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JP2003268388A - Biomass pyrolysis method and apparatus - Google Patents

Biomass pyrolysis method and apparatus

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Publication number
JP2003268388A
JP2003268388A JP2002069027A JP2002069027A JP2003268388A JP 2003268388 A JP2003268388 A JP 2003268388A JP 2002069027 A JP2002069027 A JP 2002069027A JP 2002069027 A JP2002069027 A JP 2002069027A JP 2003268388 A JP2003268388 A JP 2003268388A
Authority
JP
Japan
Prior art keywords
biomass
pyrolysis
gas
reaction
gasification
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Withdrawn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
JP2002069027A
Other languages
Japanese (ja)
Inventor
Shigeru Hashimoto
茂 橋本
Takafumi Kawamura
隆文 河村
Haruyoshi Shioda
晴是 汐田
Atsushi Fujikawa
淳 藤川
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.)
Nippon Steel Corp
Original Assignee
Nippon 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 Nippon Steel Corp filed Critical Nippon Steel Corp
Priority to JP2002069027A priority Critical patent/JP2003268388A/en
Publication of JP2003268388A publication Critical patent/JP2003268388A/en
Withdrawn legal-status Critical Current

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Abstract

<P>PROBLEM TO BE SOLVED: To solve the problems that a large grinding installation is necessary for grinding biomass to a minute size sufficient for gasification since an excessively large quantity of energy is required for grinding it because of its properties, and that a huge reactor is necessary for effecting the reaction by using large particles of a biomass, both of which are unrealistic from an economical viewpoint. <P>SOLUTION: The reaction of decomposition of the biomass is performed in a jet layer, and the residence time is adjusted by the rising gas flow velocity, thus uniformalizing the degree of reaction of particles different in particle diameter. As a result, a method of thermal decomposition without using a grinding installation can be realized. An economical process can be realized by partitioning the ground material from one grinder according to the particle sizes so as to allow the use of the biomass suitable for each of thermal decomposition and gasification. <P>COPYRIGHT: (C)2003,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、高温ガス顕熱を利
用してバイオマスを急速に熱分解する技術に関するもの
である。
TECHNICAL FIELD The present invention relates to a technique for rapidly pyrolyzing biomass by utilizing sensible heat of high temperature gas.

【0002】[0002]

【従来の技術】地球温暖化問題への対応は、新エネルギ
−の開発・実用化、低二酸化炭素発生エネルギーへのシ
フト、原子力比率の向上、既存一次エネルギーの効率的
かつ合理的利用、未利用エネルギーや廃棄物エネルギー
の利用等で進められている。特にバイオマスはカーボン
ニュートラルであり、気候変動枠組条約締約国会議(C
OP3〜6、COP; The Conference
Of the Party)での国際公約を達成する
意味でも積極的に使用して石油、石炭等を代替すべき資
源であるといえる。バイオマスとは生物量の総称であ
り、FAO(国連食糧農業機関)によれば、農業系(麦
わら、サトウキビ、米糠、草木等)、林業系(製紙廃棄
物、製材廃材、除間伐材、薪炭林等)、畜産系(家畜廃
棄物)、水産系(水産加工残滓)、廃棄物系(生ゴミ、
RDF(ゴミ固形化燃料;Refused Deriv
ed Fuel)、庭木、建設廃材、下水汚泥)等に分
類される。
2. Description of the Related Art To deal with the problem of global warming, the development and practical application of new energy, the shift to low carbon dioxide generation energy, the improvement of the nuclear power ratio, the efficient and rational use of existing primary energy, and the unused energy It is being promoted by using energy and waste energy. In particular, biomass is carbon neutral, and the Conference of the Parties to the United Nations Framework Convention on Climate Change (C
OP3-6, COP; The Conference
It can be said that it is a resource that should be actively used to replace petroleum, coal, etc. in the sense of achieving international commitments under the Of Party. Biomass is a general term for biomass, and according to FAO (United Nations Food and Agriculture Organization), agricultural systems (straw straw, sugar cane, rice bran, vegetation, etc.), forestry systems (paper waste, lumber waste, thinned timber, firewood charcoal forest) Etc.), livestock system (livestock waste), fisheries system (results of marine product processing), waste system (raw garbage,
RDF (solid waste fuel; Refused Deriv)
ed Fuel), garden trees, construction waste, sewage sludge), etc.

【0003】バイオマスからのエネルギー回収、エネル
ギー転換を考えたとき、通常は燃焼による生成ガス顕熱
で蒸気を生成し、スチームタービンで電力として回収す
る効率の低い方法がとられる。これは、バイオマスは一
般に水分を多く含んでいるため熱量が低く、熱分解やガ
ス化に必要な熱が不足することにより、燃焼しか選択肢
がないためで、外部からの熱(他の燃料による熱補償)
がないと成り立たないプロセスが多い。従って、バイオ
マスからエネルギーを回収し、有効に利用するために
は、転換効率の高い方法が必須である。本発明と同じ手
法を用いた従来技術はないが、類似する技術の内、バイ
オマスのガスエネルギーへの転換技術として、近年にな
って、特開平11−302665号公報「バイオマスと
化石燃料を用いたガス化方法」に見られる、部分酸化プ
ロセスのバイオマスへの適用技術がある。
Considering energy recovery from biomass and energy conversion, a low efficiency method is usually used in which steam is generated by sensible heat of generated gas by combustion and is recovered as electric power by a steam turbine. This is because biomass generally contains a large amount of water and has a low amount of heat, and because the heat required for pyrolysis and gasification is insufficient, there is only a choice for combustion, and heat from the outside (heat from other fuels compensation)
There are many processes that cannot be achieved without it. Therefore, in order to recover energy from biomass and use it effectively, a method with high conversion efficiency is essential. Although there is no conventional technique using the same technique as the present invention, among the similar techniques, as a technique for converting biomass to gas energy, in recent years, Japanese Patent Laid-Open No. 11-302665 "using biomass and fossil fuels has been used. There is a technology of applying the partial oxidation process to biomass, which is seen in the "gasification method".

