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JP6553877B2 - Wet biomass incineration system - Google Patents
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JP6553877B2 - Wet biomass incineration system - Google Patents

Wet biomass incineration system Download PDF

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JP6553877B2
JP6553877B2 JP2015013429A JP2015013429A JP6553877B2 JP 6553877 B2 JP6553877 B2 JP 6553877B2 JP 2015013429 A JP2015013429 A JP 2015013429A JP 2015013429 A JP2015013429 A JP 2015013429A JP 6553877 B2 JP6553877 B2 JP 6553877B2
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superheated steam
wet biomass
drying chamber
drying
biomass
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JP2016138694A (en
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竹田 航哉
航哉 竹田
松田 吉洋
吉洋 松田
秀一 太白
秀一 太白
直哉 川本
直哉 川本
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Kawasaki Motors Ltd
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    • 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
    • Y02E20/00Combustion technologies with mitigation potential
    • Y02E20/12Heat utilisation in combustion or incineration of waste
    • 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
    • Y02P80/00Climate change mitigation technologies for sector-wide applications
    • Y02P80/10Efficient use of energy, e.g. using compressed air or pressurized fluid as energy carrier
    • Y02P80/15On-site combined power, heat or cool generation or distribution, e.g. combined heat and power [CHP] supply

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Description

本発明は、湿潤バイオマス焼却システムに関する。   The present invention relates to a wet biomass incineration system.

従来、下水汚泥または木質系物質等の湿潤バイオマスを処理する施設として、例えば、焼却炉と、焼却炉からの排ガスで発電する発電装置とを備える湿潤バイオマス焼却システムが知られている。   Conventionally, as a facility for treating wet biomass such as sewage sludge or wood-based material, a wet biomass incineration system including, for example, an incinerator and a power generation device that generates electric power by the exhaust gas from the incinerator is known.

焼却炉の形式としては、例えば、内部循環流動層式が挙げられる。この形式の焼却炉は、例えば特許文献1に開示されるように、乾燥・熱分解室と燃焼室とを有する。乾燥・熱分解室と燃焼室との各々の下方には、流動媒体が流動する流動床が設けられる。乾燥・熱分解室では、流動床の下方から供給される高温の乾燥剤ガスで、湿潤バイオマスを流動媒体と混合しながら乾燥させて乾燥バイオマスとする。燃焼室では、流動床の下方から供給される高温の酸化剤ガスで、乾燥バイオマスを流動媒体と混合しながら燃焼する。   As a type of incinerator, for example, an internal circulating fluidized bed type can be mentioned. This type of incinerator has, for example, a drying / pyrolysis chamber and a combustion chamber as disclosed in Patent Document 1. Below each of the drying and thermal decomposition chamber and the combustion chamber, there is provided a fluidized bed in which a fluidized medium flows. In the drying and thermal decomposition chamber, the wet biomass is dried while being mixed with the fluid medium with a high temperature desiccant gas supplied from below the fluidized bed to form dry biomass. In the combustion chamber, dry biomass is combusted while being mixed with the fluidized medium with a high-temperature oxidant gas supplied from below the fluidized bed.

なお、乾燥・熱分解室では、乾燥バイオマスを熱分解させる場合もある。この熱分解により生じたガスは、例えば乾燥・熱分解室の外へ排出され、発電装置等の動力回収装置を用いて熱回収される。   In the drying / pyrolysis chamber, dry biomass may be pyrolyzed. The gas generated by this thermal decomposition is discharged out of the drying / pyrolysis chamber, for example, and is recovered by using a power recovery device such as a power generation device.

特開2006−275442号公報JP, 2006-275442, A

湿潤バイオマス焼却システムは、ランニングコストが低く、良好な燃焼効率で運転を行えることが求められる。従って、湿潤バイオマス焼却システムの熱回収効率は、良好であることが望ましい。また、湿潤バイオマス焼却システムは、ある程度の規模で構成されるので、設備費用を抑制することも求められる。   The wet biomass incineration system is required to have a low running cost and to be operated with good combustion efficiency. Therefore, it is desirable that the heat recovery efficiency of the wet biomass incineration system be good. In addition, since the wet biomass incineration system is configured on a certain scale, it is also required to reduce equipment costs.

しかしながら、特許文献1に記載されたシステムにおいて、乾燥・熱分解室で熱分解により生じたガスから発電装置等の動力回収装置を用いて熱回収を行う場合、当該ガスを動力回収装置に供給する前に蒸気等の成分を除去する処理を行う。このため、熱回収の損失が生じるおそれがある。   However, in the system described in Patent Document 1, when heat recovery is performed using a power recovery device such as a power generator from the gas generated by pyrolysis in the drying / pyrolysis chamber, the gas is supplied to the power recovery device. Prior to this, a process of removing components such as steam is performed. This may result in loss of heat recovery.

そこで本発明は、発電装置の熱回収の損失を抑制することで、低いランニングコストかつ良好な燃焼効率で運転でき、設備費用を抑制できる湿潤バイオマス焼却システムの提供を目的とする。   Then, an object of the present invention is to provide a wet biomass incineration system that can be operated at low running cost and good combustion efficiency by suppressing the loss of heat recovery of the power generation apparatus, and can reduce equipment cost.

上記課題を解決するため、本発明の一態様に係る湿潤バイオマス焼却システムは、炉床の上方の空間が区画壁で区画されてなる乾燥室及び燃焼室を有し、かつ前記乾燥室内の下方と前記燃焼室内の下方とにわたって、流動媒体が流動する流動床が設けられた焼却炉と、前記焼却炉の排ガスを用いて発電する発電装置と、前記乾燥室側の前記流動床の下方に接続され、前記乾燥室内で湿潤バイオマスを前記流動媒体と混合しながら乾燥するための過熱蒸気を前記乾燥室内に供給する過熱蒸気供給路と、前記燃焼室側の前記流動床の下方に接続され、前記湿潤バイオマスを乾燥して生成した乾燥バイオマスを前記燃焼室内で前記流動媒体と混合しながら燃焼するための酸化性ガスを前記燃焼室内に供給する酸化性ガス供給路と、前記乾燥室に接続され、前記湿潤バイオマスの乾燥に用いられた過熱蒸気を前記乾燥室外に排出して前記発電装置に送る過熱蒸気排出路と、を備え、前記乾燥室内の前記流動床の温度が、前記乾燥バイオマスの熱分解温度未満に設定され、前記排ガスを、前記過熱蒸気排出路を流通する過熱蒸気とする。   In order to solve the above problems, a wet biomass incineration system according to an aspect of the present invention includes a drying chamber and a combustion chamber in which a space above the hearth is partitioned by partition walls, and a lower portion in the drying chamber An incinerator provided with a fluidized bed in which a fluidized medium flows, a power generation apparatus generating electric power using exhaust gas of the incinerator, and a lower part of the fluidized bed on the drying chamber side A superheated steam supply passage for supplying superheated steam for drying while mixing wet biomass with the fluid medium in the drying chamber into the drying chamber, and connected below the fluid bed on the combustion chamber side, Connected to the drying chamber, an oxidizing gas supply path for supplying an oxidizing gas into the combustion chamber for burning the dry biomass produced by drying the biomass while mixing with the fluid medium in the combustion chamber And a superheated steam discharge passage that discharges the superheated steam used for drying the wet biomass to the power generation device and discharges the superheated steam to the power generation device, and the temperature of the fluidized bed in the dry chamber is the temperature of the dry biomass. The exhaust gas is set to a temperature lower than the thermal decomposition temperature, and the exhaust gas is superheated steam flowing through the superheated steam discharge path.

