153A (en) * 2016-03-11 2016-08-10 安徽新生力生物科技有限公司 Biomass hot blast stove control method
CN106196992A (en) * 2016-08-22 2016-12-07 北京神雾环境能源科技集团股份有限公司 The water vapour that refuse pyrolysis produces is used for the system and method for garbage drying after heating up
CN107388267A (en) * 2017-09-01 2017-11-24 嵊州市科灵机械有限公司 A kind of gasification furnace
CN107388267B (en) * 2017-09-01 2023-07-18 嵊州市科灵机械有限公司 Gasification furnace
CN109825319A (en) * 2019-01-31 2019-05-31 辽宁金和福农业科技股份有限公司 A kind of biomass carbon, gas intensive flue-cured tobacco complete set of equipments
CN110358558A (en) * 2019-07-12 2019-10-22 江苏常泓城市绿岛环保科技有限公司 The useless solid resource conversion processing system of environmental protection

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