【0004】[0004]

【発明が解決しようとする課題】従来技術では、バイオ
マスを酸化剤で部分酸化(ガス化)する時、反応率を上
げるためにバイオマスを細かく粉砕する必要があった。
確立した分野である石炭(微粉炭)ガス化では50〜1
00μmの平均粒度まで粉砕されて使用されるが、バイ
オマスは強度、靱性に方向性(繊維方向が強い)があ
り、既存の粉砕機(ハンマー型、ミル型)では数mm未
満の粉砕物を製造するのに石炭の数倍以上の動力を必要
とする。従って、粉砕は経済的で現実的な数mmサイズ
とし、反応時間を稼ぐ方向で反応率を得る手法がとられ
るため、気流層が主体の部分ガス化では炉容の拡大、反
応率の低下につながり、設備コスト増加や効率悪化の一
因となっていた。
In the prior art, when biomass was partially oxidized (gasified) with an oxidizing agent, it was necessary to finely pulverize the biomass in order to increase the reaction rate.
Coal (pulverized coal) gasification, which is an established field, is 50 to 1
Used after being crushed to an average particle size of 00 μm, biomass has strength and toughness directionality (strong fiber direction), and existing crushers (hammer type, mill type) produce crushed products of less than a few mm. It requires several times more power than coal. Therefore, the method of pulverization is economical and realistic, with a size of several mm, and the method of obtaining the reaction rate in the direction of increasing the reaction time is used. Therefore, in the partial gasification mainly in the airflow layer, the furnace volume is expanded and the reaction rate is lowered. This was one of the causes of increased equipment costs and reduced efficiency.

【0005】そこで本発明では、熱分解をガス化顕熱で
行う方式を選択し、バイオマスに適した反応形態を用い
て、粗い粒子でも適用可能な、バイオマスの熱量を有効
に利用する方法を提供することを目的とする。
Therefore, the present invention provides a method of effectively utilizing the heat quantity of biomass, which is applicable to even coarse particles by selecting a method in which thermal decomposition is carried out by sensible heat of gasification and using a reaction mode suitable for biomass. The purpose is to do.

【0006】[0006]

【課題を解決するための手段】本発明は、以上の課題を
解決するに有効な方法であり、 1)バイオマスを熱分解原料とし、噴流層で熱分解反応
によってガス、タール及びチャーの生成物を得るバイオ
マス熱分解方法において、該熱分解反応の熱源として8
00℃以上の高温ガスを用いるバイオマス熱分解方法で
あって、熱分解部でのガスの上昇流速を1m/sec〜
15m/secとすることを特徴とする、バイオマス熱
分解方法、 2)バイオマスをガス化原料とし、酸素、あるいは酸素
と水蒸気でガス化して得られるガスを熱分解反応の熱源
として使用するに際し、粉砕したバイオマスを篩い分
け、細かい粒度のバイオマスをガス化原料として、また
粗い粒度のバイオマスを熱分解原料として使用すること
を特徴とする、1)記載のバイオマス熱分解方法、 3)ガス化炉と、熱分解部と、該ガス化炉と該熱分解部
を連接する接続部と、バイオマス粉砕機と、該バイオマ
ス粉砕機での粉砕物を篩い分けする篩い分け装置と、篩
い分けされた篩上粒子を熱分解部に、篩下粒子をガス化
炉に供給する供給装置を備えたバイオマス熱分解装置、
からなる。
The present invention is an effective method for solving the above problems. 1) The products of gas, tar and char are produced by a pyrolysis reaction in a spouted bed using biomass as a pyrolysis raw material. In the method for the thermal decomposition of biomass, the heat source for the thermal decomposition reaction is 8
A biomass pyrolysis method using a high-temperature gas of 00 ° C or higher, wherein the rising velocity of gas in the pyrolysis unit is 1 m / sec to
Biomass pyrolysis method, characterized in that it is set to 15 m / sec, 2) When biomass is used as a gasification raw material and oxygen or a gas obtained by gasification with oxygen and steam is used as a heat source for a pyrolysis reaction, pulverization 1) The biomass pyrolysis method described in 1), 3) a gasification furnace, characterized in that the biomass having a small particle size is used as a gasification raw material, and the biomass having a coarse particle size is used as a pyrolysis raw material. Pyrolysis part, connection part connecting the gasification furnace and the pyrolysis part, a biomass crusher, a sieving device for sieving pulverized products in the biomass crusher, and sieved on-screen particles In the pyrolysis part, a biomass pyrolysis device equipped with a supply device for supplying the undersize particles to the gasification furnace,
Consists of.