上記構成によれば、乾燥室内の流動床の温度を乾燥バイオマスの熱分解温度未満に設定することで、乾燥室内での乾燥バイオマスの熱分解を防止でき、乾燥室から過熱蒸気排出路に排出される過熱蒸気に、乾燥バイオマスの熱分解に伴って生じるガスが混入するのを防止できる。これにより、高純度の過熱蒸気を過熱蒸気排出路を介して発電装置に供給するので、発電装置に供給するガスの不純物成分を予め除去する工程が不要になる。よって、過熱蒸気排出路を流通するガスのほぼ全てを用いて熱回収できる。従って、熱回収の損失を抑制しながら、過熱蒸気の豊富な潜熱を有効に利用して、高い発電効率で安定して発電できる。   According to the above configuration, by setting the temperature of the fluidized bed in the drying chamber to less than the thermal decomposition temperature of the dry biomass, thermal decomposition of the dried biomass in the drying chamber can be prevented, and the drying chamber is discharged to the superheated steam discharge passage The superheated steam can be prevented from mixing with the gas generated by the thermal decomposition of dry biomass. As a result, the superheated steam of high purity is supplied to the power generation apparatus through the superheated steam discharge path, so that the process of removing the impurity component of the gas supplied to the power generation apparatus in advance becomes unnecessary. Therefore, heat can be recovered using substantially all of the gas flowing through the superheated steam discharge passage. Accordingly, it is possible to stably generate power with high power generation efficiency by effectively using the latent heat rich in superheated steam while suppressing loss of heat recovery.

また、過熱蒸気は、乾燥バイオマスの熱分解に伴って生じるガス等に比べ、発電装置及び排ガス流通路を汚染しにくいので、発電装置が汚染されて発電効率が低下するのを防止できる。これにより、良好な燃焼効率で焼却炉を運転できるとともに、湿潤バイオマス焼却システムのランニングコストを低減できる。また、乾燥室と燃焼室とを有するように焼却炉を一体的に構成することによって、焼却炉をコンパクトに構成でき、設備費用を抑制できる。   In addition, since the superheated steam is less likely to contaminate the power generation device and the exhaust gas flow passage as compared with the gas or the like generated due to the thermal decomposition of the dry biomass, it is possible to prevent the power generation device from being contaminated and reducing the power generation efficiency. As a result, the incinerator can be operated with good combustion efficiency, and the running cost of the wet biomass incineration system can be reduced. Further, by integrally configuring the incinerator so as to have a drying chamber and a combustion chamber, the incinerator can be configured in a compact manner, and facility costs can be suppressed.

前記焼却炉に接続され、前記湿潤バイオマスを前記乾燥室内に直接供給する第1の湿潤バイオマス供給路と、前記過熱蒸気排出路に接続され、前記湿潤バイオマスを前記過熱蒸気排出路の一部を経由して前記乾燥室内に供給する第2の湿潤バイオマス供給路と、をさらに備えてもよい。   Connected to the incinerator, connected to the first wet biomass supply passage for supplying the wet biomass directly into the drying chamber, and the superheated steam discharge passage, and the wet biomass via a part of the superheated steam discharge passage And a second wet biomass feed path for feeding into the drying chamber.

上記構成によれば、第1及び第2の湿潤バイオマス供給路を通じて、複数の位置から湿潤バイオマスを乾燥室内に分散して供給でき、湿潤バイオマスを効率よく過熱蒸気で迅速に乾燥できる。また、乾燥室内で湿潤バイオマスが局所的に堆積するのを防止でき、乾燥室の炉床への負荷を抑制できる。   According to the above configuration, the wet biomass can be dispersed and supplied from the plurality of positions into the drying chamber through the first and second wet biomass supply channels, and the wet biomass can be efficiently dried rapidly with the superheated steam. Moreover, it is possible to prevent the wet biomass from being locally deposited in the drying chamber, and to suppress the load on the hearth of the drying chamber.

前記焼却炉は、前記乾燥室近傍の前記燃焼室側の前記流動床の内部に、前記燃焼室側の前記流動床の下方から、前記燃焼室の流動床の層高よりも低い高さまで延びるように設けられた仕切壁をさらに有していてもよい。   The incinerator extends from the lower side of the fluidized bed on the combustion chamber side to a height lower than the bed height of the fluidized bed in the combustion chamber, inside the fluidized bed on the combustion chamber side near the drying chamber. You may have further the partition wall provided in.

これにより、燃焼室内の燃焼ガスまたは酸化性ガスが乾燥室内に流入し、過熱蒸気に混入するのを仕切壁によって一層防止でき、過熱蒸気を用いて発電する発電装置の発電効率を向上できる。   Thus, the partition wall can further prevent the combustion gas or the oxidizing gas in the combustion chamber from flowing into the drying chamber and mixing in the overheated steam, and the power generation efficiency of the power generation apparatus that generates power using the overheated steam can be improved.

前記乾燥室に前記過熱蒸気供給路が複数接続され、いずれかの前記過熱蒸気供給路同士の蒸気流量が異なっていてもよい。   A plurality of the superheated steam supply paths may be connected to the drying chamber, and the steam flow rates of any of the superheated steam supply paths may be different.

このように、蒸気流量が異なる複数の過熱蒸気供給路を乾燥室に接続し、各過熱蒸気供給路から過熱蒸気を乾燥室に供給することで、乾燥室内で、流動媒体と湿潤バイオマスとを過熱蒸気流量が高い位置から低い位置に向けて移動できる。これにより、湿潤バイオマスと過熱蒸気とを良好に混合して、湿潤バイオマスの乾燥を早めることができる。   In this way, by connecting a plurality of superheated steam supply paths with different steam flow rates to the drying chamber and supplying superheated steam from each superheated steam supply path to the drying chamber, the fluid medium and wet biomass are superheated in the drying chamber. It can move from a high steam flow position to a low position. Thereby, wet biomass and superheated steam can be mixed well, and drying of wet biomass can be accelerated.