【0007】[0007]

【発明の実施の形態】本明細書において、バイオマスに
ついての定義は上記FAOの定義に準ずる。また、バイ
オマスを熱分解した際に生成する生成物の内、固形分を
チャー(バイオマスチャー)、常温で液体となる成分を
タールとする。噴流層とは、上昇ガス流中に固体が存在
する固気混合層であって、ガスの流れによる推進力(抵
抗)と重力とのバランスで粒子の循環滞留部ができる層
である。比重の重い粒子ほど循環部への滞在時間が長く
なる。噴流層の噴き出し口あたりの一般的なプロファイ
ルは、上昇ガスの噴き出し口面積が噴流層部面積より小
さくなっており、中心部では高速のガス・粒子上昇流
が、周辺部(壁面近傍)では逆に下降流が生じ、粒子は
循環、滞留する。
BEST MODE FOR CARRYING OUT THE INVENTION In the present specification, the definition of biomass follows the definition of FAO. In addition, among the products generated when pyrolyzing biomass, the solid content is char (biomass char), and the component that becomes liquid at room temperature is tar. The spouted bed is a solid-gas mixture layer in which solids are present in the ascending gas flow, and is a layer in which particles are circulated and accumulated due to the balance between the propulsive force (resistance) due to the gas flow and gravity. Particles with a higher specific gravity have a longer residence time in the circulation part. The general profile of the spouted bed outlet is that the rising gas outlet area is smaller than the spouted bed area, and high-speed gas / particle upward flow in the center part is opposite in the peripheral part (near the wall surface). A downward flow occurs in the particles, and the particles circulate and accumulate.

【0008】つぎに、図面を参照しながら、本発明の実
施態様を説明する。すなわち、図1に示すように、バイ
オマスの熱分解部1には、熱分解部バイオマス供給装置
2により、バイオマス3が供給される。供給されたバイ
オマス3は、ガス化炉8より接続部4を経て供給される
800℃以上の高温ガス5により、急速に昇温され、熱
分解される。高温ガス5の温度範囲に関しては、800
℃未満の場合、熱分解に必要なガス顕熱が不足する。熱
分解に必要なガス顕熱としては、熱分解反応部として4
00℃以上を目安とできる。また高温ガスの温度上限は
特に規定するものではなく、高温による設備的制約(炉
材等)を考慮して適宜設定すれば良い。但し、炉温が高
いほど増大する放散熱や、高温ほど流動性が増す炉壁成
分の安定性の観点から、1700℃以下が良く、好まし
くは1600℃以下としたい。
Next, an embodiment of the present invention will be described with reference to the drawings. That is, as shown in FIG. 1, the thermal decomposition part 1 of biomass is supplied with the biomass 3 by the thermal decomposition part biomass supply device 2. The supplied biomass 3 is rapidly heated and thermally decomposed by the high temperature gas 5 of 800 ° C. or higher supplied from the gasification furnace 8 through the connecting portion 4. For the temperature range of the hot gas 5, 800
When the temperature is lower than ℃, the sensible heat of gas required for thermal decomposition is insufficient. As the sensible heat of gas required for the thermal decomposition, 4
A temperature of 00 ° C or higher can be used as a guide. Further, the temperature upper limit of the high temperature gas is not particularly specified, and may be set appropriately in consideration of facility restrictions (furnace material etc.) due to high temperature. However, from the viewpoint of the radiated heat that increases as the furnace temperature rises and the stability of the furnace wall component that increases the fluidity as the temperature rises, 1700 ° C. or lower is preferable, and 1600 ° C. or lower is preferable.

【0009】熱分解部1の下部構造は、噴流層6形成の
ため一般的に傾斜をもったテーパー部7となっており、
中心には高温ガス5による上昇流が、壁面近傍にはガス
下降流9が存在する。テーパー部7より下流(後段側)
の熱分解部1では、高温ガス量、熱分解生成ガス量、雰
囲気温度・圧力で決まる上昇流速で生成ガスが後段に運
ばれる。本発明で言う上昇流速とは、熱分解反応器での
ガスの実流速を言い、ガスの流量(標準状態)を、ガス
温度、雰囲気圧力で補正し、流路断面積で除した数値
(この場合、熱分解部断面積)である。反応器の形状が
複雑である場合は、接続部4に近く、最も流速が遅くな
る(流路断面積が大きくなる)部分での流速を上昇流速
として使用する。これは、熱分解反応自体が短時間の反
応であるため、高温ガスとの接触地点に近い(すなわち
温度が高く反応速度が速い)場所での反応が全体の反応
を代表するためである。
The lower structure of the thermal decomposition part 1 is a tapered part 7 which is generally inclined due to the formation of the spouted bed 6,
An ascending flow of the hot gas 5 exists in the center, and a gas descending flow 9 exists near the wall surface. Downstream from the taper part 7 (post-stage side)
In the thermal decomposition section 1, the generated gas is conveyed to the subsequent stage at an ascending flow rate determined by the amount of high temperature gas, the amount of thermally decomposed product gas, and the ambient temperature / pressure. The rising flow velocity referred to in the present invention refers to the actual flow velocity of gas in the pyrolysis reactor, and is a numerical value obtained by correcting the gas flow rate (standard state) with the gas temperature and atmospheric pressure and dividing by the flow passage cross-sectional area (this In the case of the thermal decomposition section). When the shape of the reactor is complicated, the flow velocity at the portion near the connection portion 4 where the flow velocity is the slowest (the flow passage cross-sectional area is large) is used as the rising flow velocity. This is because the thermal decomposition reaction itself is a short-time reaction, and therefore the reaction in the place near the contact point with the high temperature gas (that is, the temperature is high and the reaction rate is fast) represents the entire reaction.