前記乾燥室内で、前記湿潤バイオマス及び前記流動媒体が循環するように、複数の前記過熱蒸気供給路の蒸気流量が設定されてもよい。   The steam flow rates of the plurality of superheated steam supply paths may be set such that the wet biomass and the fluid medium circulate in the drying chamber.

このように、湿潤バイオマス及び流動媒体を循環させて循環流を形成することで、湿潤バイオマスの乾燥を一層早めることができる。   Thus, by circulating the wet biomass and the fluid medium to form a circulating flow, the drying of the wet biomass can be further accelerated.

前記過熱蒸気供給路は、第1過熱蒸気供給路であり、前記乾燥室の側壁に接続され、前記流動床に対し、前記乾燥室から前記燃焼室に向けて前記流動媒体及び前記乾燥バイオマスの移動を促すように前記乾燥室内に過熱蒸気を供給する第2過熱蒸気供給路をさらに備えていてもよい。   The superheated steam supply path is a first superheated steam supply path, is connected to a side wall of the drying chamber, and moves the fluid medium and the dried biomass from the drying chamber toward the combustion chamber with respect to the fluidized bed A second superheated steam supply path for supplying superheated steam into the drying chamber may be further provided.

上記構成によれば、乾燥室の下方と側方の複数の位置から湿潤バイオマスに過熱蒸気を接触させ、湿潤バイオマスの乾燥を早めることができる。また、焼却炉内の乾燥バイオマスの搬送を効率よく行うことができる。   According to the above configuration, the wet biomass can be brought into contact with the superheated steam from a plurality of positions on the lower side and the side of the drying chamber to accelerate the drying of the wet biomass. Moreover, the dry biomass in the incinerator can be efficiently transported.

前記発電装置は、前記過熱蒸気排出路を流通する過熱蒸気と熱媒体とが熱交換する熱交換器と、前記熱交換器に接続され、前記熱媒体により発電する発電機とを有するバイナリー発電装置であってもよい。   The power generating apparatus is a binary power generating apparatus including: a heat exchanger in which the overheated steam flowing through the overheated vapor discharge path exchanges heat with a heat medium; and a generator connected to the heat exchanger and generating electricity from the heat medium It may be

これにより、熱交換器において、熱媒体と過熱蒸気とを熱交換させ、熱媒体で発電装置を駆動することで、発電装置において効率よく発電できる。   Thereby, in the heat exchanger, the heat medium and the superheated steam are subjected to heat exchange, and the heat medium drives the power generation device, whereby the power generation device can efficiently generate power.

前記過熱蒸気排出路から前記発電装置を迂回するように分岐する迂回路と、前記過熱蒸気排出路の前記発電装置が設けられた位置よりも上流側から分岐し、かつ前記過熱蒸気排出路を流通した過熱蒸気を大気中に開放する開放路とのいずれかを含む分岐路をさらに備え、前記分岐路には、前記発電装置に供給する過熱蒸気量を一定にするためのバルブが設けられていてもよい。   A detour that branches to bypass the power generation device from the superheated steam discharge channel, and a branch from the upstream side of the position where the power generation device of the superheated steam discharge channel is provided, and flows through the superheated steam discharge channel The fuel cell system further includes a branch path including one of an open path for opening the superheated steam to the atmosphere, and the branch path is provided with a valve for making the amount of the superheated steam supplied to the power generation apparatus constant. It is also good.

上記構成により、発電装置に流通する過熱蒸気量が一定になるように図ることができ、発電装置において、安定した発電電力が得られる。   According to the above configuration, the amount of overheated steam flowing through the power generation device can be made constant, and stable power generation can be obtained in the power generation device.

前記過熱蒸気供給路と前記過熱蒸気排出路との間に接続され、前記過熱蒸気排出路を流通する過熱蒸気の一部を前記過熱蒸気供給路に戻す過熱蒸気還流路をさらに備えていてもよい。   A superheated steam recirculation path connected between the superheated steam supply path and the superheated steam discharge path and returning a part of the superheated steam flowing through the superheated steam discharge path to the superheated steam supply path may be further provided. .

これにより、例えば乾燥室内の過熱蒸気量が不足した場合であっても、過熱蒸気還流路から過熱蒸気を乾燥室内に供給でき、その不足分を補うことができる。   Thereby, even if the amount of superheated steam in the drying chamber is insufficient, for example, the superheated steam can be supplied from the superheated steam return path into the drying chamber, and the shortage can be compensated.

前記過熱蒸気排出路の途中に設けられ、過熱蒸気に含まれる煤塵を回収する集塵機と、前記集塵機と前記焼却炉の間に接続され、前記集塵機で回収された煤塵を前記燃焼室に戻す煤塵流通路と、をさらに備えていてもよい。   A dust collector provided in the middle of the superheated steam discharge path and connected between a dust collector for collecting dust contained in the superheated steam, the dust collector and the incinerator, and returning the dust collected by the dust collector to the combustion chamber And a path may be further provided.

これにより、乾燥バイオマスの燃焼灰と煤塵とを一カ所に集約でき、燃焼灰と煤塵との管理を行い易くできる。   As a result, it is possible to concentrate the dried biomass combustion ash and dust in one place, and to easily manage the combustion ash and dust.

前記過熱蒸気供給路から分岐して前記乾燥室に接続された過熱蒸気流通路をさらに備え、前記過熱蒸気流通路を流通した過熱蒸気が、前記乾燥室内で、前記流動床に向かって落下する前記湿潤バイオマスに対して分散しながら噴出されてもよい。   The superheated steam flow passage is further branched from the superheated steam supply passage and connected to the drying chamber, and the superheated steam flowing through the superheated steam flow passage drops toward the fluidized bed in the drying chamber. It may be jetted while being dispersed to the wet biomass.

これにより、分岐路を流通した過熱蒸気で湿潤バイオマスを分散させ、湿潤バイオマスと過熱蒸気とを効率よく接触させることにより、湿潤バイオマスの乾燥を早めることができる。   Thereby, the wet biomass can be accelerated by dispersing the wet biomass with the superheated steam flowing through the branch path and efficiently contacting the wet biomass with the superheated steam.

前記焼却炉に接続され、前記乾燥室に前記湿潤バイオマスを供給する湿潤バイオマス供給路をさらに備え、前記湿潤バイオマス供給路は、前記燃焼室内を経由して設けられていてもよい。   The system may further include a wet biomass feed path connected to the incinerator and supplying the wet biomass to the drying chamber, and the wet biomass feed path may be provided via the combustion chamber.

これにより、乾燥室に供給する前に湿潤バイオマスを予め加熱でき、乾燥室内における湿潤バイオマスの乾燥を早めることができる。   Thus, the wet biomass can be preheated before being supplied to the drying chamber, and the drying of the wet biomass in the drying chamber can be accelerated.

上記した本発明の各態様によれば、発電装置の熱回収の損失を抑制することで、低いランニングコストかつ良好な燃焼効率で運転でき、設備費用を抑制できる湿潤バイオマス焼却システムを提供できる。   According to each aspect of the present invention described above, it is possible to provide a wet biomass incineration system that can be operated at low running cost and good combustion efficiency and can reduce facility cost by suppressing the loss of heat recovery of the power generation apparatus.

第1実施形態に係る湿潤バイオマス焼却システムの全体を示す図である。It is a figure showing the whole wet biomass incineration system concerning a 1st embodiment. 第2実施形態に係る湿潤バイオマス焼却システムの一部を示す図である。It is a figure which shows a part of wet biomass incineration system which concerns on 2nd Embodiment. 第3実施形態に係る湿潤バイオマス焼却システムの一部を示す図である。It is a figure showing a part of wet biomass incineration system concerning a 3rd embodiment. 第4実施形態に係る湿潤バイオマス焼却システムの一部を示す図である。It is a figure which shows a part of wet biomass incineration system which concerns on 4th Embodiment. 第5実施形態に係る湿潤バイオマス焼却システムの一部を示す図である。It is a figure which shows a part of wet biomass incineration system concerning 5th Embodiment. 第6実施形態に係る湿潤バイオマス焼却システムの一部を示す図である。It is a figure which shows a part of wet biomass incineration system concerning 6th Embodiment. 第7実施形態に係る湿潤バイオマス焼却システムの一部を示す図である。It is a figure which shows a part of wet biomass incineration system which concerns on 7th Embodiment. 第8実施形態に係る湿潤バイオマス焼却システムの一部を示す図である。It is a figure showing a part of wet biomass burning system concerning an 8th embodiment. 第9実施形態に係る湿潤バイオマス焼却システムの一部を示す図である。It is a figure which shows a part of wet biomass incineration system which concerns on 9th Embodiment. 第10実施形態に係る湿潤バイオマス焼却システムの一部を示す図である。It is a figure which shows a part of wet biomass incineration system which concerns on 10th Embodiment.

以下、本発明の各実施形態について、各図を参照しながら説明する。   Hereinafter, embodiments of the present invention will be described with reference to the drawings.

(第1実施形態)
図1は、第1実施形態に係る湿潤バイオマス焼却システム1の全体を示す図である。図1に示すように、湿潤バイオマス焼却システム1は、焼却炉2、集塵機3、発電装置4、湿潤バイオマス供給路R1、過熱蒸気供給路R2、過熱蒸気排出路R3、酸化性ガス供給路R4、燃焼ガス排出路R5及び燃焼灰排出路R6を備える。
First Embodiment
FIG. 1 is a diagram showing the entire wet biomass incineration system 1 according to the first embodiment. As shown in FIG. 1, the wet biomass incineration system 1 includes an incinerator 2, a dust collector 3, a power generation device 4, a wet biomass supply path R1, a superheated steam supply path R2, a superheated steam discharge path R3, an oxidizing gas supply path R4, A combustion gas discharge path R5 and a combustion ash discharge path R6 are provided.

焼却炉2では、炉床2iの上方の空間S1、S2が区画壁2eで区画されることにより、湿潤バイオマスMを乾燥させる乾燥室2aと、乾燥バイオマス(乾燥された湿潤バイオマスM)を燃焼する燃焼室2bとが形成される。また、焼却炉2には、乾燥室2a内の下方と燃焼室2b内の下方とにわたって、流動床2c、2dが設けられる。流動床2c、2dは、流動媒体Fを用いて構成される。流動媒体Fは、例えば珪砂であるが、流動媒体Fは、これに限定されない。   In the incinerator 2, the space S1 and S2 above the hearth 2i are partitioned by the partition wall 2e, so that the drying chamber 2a for drying the wet biomass M and the dry biomass (dried wet biomass M) are combusted. A combustion chamber 2b is formed. Further, the incinerator 2 is provided with fluidized beds 2c and 2d over the lower part in the drying chamber 2a and the lower part in the combustion chamber 2b. The fluidized beds 2 c and 2 d are configured using a fluid medium F. The fluid medium F is, for example, silica sand, but the fluid medium F is not limited thereto.

乾燥室2aの上方には、湿潤バイオマス供給口2a1が形成される。湿潤バイオマス供給口2a1には、外部から乾燥室2a内に湿潤バイオマスMを供給するための湿潤バイオマス供給路R1が接続される。乾燥室2aの流動床2cの下方には、内部が中空の箱体である風箱2fが設けられる。風箱2fの下方には、湿潤バイオマスMを流動媒体(粒子状物質)Fと混合させながら乾燥させるための過熱蒸気を乾燥室2aに供給する過熱蒸気供給路R2が接続される。乾燥室2aの上方には、湿潤バイオマスMの乾燥に用いられた過熱蒸気を排ガスとして、乾燥室2aの外部に排出するための過熱蒸気排出路R3が接続される。   A wet biomass feed port 2a1 is formed above the drying chamber 2a. A wet biomass supply passage R1 for supplying the wet biomass M from the outside into the drying chamber 2a is connected to the wet biomass supply port 2a1. Below the fluidized bed 2c of the drying chamber 2a, an air box 2f that is a hollow box is provided. Below the air box 2f is connected a superheated steam supply passage R2 for supplying superheated steam for drying the wet biomass M while mixing it with the fluid medium (particulate matter) F to the drying chamber 2a. Above the drying chamber 2a, a superheated steam discharge passage R3 for discharging the superheated steam used for drying the wet biomass M to the outside of the drying chamber 2a as exhaust gas is connected.

燃焼室2bの流動床2dの下方には、風箱2fとほぼ同様の構成の風箱2gが設けられる。風箱2gの下方には、乾燥バイオマスを流動媒体Fと混合させながら燃焼させるための酸化性ガスを燃焼室2bに供給する酸化性ガス供給路R4が接続される。風箱2f、2gの間は、仕切壁2hにより仕切られる。燃焼室2bの上方には、乾燥バイオマスの燃焼により生じた燃焼ガスを燃焼室2bの外部に排出するための燃焼ガス排出路R5が接続される。   Below the fluidized bed 2d of the combustion chamber 2b, a wind box 2g having a configuration similar to that of the wind box 2f is provided. Below the air box 2g, an oxidizing gas supply passage R4 is connected which supplies an oxidizing gas for burning the dry biomass while mixing it with the fluid medium F to the combustion chamber 2b. The air box 2f, 2g is partitioned by a partition wall 2h. Above the combustion chamber 2b, a combustion gas discharge passage R5 for discharging the combustion gas generated by the combustion of the dry biomass to the outside of the combustion chamber 2b is connected.