【0010】図1のように、熱分解部1が直管の場合
で、内部温度変化が小さい場合は、熱分解部後段で計測
したガス量を直管部断面積で割るというような、計測、
計算の容易な平均流速を用いても良い。バイオマス粒子
は、投入直後は、ガス上昇速度、反応器形状、粒子形状
・性状により、噴流層6で循環滞留するが、時間がたつ
につれ反応して粒径、密度が減少することで上昇ガスに
よる推進力が相対的に大きくなって、バイオマス粒子が
後段に排出される。その条件は、概略で球状粒子での終
末沈降速度の考えが適用でき、上昇ガス流起因の推進力
(抵抗)が重力を上回ることであるが、粒子形態、内部
細孔量(密度に影響)、反応の進行形態、粒子位置等に
よって大きく変わるため、計算では一義的に決まりにく
い。
As shown in FIG. 1, when the pyrolysis unit 1 is a straight pipe and the internal temperature change is small, the amount of gas measured at the latter stage of the pyrolysis unit is divided by the cross-sectional area of the straight pipe. ,
An average flow velocity that is easy to calculate may be used. Immediately after being charged, the biomass particles circulate and stay in the spouted bed 6 due to the gas rising speed, reactor shape, particle shape / property, etc. However, due to reaction, the particle size and density decrease over time, which causes the rising gas. The driving force becomes relatively large, and the biomass particles are discharged to the latter stage. The condition is that the concept of terminal sedimentation velocity in spherical particles can be roughly applied, and the propulsive force (resistance) due to rising gas flow exceeds gravity, but particle morphology, internal pore volume (affecting density) Since it greatly changes depending on the reaction progress mode, particle position, etc., it is difficult to uniquely determine by calculation.

【0011】本発明では、実験から得られた、原料粒度
によらず反応が充分に進行する流速条件を規定した。具
体的な流速条件は、上昇流速で1〜15m/secであ
る。1m/sec未満の場合にはバイオマスの炉内滞留
量が増加するため、単位体積あたりのバイオマス密度が
増加し、伝熱や反応生成ガスの流通が阻害されたり、噴
流層6での圧力損失が増えて操業不安定になることから
好ましくない。また15m/secを越えた場合は、大
きい粒子しか滞留できなくなり、反応不足で短時間で後
段に排出される粒子が増え、反応率が落ちてしまう。上
記条件の中でも、2〜10m/secが、熱分解が充分
に進み、しかも操業が安定する流速条件であるため、さ
らに好ましい。
In the present invention, the flow rate condition, which is obtained from the experiment and allows the reaction to proceed sufficiently regardless of the particle size of the raw material, is defined. A specific flow velocity condition is an ascending flow velocity of 1 to 15 m / sec. If it is less than 1 m / sec, the amount of biomass retained in the furnace increases, so that the biomass density per unit volume increases, heat transfer and flow of reaction product gas are hindered, and pressure loss in the spouted bed 6 is reduced. It is not preferable because it increases and the operation becomes unstable. Further, when it exceeds 15 m / sec, only large particles can be retained, and due to insufficient reaction, the number of particles discharged to the subsequent stage increases in a short time and the reaction rate decreases. Of the above conditions, 2 to 10 m / sec is more preferable because it is a flow rate condition at which thermal decomposition sufficiently progresses and the operation is stable.

【0012】また、バイオマスをガス化原料とし、酸
素、あるいは酸素と水蒸気でガス化して得られるガスを
熱分解反応の熱源として使用する場合を図1に示す。す
なわち、ガス化と熱分解を組み合わせた場合を示す。こ
のケースでは、バイオマスの熱分解部1には、熱分解部
バイオマス供給装置2により、バイオマス3が供給され
る。供給されたバイオマス3は、接続部4からの800
℃〜1700℃の高温ガス5により、急速に昇温され、
熱分解される。ガス化温度範囲(すなわち高温ガス5の
温度)に関しては、800℃未満の場合、熱分解に必要
なガス顕熱の不足や、ガス化反応速度の低下による未燃
物発生等で全体の効率が低下する。また1700℃を越
えた場合、高温による設備的制約(炉材等)や、大量の
スス生成によるガス化反応率低下が起こる。
FIG. 1 shows a case where biomass is used as a gasification raw material and oxygen or a gas obtained by gasifying with oxygen and steam is used as a heat source for a thermal decomposition reaction. That is, the case where gasification and thermal decomposition are combined is shown. In this case, the biomass 3 is supplied to the biomass pyrolysis unit 1 by the pyrolysis unit biomass supply device 2. The supplied biomass 3 is 800 from the connection part 4.
The temperature is rapidly raised by the high temperature gas 5 of ℃ ~ 1700 ℃,
Pyrolyzed. Regarding the gasification temperature range (that is, the temperature of the high-temperature gas 5), when the temperature is less than 800 ° C, the overall efficiency is low due to insufficient sensible heat of gas required for thermal decomposition and generation of unburned materials due to a decrease in gasification reaction rate descend. Further, when the temperature exceeds 1700 ° C., facility restrictions due to high temperatures (furnace materials, etc.) and a decrease in the gasification reaction rate due to the formation of a large amount of soot occur.

【0013】現在、バイオマス粉砕においては、経済
的、実用的には数mm程度の粒径が粉砕限度である。粉
砕方法としては、衝撃型(ハンマー型、棒型等)、切断
型(回転羽裁断型、スクリュー羽型等)、臼型ミル等あ
るが、10mm以上のサイズの破砕にはハンマー型が、
10mm未満のサイズの破砕にはハンマー型+棒型や切
断型が主として使用される。さらに2mm程度までの粉
砕には、切断型を主とした設備構成がとられるが、必要
動力が大きいため、処理能力は小さい。本来、熱分解反
応を短時間で充分に行わせるには、粒子径は小さければ
小さいほど良い(ここでの粒子径は、反応の観点から、
短径を指すこととする)。本発明とは異なる代表的な系
である気流層タイプの炉で一般的な数秒の熱分解反応時
間で反応するには、バイオマスでは100μmから大き
くても1〜2mm程度である必要がある。衝撃型の粉砕
法では、繊維方向に強度が強い特性を持つバイオマスの
粉砕物は、幅広い粒度分布を持つため(衝撃を与える方
向を繊維方向に対して一定にすることが難しい)、すべ
ての粒度のバイオマスを同等に反応させることは難し
い。従って、気流層ガス化ではどうしても粒度上限管理
が基本となり(たとえば全量2mm未満)、切断型のよ
うな粉砕動力が大きく、処理能力の低い粉砕器を用いざ
るを得ない。
At present, in the biomass pulverization, the grain size of about several mm is economically and practically the pulverization limit. As a crushing method, there are an impact type (hammer type, rod type, etc.), a cutting type (rotary blade cutting type, screw blade type, etc.), a mortar type mill, etc., but a hammer type is used for crushing a size of 10 mm or more,
A hammer type + rod type or a cutting type is mainly used for crushing a size of less than 10 mm. Further, for pulverization up to about 2 mm, a cutting die is mainly used as an equipment configuration, but since the required power is large, the processing capacity is small. Originally, in order to allow the thermal decomposition reaction to be sufficiently carried out in a short time, the smaller the particle size, the better (the particle size here is from the viewpoint of the reaction,
We shall refer to the short diameter). In order to react with a typical pyrolysis reaction time of several seconds in a typical air flow bed type furnace different from the present invention, the biomass needs to have a size of 100 μm to at most 1 to 2 mm. In the impact-type pulverization method, the pulverized product of biomass, which has the characteristic that the strength is strong in the fiber direction, has a wide particle size distribution (it is difficult to make the impact direction constant with respect to the fiber direction). It is difficult to make the same biomass react. Therefore, in the gasification of the gas stream, the upper limit of the particle size is inevitably controlled (for example, the total amount is less than 2 mm), and a crusher having a large crushing power and a low processing capacity such as a cutting die must be used.

【0014】本発明では、噴流層を形成させることで、
細かい粒子は短時間で、大きい粒子は長時間で反応し、
後段に排出される粒子の反応度合いをそろえることを可
能としている。その結果、10mm以上のサイズの、粗
い粒度のバイオマスであっても上昇流速を適切に設定す
ることで、バイオマス粒子が噴流層に滞留して充分に反
応させることができる。従って、本願発明では、衝撃型
のような低動力の粉砕設備の選択が可能になり、さらに
多量のバイオマス熱分解が可能となることを見いだし
た。
In the present invention, by forming a spouted bed,
Fine particles react in a short time, large particles react in a long time,
It is possible to arrange the reaction degree of the particles discharged in the latter stage. As a result, even with biomass having a coarse particle size of 10 mm or more, by appropriately setting the rising flow rate, the biomass particles can be retained in the spouted bed and sufficiently reacted. Therefore, in the present invention, it has been found that it is possible to select a low-power crushing equipment such as an impact type, and it is possible to pyrolyze a large amount of biomass.

【0015】本発明ではさらに、ガス化方法に関しても
検討した。バイオマスを熱分解する際に必要な高温ガス
の原料には、天然ガスやLPGのガス燃料、石炭、石
油、重油等の炭素質原料等多くの候補があるが、バイオ
マスをガス化原料としても使用することで、他の外部燃
料を最小限とする経済的なプロセスが構築可能である。
In the present invention, the gasification method was also examined. There are many candidates for high-temperature gas raw materials required for pyrolyzing biomass, such as natural gas and LPG gas fuel, carbonaceous raw materials such as coal, petroleum, and heavy oil, but biomass is also used as a gasification raw material. By doing so, it is possible to build an economical process that minimizes other external fuels.