流動床2c、2dの下方に配置された炉床2iには、複数のノズル2jが、分散して設けられる。乾燥室2a内の各ノズル2jからは、過熱蒸気供給路R2から供給された過熱蒸気が、風箱2fを経由して乾燥室2a内に噴出される。流動床2cでは、各ノズル2jから噴出する過熱蒸気の流れにより、湿潤バイオマスMが流動媒体Fとともに流動し、撹拌混合されながら乾燥され、乾燥バイオマスとなる。図1に示すように、乾燥バイオマスは、乾燥室2aから燃焼室2bへと送られる。燃焼室2b内の各ノズル2jからは、酸化性ガス供給路R4から供給された酸化性ガスが、風箱2gを経由して燃焼室2b内に噴出される。酸化性ガスは、例えば空気であるが、これに限定されない。流動床2dでは、各ノズル2jから噴出する酸化性ガスの流れにより、乾燥バイオマスが流動媒体Fとともに流動し、撹拌混合されながら燃焼される。燃焼室2bの熱は、流動媒体Fとともに乾燥室2a側に移動し、乾燥室2a内における湿潤バイオマスMの乾燥に用いられる。   A plurality of nozzles 2j are provided in a distributed manner in the hearth 2i disposed below the fluidized beds 2c and 2d. The superheated steam supplied from the superheated steam supply passage R2 is ejected from the nozzles 2j in the drying chamber 2a into the drying chamber 2a via the air box 2f. In the fluidized bed 2c, the wet biomass M flows together with the fluid medium F by the flow of the superheated steam spouted from the respective nozzles 2j, and is dried while being stirred and mixed to become a dried biomass. As shown in FIG. 1, dry biomass is sent from the drying chamber 2a to the combustion chamber 2b. The oxidizing gas supplied from the oxidizing gas supply passage R4 is ejected from the nozzles 2j in the combustion chamber 2b into the combustion chamber 2b via the air box 2g. The oxidizing gas is, for example, air, but is not limited thereto. In the fluidized bed 2d, the dried biomass flows together with the fluid medium F by the flow of the oxidizing gas ejected from each nozzle 2j, and is burned while being stirred and mixed. The heat of the combustion chamber 2b moves to the drying chamber 2a side together with the fluid medium F, and is used for drying the wet biomass M in the drying chamber 2a.

燃焼室2bには、乾燥バイオマスの燃焼灰を排出するための燃焼灰排出路R6が接続される。乾燥バイオマスの燃焼に伴って発生した燃焼灰(焼却灰)は、燃焼灰排出路R6を介して燃焼室2bの外に排出される。   A combustion ash discharge path R6 for discharging the combustion ash of dry biomass is connected to the combustion chamber 2b. The combustion ash (incineration ash) generated along with the combustion of the dry biomass is discharged out of the combustion chamber 2b via the combustion ash discharge passage R6.

集塵機3は、過熱蒸気排出路R3に設けられる。集塵機3は、過熱蒸気排出路R3内を流通する過熱蒸気に混入した煤塵を回収する。   The dust collector 3 is provided in the superheated steam discharge passage R3. The dust collector 3 collects the dust mixed in the superheated steam flowing through the superheated steam discharge path R3.

発電装置4は、一例としてバイナリー発電装置であり、蒸発器5、予熱器6、タービン発電機7、凝縮器8、冷却塔9及び複数のポンプP1〜P3を有する。発電装置4において、過熱蒸気排出路R3を流通する過熱蒸気は、ポンプP1により蒸発器5に送られ、熱媒体循環路R7を流通する低沸点熱媒体と熱交換される。その後、過熱蒸気は、予熱器6に送られてさらに熱交換に供され、外部に放出される。蒸発器5では、低沸点熱媒体が過熱蒸気と熱交換されて気化する。気化した低沸点熱媒体は、タービン発電機7に送られて発電に供される。低沸点熱媒体は、その後、凝縮器8に送られる。低沸点熱媒体は、冷却塔9にて冷却され、かつポンプP3により流路R8を流通する冷却水と熱交換されて凝縮される。これにより、低沸点熱媒体は液化し、ポンプP2により予熱器6に送られて予熱される。その後、低沸点熱媒体は、再び蒸発器5に送られる。   The power generation device 4 is, for example, a binary power generation device, and includes an evaporator 5, a preheater 6, a turbine generator 7, a condenser 8, a cooling tower 9, and a plurality of pumps P1 to P3. In the power generation device 4, the superheated steam flowing in the superheated steam discharge passage R3 is sent to the evaporator 5 by the pump P1 and is heat-exchanged with the low boiling heat medium flowing in the heat medium circulation passage R7. Thereafter, the superheated steam is sent to the preheater 6 for further heat exchange and released to the outside. In the evaporator 5, the low boiling point heat medium is heat exchanged with the superheated steam and vaporized. The vaporized low-boiling point heat medium is sent to the turbine generator 7 to be used for power generation. The low boiling heat medium is then sent to the condenser 8. The low boiling point heat medium is cooled in the cooling tower 9 and heat-exchanged with the cooling water flowing through the flow path R8 by the pump P3 to be condensed. As a result, the low boiling point heat medium is liquefied, sent to the preheater 6 by the pump P2, and preheated. Thereafter, the low boiling heat medium is sent to the evaporator 5 again.

湿潤バイオマス焼却システム1では、乾燥室2aに供給される過熱蒸気で湿潤バイオマスMを乾燥する。これによって生成した乾燥バイオマスを流動媒体Fとともに燃焼室2bに搬送することで、燃焼室2b内で乾燥バイオマスを着火し易くし、燃焼効率が高められている。また、乾燥室2aに供給される過熱蒸気の温度は、流動床2cの温度が乾燥バイオマスの熱分解温度未満になるよう設定されている。この過熱蒸気の温度は、適宜設定できるが、例えば、流動床2cの温度が100℃以上150℃以下となる範囲に設定できる。また、ここで言う「熱分解未満」の温度とは、乾燥室2a内の乾燥バイオマスが全く熱分解されない厳密な温度に限定されず、若干の熱分解を許容する温度(過熱蒸気排出路R3を流通するガス中の水蒸気以外の成分の濃度が数%以下となる温度)に設定できる。このように流動床2cの温度を乾燥バイオマスの熱分解温度未満に設定することにより、乾燥室2a内での乾燥バイオマスの熱分解が防止され、乾燥バイオマスの熱分解に伴って発生するガスが、乾燥室2aから過熱蒸気排出路R3を流通する過熱蒸気に混入するのが防止される。また、焼却炉2では、乾燥室2aの空間S1と、燃焼室2bの空間S2とが区画壁2eで区画されているので、乾燥室2aから過熱蒸気排出路R3を流通する過熱蒸気に燃焼室2b内の燃焼ガスが混入するのが抑制されている。よって、発電装置4に高純度の過熱蒸気を供給できる。このように、高純度の過熱蒸気が発電装置4に供給されるので、過熱蒸気排出路R3を流通するガスのほぼ全てを用いて発電装置4で熱回収することができる。これにより、例えば特許文献1のように、凝縮器やスクラバーを用いて、発電装置4に供給するガスの不純物成分(過熱蒸気以外の成分)を予め除去することによりガスを精製する工程が不要である。よって、湿潤バイオマス焼却システム1では、熱回収の損失を抑制しながら、過熱蒸気の豊富な潜熱を有効に利用して、高い発電効率で安定して発電できる。   In the wet biomass incineration system 1, the wet biomass M is dried with superheated steam supplied to the drying chamber 2a. By conveying the dried biomass produced thereby to the combustion chamber 2b together with the fluid medium F, the dried biomass is easily ignited in the combustion chamber 2b, and the combustion efficiency is enhanced. Moreover, the temperature of the superheated steam supplied to the drying chamber 2a is set so that the temperature of the fluidized bed 2c becomes lower than the thermal decomposition temperature of the dry biomass. Although the temperature of this superheated steam can be set suitably, it can set to the range from which the temperature of the fluidized bed 2c becomes 100 to 150 degreeC, for example. In addition, the temperature of “below pyrolysis” as used herein is not limited to a strict temperature at which dry biomass in the drying chamber 2a is not pyrolyzed at all, and a temperature that allows some pyrolysis (the superheated steam discharge path R3 It can be set to a temperature at which the concentration of components other than water vapor in the circulating gas is several percent or less. Thus, by setting the temperature of the fluidized bed 2c to less than the thermal decomposition temperature of the dry biomass, thermal decomposition of the dry biomass in the drying chamber 2a is prevented, and the gas generated along with the thermal decomposition of the dry biomass is Mixing into the superheated steam flowing through the superheated steam discharge path R3 from the drying chamber 2a is prevented. In the incinerator 2, since the space S1 of the drying chamber 2a and the space S2 of the combustion chamber 2b are partitioned by the partition wall 2e, the combustion chamber is transferred from the drying chamber 2a to the superheated steam flowing through the superheated steam discharge path R3. It is suppressed that the combustion gas in 2b mixes. Therefore, the superheated steam of high purity can be supplied to the power generation device 4. As described above, since the superheated steam of high purity is supplied to the power generation device 4, the heat recovery of the power generation device 4 can be performed using almost all of the gas flowing through the superheated steam discharge passage R3. Thus, as in Patent Document 1, for example, the step of purifying the gas by removing in advance the impurity components (components other than the superheated steam) of the gas supplied to the power generation device 4 using a condenser or a scrubber is unnecessary. is there. Therefore, the wet biomass incineration system 1 can stably generate electric power with high power generation efficiency by effectively using the latent heat rich in superheated steam while suppressing the loss of heat recovery.

なお、一般にキルン式の乾燥機では、所定時間内で湿潤バイオマスを乾燥させるため、湿潤バイオマスを乾燥させる乾燥用ガスをかなり高温に設定する必要がある。これに対し、内部循環流動層式の焼却炉2を備える湿潤バイオマス焼却システム1では、湿潤バイオマスMを流動媒体Fと混合することで湿潤バイオマスM及び過熱蒸気の接触効率を高め、湿潤バイオマスMを効率よく乾燥できる。従って、乾燥室2aに供給される過熱蒸気の温度が、乾燥バイオマスの熱分解温度未満に設定されていても、湿潤バイオマスMを迅速且つ良好に乾燥できる。   In general, in a kiln-type dryer, in order to dry the wet biomass within a predetermined time, it is necessary to set a drying gas for drying the wet biomass to a considerably high temperature. In contrast, in the wet biomass incineration system 1 including the internal circulation fluidized bed type incinerator 2, the wet biomass M is mixed with the fluid medium F to increase the contact efficiency of the wet biomass M and superheated steam. It can dry efficiently. Therefore, even if the temperature of the superheated steam supplied to the drying chamber 2a is set below the thermal decomposition temperature of the dry biomass, the wet biomass M can be dried quickly and satisfactorily.

また、湿潤バイオマス焼却システム1では、湿潤バイオマスMを乾燥した後の過熱蒸気を過熱蒸気排出路R3に排出し、発電装置4の発電に用いることで、過熱蒸気の豊富な潜熱を利用して、高い発電効率で発電できる。また、乾燥バイオマスの熱分解に伴って生じるガスを発電に用いないので、発電装置4または排ガス流通路(過熱蒸気排出路R3)が前記ガスにより汚染され、発電効率が低下するのが防止される。従って、湿潤バイオマス焼却システム1では、良好な燃焼効率で焼却炉2を運転できるとともに、ランニングコストを低減できる。   Also, in the wet biomass incineration system 1, the superheated steam after drying the wet biomass M is discharged to the superheated steam discharge passage R3, and used for power generation of the power generation device 4, utilizing the latent heat of abundant superheated steam, It can generate power with high power generation efficiency. In addition, since the gas generated due to the thermal decomposition of dry biomass is not used for power generation, the power generation device 4 or the exhaust gas flow passage (superheated steam discharge passage R3) is prevented from being contaminated by the gas, and the power generation efficiency is not lowered. . Therefore, in the wet biomass incineration system 1, the incinerator 2 can be operated with good combustion efficiency, and the running cost can be reduced.

また、焼却炉2を乾燥室2aと燃焼室2bとを有するように一体的に構成することによって、焼却炉2をコンパクトに構成でき、その分、湿潤バイオマス焼却システム1の設備費用を抑制できる。   Further, by integrally forming the incinerator 2 so as to have the drying chamber 2a and the combustion chamber 2b, the incinerator 2 can be configured compactly, and the equipment cost of the wet biomass incineration system 1 can be suppressed.

なお、第1実施形態における湿潤バイオマス焼却システム1では、ポンプP1及び予熱器6は省略することもできる。   In the wet biomass incineration system 1 according to the first embodiment, the pump P1 and the preheater 6 can be omitted.

以下、本発明のその他の各実施形態について、第1実施形態との差異を中心に説明する。   Hereinafter, each other embodiment of the present invention will be described focusing on differences from the first embodiment.