【0016】ところが、バイオマスのガス化に関して
は、反応を充分に進行させるために気流層でのガス化方
法を用いなければならず、上記の通り、例えば全量短径
で2mm程度未満まで粉砕する必要が生じる。そこで、
10〜20mmを狙った衝撃式の粉砕機で十分対応可能
な利用方法を考案した。すなわち、上述の衝撃型破砕機
の持つ幅広い粒度分布特性を逆に利用したもので、粉砕
されたバイオマスを粗い粒子と細かい粒子に篩い分け
て、粗い粒子を熱分解に、細かい粒子をガス化に利用す
るというものである。図2に粒度分配によるバイオマス
供給機構をもった反応器の例を示した。図1の構成に、
バイオマス粉砕機10と粒度分配機構11、ガス化バイ
オマス供給装置12を加えたもので、粒度分配機構11
にはスクリーン、風力分級器等を用いることで実施でき
る。なお、同図において図1の符号と同一の符号は、同
一の部材を示す。
However, in regard to the gasification of biomass, it is necessary to use a gasification method in an airflow layer in order to allow the reaction to proceed sufficiently, and as described above, for example, it is necessary to pulverize the whole amount to a diameter of less than 2 mm. Occurs. Therefore,
We devised a usage method that can be sufficiently applied with an impact type crusher aiming at 10 to 20 mm. That is, the wide particle size distribution characteristics of the above-mentioned impact type crusher are used in reverse, by sieving the crushed biomass into coarse particles and fine particles, the coarse particles are pyrolyzed, and the fine particles are gasified. It is to use. FIG. 2 shows an example of a reactor having a biomass supply mechanism by particle size distribution. In the configuration of FIG.
A biomass crusher 10, a particle size distribution mechanism 11, and a gasified biomass supply device 12 are added, and the particle size distribution mechanism 11
Can be carried out by using a screen, an air classifier, or the like. In the figure, the same reference numerals as those in FIG. 1 denote the same members.

【0017】また、本願発明では、粗い粒子と細かい粒
子の定義は、両者を比較した場合の相対的な粒子の大き
さの違いであり、特に具体的に粒径を規定するものでは
ない。但し、効率の良い気流層のガス化炉で操業する場
合、現実的には細かい粒子は10mm未満のものが扱わ
れ、さらに反応性の観点から、好ましくは5〜6mm以
下である。また、粗い粒子は、上記の細かい粒子以外の
ものを意味する。
Further, in the present invention, the definitions of coarse particles and fine particles are differences in relative particle sizes when comparing the two, and do not particularly specify the particle size. However, when operating in a gasification furnace having an efficient air flow layer, in reality, fine particles having a size of less than 10 mm are handled, and in view of reactivity, the particle size is preferably 5 to 6 mm or less. Coarse particles mean particles other than the above-mentioned fine particles.

【0018】[0018]

【実施例】つぎに、実施例を挙げて、本発明をさらに詳
細に説明する。
EXAMPLES Next, the present invention will be described in more detail with reference to examples.

【0019】実施例1 衝突型破砕機の一つであるハンマー型破砕機により、バ
イオマスを破砕し、熱分解部1に投入した試験を実施し
た。バイオマス粒度は、短径で10mm未満が10質量
%、10mm以上50mm未満が60質量%、50mm
以上が30質量%と粗い粒子であった。バイオマス粉砕
物は一般的に短径と長径の差が大きく、代表値を規定し
にくいため、ここの場合、例えば10mm×10mmの
篩い目のスクリーンを充分時間をかけて通過した篩い下
粒子を「短径で10mm未満の粒子」、同様に10mm
×10mmの篩い目のスクリーンの篩い上でかつ50m
m×50mmの篩い目のスクリーンの篩い下の粒子を
「短径で10mm以上50mm未満の粒子」、50mm
×50mmの篩い目のスクリーンの篩い上の粒子を「短
径で50mm以上の粒子」とした。
Example 1 A test was carried out in which the biomass was crushed by a hammer crusher, which is one of the collision crushers, and the crushed biomass was put into the thermal decomposition section 1. Biomass particle size is 10% by mass with a short diameter of less than 10 mm, 60% by mass of 10 mm or more and less than 50 mm, 50 mm
The above was 30% by mass and coarse particles. In general, pulverized biomass has a large difference between the short diameter and the long diameter, and it is difficult to define a representative value. In this case, for example, the particles under the sieve that have passed through a screen of 10 mm × 10 mm sieve mesh for a sufficient time are “ Minor particles less than 10 mm ", also 10 mm
50m on the screen of a screen with a 10mm screen
Particles under the sieve of a screen of mx 50 mm sieve are "particles with a short diameter of 10 mm or more and less than 50 mm", 50 mm
The particles on the screen of the screen with a screen size of 50 mm × 50 mm were defined as “particles having a short diameter of 50 mm or more”.

【0020】熱分解温度の熱源としての高温ガスに、L
PG燃焼ガスを用いた場合(熱分解バイオマス量160
kg/hr、上記高温ガス温度1200℃、熱分解温度
700℃、上昇流速4m/s)、熱分解バイオマス量の
81%がガス及びタールに転換した。大きな粒度のバイ
オマスを用いても、バイオマスの揮発分(工業分析値;
83質量%程度)がほぼ揮発しており、充分熱を受けて
いることが確認できた。
The high-temperature gas as a heat source for the pyrolysis temperature contains L
When using PG combustion gas (Pyrolysis biomass amount 160
kg / hr, the above-mentioned high temperature gas temperature 1200 ° C, pyrolysis temperature 700 ° C, rising flow rate 4m / s), and 81% of the amount of pyrolysis biomass was converted to gas and tar. Even if a large particle size biomass is used, the volatile content of the biomass (industrial analysis value;
It was confirmed that about 83% by mass) was almost volatilized and that it was sufficiently heated.

【0021】実施例2 ガス化可能な短径2mm未満粒子を分離する例を以下に
示す。20mmの粉砕径を狙ったハンマー型バイオマス
破砕機10を使用し、目開き2mm×2mmのスクリー
ンを使用して分配すると、短径で2mm未満粒子が約3
0質量%となった。これにより、ガス化用に動力が大き
くコスト的に不利な切断型の破砕機を導入することな
く、安価な衝撃型(ハンマー型)破砕機を使用し、短径
で2mm以上の粒度のバイオマス70質量%を熱分解
に、短径で2mm未満の粒度のバイオマス30質量%を
ガス化に利用した。例えばバイオマスガス化量70kg
/hr、酸素40Nm3/hr、水蒸気10kg/h
r、ガス化温度1200℃、熱分解バイオマス量160
kg/hr、熱分解温度700℃で、上昇流速4m/s
ecとした場合(圧力で調整)バイオマスガス化量の9
5%が高温ガスに転換し、バイオマス熱分解量の82%
がガス及びタールに転換した。実施例1と同様、熱分解
バイオマス揮発分はほぼ揮発しており、充分熱を受けて
いる。
Example 2 An example of separating gasifiable particles having a short diameter of less than 2 mm is shown below. When a hammer type biomass crusher 10 aiming at a crushing diameter of 20 mm is used and distribution is performed using a screen having an opening of 2 mm × 2 mm, particles having a short diameter of less than 2 mm are about 3 particles.
It became 0 mass%. As a result, an inexpensive impact-type (hammer-type) crusher is used without introducing a cutting-type crusher that has large power for gasification and is disadvantageous in terms of cost, and the biomass 70 with a short diameter and a particle size of 2 mm or more is used. % By mass was used for pyrolysis, and 30% by mass of biomass with a short diameter and a particle size of less than 2 mm was used for gasification. For example, biomass gasification amount 70kg
/ Hr, oxygen 40Nm3 / hr, steam 10kg / h
r, gasification temperature 1200 ° C, pyrolysis biomass amount 160
kg / hr, pyrolysis temperature 700 ° C, rising flow rate 4 m / s
When ec is set (adjusted by pressure), the amount of biomass gasification is 9
5% converted to hot gas, 82% of biomass pyrolysis
Converted to gas and tar. As in Example 1, the volatile components of the pyrolyzed biomass are almost volatilized and are sufficiently heated.

【0022】なお、粒度分離の分岐点のサイズ(上記の
場合2mm)は、上昇流速を変えることで調整可能であ
り(たとえば原料性状によって2mm未満サイズの割合
が30質量%に満たない場合は、圧力調整等で上昇流速
を大きく設定することにより、分岐点サイズがたとえば
3mmというように大きくとれ、ガス化に必要な量を確
保することが可能)、原料性状による破砕粒度の変化に
対しても自由度の高い設備である。
The size of the branch point for particle size separation (2 mm in the above case) can be adjusted by changing the rising flow rate (for example, when the ratio of the size of less than 2 mm is less than 30% by mass depending on the raw material properties, By setting the rising flow velocity to a large value by adjusting the pressure etc., the branch point size can be made large, for example, 3 mm, and the amount necessary for gasification can be secured.) This is a highly flexible facility.

【0023】[0023]

【発明の効果】本発明により、粒度の大きいバイオマス
でも安定して熱分解反応を進行させることが可能とな
る。また、その結果として、動力が大きく、処理量の少
ない切断型の粉砕設備を用いずに設備構成を選択するこ
とも可能となる。さらに、篩い分け装置を使用すること
で、外部燃料を最小限とする熱分解が可能となる。
EFFECTS OF THE INVENTION According to the present invention, it is possible to stably proceed the thermal decomposition reaction even with biomass having a large particle size. In addition, as a result, it becomes possible to select the equipment configuration without using a cutting-type crushing equipment having a large power and a small throughput. In addition, the use of a sieving device allows pyrolysis with minimal external fuel.

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

【図1】 噴流層バイオマスガス化炉、熱分解部の概略
図。
FIG. 1 is a schematic view of a spouted bed biomass gasification furnace and a pyrolysis unit.

【図2】 粒度分配によるバイオマス供給装置の概略
図。
FIG. 2 is a schematic diagram of a biomass supply device by particle size distribution.