(第2実施形態)
図2は、第2実施形態に係る湿潤バイオマス焼却システム1の一部を示す図である。図2に示すように、湿潤バイオマス焼却システム1は、焼却炉2に接続され、湿潤バイオマスMを乾燥室2a内に直接供給する第1の湿潤バイオマス供給路としての湿潤バイオマス供給路R1と、過熱蒸気排出路R3に接続され、湿潤バイオマスMを過熱蒸気排出路R3の一部を経由して乾燥室2a内に供給する第2の湿潤バイオマス供給路R1aと、をさらに備える。焼却炉2は、互いに離間して設けられた複数の湿潤バイオマス供給口2a1を有する。第1の湿潤バイオマス供給路R1と第2の湿潤バイオマス供給路R1aとは、個別に湿潤バイオマス供給口2a1に接続される。これにより、焼却炉2では、複数の位置から乾燥室2a内に湿潤バイオマスMが供給される。
Second Embodiment
FIG. 2 is a view showing a part of the wet biomass incineration system 1 according to the second embodiment. As shown in FIG. 2, the wet biomass incineration system 1 is connected to an incinerator 2, a wet biomass supply path R <b> 1 as a first wet biomass supply path that supplies wet biomass M directly into the drying chamber 2 a, and overheating. A second wet biomass supply path R1a connected to the steam discharge path R3 and supplying the wet biomass M into the drying chamber 2a via a part of the superheated steam discharge path R3 is further provided. The incinerator 2 has a plurality of wet biomass feed ports 2a1 provided apart from each other. The first wet biomass supply path R1 and the second wet biomass supply path R1a are individually connected to the wet biomass supply port 2a1. Thereby, in the incinerator 2, the wet biomass M is supplied into the drying chamber 2a from a plurality of positions.

このように、第1の湿潤バイオマス供給路R1と第2の湿潤バイオマス供給路R1aとを通じて、複数の位置から湿潤バイオマスMを乾燥室2a内に分散して供給することで、例えば、乾燥室2a内で湿潤バイオマスMを搬送する際にも、湿潤バイオマスMを過熱蒸気で効率よく迅速に乾燥して、乾燥バイオマスを生成できる。また、乾燥室2a内で局所的に湿潤バイオマスMが堆積して炉床2iへの負荷が増大するのを防止することもできる。なお、第1の湿潤バイオマス供給路R1と第2の湿潤バイオマス供給路R1aとのいずれかには、乾燥室2a内への湿潤バイオマスMの供給を促進する目的で、スクリューコンベヤまたはモーノポンプを配設してもよい。   Thus, for example, the drying chamber 2a can be provided by dispersing and supplying the wet biomass M from the plurality of positions into the drying chamber 2a through the first wet biomass supply passage R1 and the second wet biomass supply passage R1a. Even when transporting the wet biomass M, the wet biomass M can be efficiently and rapidly dried with superheated steam to produce dry biomass. In addition, it is possible to prevent the deposition of the wet biomass M locally in the drying chamber 2a and an increase in the load on the hearth 2i. A screw conveyor or a mono pump is disposed in any of the first wet biomass supply passage R1 and the second wet biomass supply passage R1a for the purpose of promoting the supply of the wet biomass M into the drying chamber 2a. You may

なお、第2の湿潤バイオマス供給路R1aは、過熱蒸気排出路R3に接続せずに、湿潤バイオマス供給口2a1に直接接続してもよい。   The second wet biomass feed passage R1a may be directly connected to the wet biomass feed port 2a1 without being connected to the superheated steam discharge passage R3.

(第3実施形態)
図3は、第3実施形態に係る湿潤バイオマス焼却システム1の一部を示す図である。図3に示すように、焼却炉2は、乾燥室2a近傍における燃焼室2b側の流動床2dの内部に、流動床2dの下方(炉床2i)から流動床2dの層高よりも低い高さまで延びるように設けられた仕切壁2kをさらに有する。一例として、仕切壁2kの板面は、区画壁2eの板面と間隔をおいて対向配置される。区画壁2eは、仕切壁2kよりも乾燥室2aに近接する位置に設けられる。これにより、焼却炉2の内部の中央には、区画壁2eと仕切壁2kとで挟まれた中間域Aが形成される。
Third Embodiment
FIG. 3 is a diagram showing a part of the wet biomass incineration system 1 according to the third embodiment. As shown in FIG. 3, the incinerator 2 has a height lower than the bed height of the fluidized bed 2d from the bottom of the fluidized bed 2d (furnace floor 2i) inside the fluidized bed 2d on the combustion chamber 2b side in the vicinity of the drying chamber 2a. It further has a partition wall 2k provided so as to extend. As an example, the plate surface of the partition wall 2k is disposed to face the plate surface of the partition wall 2e at a distance. The partition wall 2e is provided at a position closer to the drying chamber 2a than the partition wall 2k. As a result, in the center of the interior of the incinerator 2, an intermediate area A sandwiched between the partition wall 2e and the partition wall 2k is formed.

このような仕切壁2kを用いることで、燃焼室2b内の燃焼ガスまたは酸化性ガスが乾燥室2a内に流入し、燃焼ガスまたは酸化性ガスが過熱蒸気に混入するのを一層防止できる。従って、発電装置4では、過熱蒸気の豊富な潜熱を利用して発電を行えるので、発電装置4の発電効率を向上できる。なお、第3実施形態では、乾燥室2a内の気圧を燃焼室2b内の気圧よりも高くし、仕切壁2kと区画壁2eの中間域Aを通じて、乾燥室2a内の過熱蒸気の一部を燃焼室2bに流入させるように図ることで、乾燥室2a内の過熱蒸気に燃焼ガスまたは酸化性ガスが混入するのを一層防止できる。   By using such a partition wall 2k, it is possible to further prevent the combustion gas or the oxidizing gas in the combustion chamber 2b from flowing into the drying chamber 2a and the combustion gas or the oxidizing gas from being mixed in the overheated vapor. Therefore, since the power generation device 4 can generate power using the latent heat rich in superheated steam, the power generation efficiency of the power generation device 4 can be improved. In the third embodiment, the air pressure in the drying chamber 2a is made higher than the air pressure in the combustion chamber 2b, and a part of the superheated steam in the drying chamber 2a is made through the intermediate area A of the partition wall 2k and the partition wall 2e. By inflowing into the combustion chamber 2b, it is possible to further prevent the combustion gas or the oxidizing gas from being mixed in the overheated vapor in the drying chamber 2a.