【符号の説明】[Explanation of symbols]

1…熱分解部 2…熱分解部バイオマス供給装置 3…バイオマス 4…接続部 5…高温ガス 6…噴流層 7…テーパー部 8…ガス化炉 9…ガス下降流 10…バイオマス粉砕機 11…粒度分配機構 12…ガス化バイオマス供給装置 1 ... Thermal decomposition part 2 Pyrolysis section biomass supply device 3 ... Biomass 4 ... Connection part 5 ... High temperature gas 6 ... Spout layer 7 ... Tapered part 8 ... Gasification furnace 9 ... Gas downflow 10 ... Biomass crusher 11 ... Grain size distribution mechanism 12 ... Gasification biomass supply device

───────────────────────────────────────────────────── 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) B09B 3/00 ZAB B09B 3/00 Z 5/00 5/00 Z (72)発明者 汐田 晴是 千葉県富津市新富20−1 新日本製鐵株式 会社技術開発本部内 (72)発明者 藤川 淳 福岡県北九州市戸畑区大字中原46−59 新 日本製鐵株式会社エンジニアリング事業本 部内 Fターム(参考) 4D004 AA01 CA04 CA08 CA24 CA27 CB01 DA03 DA06 DA20 4D021 AA03 EA10 EB01 ─────────────────────────────────────────────────── ─── Continuation of front page (51) Int.Cl. 7 Identification code FI theme code (reference) B09B 3/00 ZAB B09B 3/00 Z 5/00 5/00 Z (72) Inventor Haruta Shioda Chiba Prefecture 20-1 Shintomi, Futtsu-shi Nippon Steel Co., Ltd. Technology Development Division (72) Inventor Atsushi Fujikawa 46-59 Nakahara, Tobata-ku, Kitakyushu, Fukuoka Prefecture F-Term (Reference) 4D004, Engineering Business Division, Nippon Steel Corporation AA01 CA04 CA08 CA24 CA27 CB01 DA03 DA06 DA20 4D021 AA03 EA10 EB01

Claims (3)

【特許請求の範囲】[Claims] 【請求項1】 バイオマスを熱分解原料とし、噴流層で
熱分解反応によってガス、タール及びチャーの生成物を
得るバイオマス熱分解方法において、該熱分解反応の熱
源として800℃以上の高温ガスを用いるバイオマス熱
分解方法であって、熱分解部でのガスの上昇流速を1m
/sec〜15m/secとすることを特徴とする、バ
イオマス熱分解方法
1. A high-temperature gas of 800 ° C. or higher is used as a heat source of the pyrolysis reaction in a biomass pyrolysis method for obtaining a product of gas, tar and char by a pyrolysis reaction in a spouted bed using biomass as a pyrolysis raw material. Biomass pyrolysis method, in which the rising velocity of gas in the pyrolysis unit is 1 m
/ Sec to 15 m / sec, biomass pyrolysis method
【請求項2】 バイオマスをガス化原料とし、酸素、あ
るいは酸素と水蒸気でガス化して得られるガスを熱分解
反応の熱源として使用するに際し、粉砕したバイオマス
を篩い分け、細かい粒度のバイオマスをガス化原料とし
て、また粗い粒度のバイオマスを熱分解原料として使用
することを特徴とする、請求項1記載のバイオマス熱分
解方法
2. When using biomass as a gasification raw material and oxygen or a gas obtained by gasifying with oxygen and steam as a heat source for a thermal decomposition reaction, crushed pulverized biomass is sieved to gasify fine-grained biomass. The biomass pyrolysis method according to claim 1, characterized in that biomass having a coarse grain size is used as a raw material and as a pyrolysis raw material.
【請求項3】 ガス化炉と、熱分解部と、該ガス化炉と
該熱分解部を連接する接続部と、バイオマス粉砕機と、
該バイオマス粉砕機での粉砕物を篩い分けする篩い分け
装置と、篩い分けされた篩上粒子を熱分解部に、篩下粒
子をガス化炉に供給する供給装置を備えたバイオマス熱
分解装置
3. A gasification furnace, a thermal decomposition section, a connecting section connecting the gasification furnace and the thermal decomposition section, and a biomass crusher,
Biomass pyrolyzer equipped with a sieving device for sieving the pulverized material in the biomass pulverizer, and a supply device for supplying the sieved particles on the screen to the thermal decomposition part and the particles under the screen to the gasification furnace.
JP2002069027A 2002-03-13 2002-03-13 Biomass pyrolysis method and apparatus Withdrawn JP2003268388A (en)

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Publication Number Publication Date
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Family

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Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2010521544A (en) * 2007-03-15 2010-06-24 シンクラフト エンジニアリング ゲーエムベーハー Gasifier
JP2021088694A (en) * 2019-11-08 2021-06-10 シンクラフト エンジニアリング ゲーエムベーハーSynCraft Engineering GmbH Method and apparatus for adjusting filling level in floating bed reactor
CN114479952A (en) * 2020-10-27 2022-05-13 中国石油化工股份有限公司 Biomass hydrogen production heat carrier and preparation method and application thereof

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2010521544A (en) * 2007-03-15 2010-06-24 シンクラフト エンジニアリング ゲーエムベーハー Gasifier
JP2021088694A (en) * 2019-11-08 2021-06-10 シンクラフト エンジニアリング ゲーエムベーハーSynCraft Engineering GmbH Method and apparatus for adjusting filling level in floating bed reactor
JP7612188B2 (en) 2019-11-08 2025-01-14 シンクラフト エンジニアリング ゲーエムベーハー Method and device for adjusting the filling level of a floating bed reactor
CN114479952A (en) * 2020-10-27 2022-05-13 中国石油化工股份有限公司 Biomass hydrogen production heat carrier and preparation method and application thereof

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