(第4実施形態)
図4は、第4実施形態に係る湿潤バイオマス焼却システム1の一部を示す図である。図4に示すように、焼却炉2は、風箱2fが複数に分割された分割室2f1、2f2、2f3を有する。過熱蒸気供給路R2は、複数に分岐する複数の過熱蒸気供給分岐路(以下、単に分岐路という。)R2a、R2b、R2cを有する。分割室2f1、2f2、2f3には、分岐路R2a、R2b、R2cが順に接続される。分岐路R2a、R2b、R2cには、バルブV1、V2、V3が順に設けられる。このバルブV1、V2、V3を調節することで、分岐路R2a、R2b、R2c同士における各蒸気流量が、互いに異なるように設定される。
Fourth Embodiment
FIG. 4 is a diagram showing a part of the wet biomass incineration system 1 according to the fourth embodiment. As shown in FIG. 4, the incinerator 2 has divided chambers 2 f 1, 2 f 2 and 2 f 3 in which the air box 2 f is divided into a plurality. The superheated steam supply path R2 has a plurality of superheated steam supply branch paths (hereinafter simply referred to as “branch paths”) R2a, R2b, and R2c. Branch paths R2a, R2b, R2c are sequentially connected to the division chambers 2f1, 2f2, 2f3. Valves V1, V2, and V3 are provided in order in the branch paths R2a, R2b, and R2c. By adjusting the valves V1, V2, and V3, the steam flow rates in the branch paths R2a, R2b, and R2c are set to be different from each other.

このように、互いに蒸気流量が異なるように設定された各分岐路R2a、R2b、R2cを分割室2f1〜2f3を介して乾燥室2aに接続することで、乾燥室2a内において、流動媒体Fと湿潤バイオマスMとを、分岐路R2a、R2b、R2cのうちで蒸気流量が多い位置から少ない位置に向けて循環移動させることができる。これにより、湿潤バイオマスMと過熱蒸気とを良好に混合し、湿潤バイオマスMの乾燥を早めることができる。ここで、例えば、燃焼室2bから離隔するにつれて蒸気流量が少なくなるようにバルブV1、V2、V3をそれぞれ調節すれば、乾燥室2a内において、流動床2cの深さ方向に循環する湿潤バイオマスM及び流動媒体Fの循環流が形成され、一層、湿潤バイオマスMの乾燥を早められると考えられる。   As described above, by connecting the branch paths R2a, R2b and R2c set so that the flow rates of the vapor are different from each other to the drying chamber 2a via the division chambers 2f1 to 2f3, the fluid medium F and the flow medium F can be The wet biomass M can be circulated and moved among the branch paths R2a, R2b, and R2c from a position where the steam flow rate is high to a position where the steam flow rate is low. Thereby, wet biomass M and superheated steam can be mixed well, and drying of wet biomass M can be accelerated. Here, for example, if the valves V1, V2, and V3 are adjusted so that the steam flow rate decreases as the distance from the combustion chamber 2b increases, the wet biomass M that circulates in the depth direction of the fluidized bed 2c in the drying chamber 2a. In addition, a circulation flow of the fluid medium F is formed, and it is considered that the drying of the wet biomass M can be further accelerated.

(第5実施形態)
図5は、第5実施形態に係る湿潤バイオマス焼却システム1の一部を示す図である。図5に示すように、過熱蒸気供給路R2は、第1過熱蒸気供給路として、乾燥室2aに接続される。湿潤バイオマス焼却システム1は、焼却炉2の乾燥室2aの側壁に接続された第2過熱蒸気供給路R9をさらに備える。第2過熱蒸気供給路R9は、流動床2cに対し、乾燥室2aから燃焼室2bに向けて、流動媒体F及び乾燥バイオマスの移動を促すように、乾燥室2a内に過熱蒸気を供給する。
Fifth Embodiment
FIG. 5 is a view showing a part of the wet biomass incineration system 1 according to the fifth embodiment. As shown in FIG. 5, the superheated steam supply passage R2 is connected to the drying chamber 2a as a first superheated steam supply passage. The wet biomass incineration system 1 further includes a second superheated steam supply passage R9 connected to the side wall of the drying chamber 2a of the incinerator 2. The second superheated steam supply path R9 supplies superheated steam into the drying chamber 2a so as to promote the movement of the fluid medium F and the dry biomass from the drying chamber 2a toward the combustion chamber 2b.

第1過熱蒸気供給路R2と第2過熱蒸気供給路R9との両方から、乾燥室2a内に過熱蒸気を供給することで、乾燥室2aの下方と側方との複数の位置から、湿潤バイオマスMに過熱蒸気を接触させることができ、湿潤バイオマスMの乾燥を早めることができる。また、第2過熱蒸気供給路R9から供給される過熱蒸気で、乾燥室2aから燃焼室2bへの流動媒体F及び乾燥バイオマスの移動を促すことで、焼却炉2内において、乾燥バイオマスを効率よく搬送できる。   By supplying superheated steam into the drying chamber 2a from both the first superheated steam supply passage R2 and the second superheated steam supply passage R9, wet biomass can be obtained from a plurality of positions below and on the side of the drying chamber 2a. M can be brought into contact with superheated steam, and drying of wet biomass M can be accelerated. In addition, the superheated steam supplied from the second superheated steam supply path R9 facilitates the movement of the fluidized medium F and the dry biomass from the drying chamber 2a to the combustion chamber 2b, so that the dry biomass is efficiently obtained in the incinerator 2. It can be transported.

(第6実施形態)
図6は、第6実施形態に係る湿潤バイオマス焼却システム1の一部を示す図である。図6に示すように、湿潤バイオマス焼却システム1は、過熱蒸気排出路R3の分岐路として、発電装置4が設けられた位置よりも上流側の過熱蒸気排出路R3から分岐し、かつ過熱蒸気を大気中に開放する開放路R10と、発電装置4を迂回するように過熱蒸気排出路R3から分岐する迂回路R11をさらに備える。開放路R10にはバルブV4が設けられ、迂回路R11にはバルブV5が設けられる。バルブV4、V5は、発電装置4に供給する過熱蒸気量を所定の一定値以下に保つために設けられる。過熱蒸気排出路R3の過熱蒸気量が前記一定値より多くなると、バルブV4、V5の少なくとも一方が作動して、過熱蒸気の一部を外部に逃がすことにより、発電装置4に送られる過熱蒸気量が一定になるように図られる。
Sixth Embodiment
FIG. 6 is a diagram showing a part of the wet biomass incineration system 1 according to the sixth embodiment. As shown in FIG. 6, the wet biomass incineration system 1 branches from the superheated steam discharge path R3 upstream of the position where the power generation device 4 is provided as a branch path of the superheated steam discharge path R3, and the superheated steam is discharged. An open path R10 that opens to the atmosphere, and a bypass R11 that branches from the superheated steam discharge path R3 so as to bypass the power generation device 4 are further provided. The open passage R10 is provided with a valve V4, and the bypass passage R11 is provided with a valve V5. The valves V4 and V5 are provided to keep the amount of superheated steam supplied to the power generation device 4 at or below a predetermined constant value. When the amount of superheated steam in the superheated steam discharge path R3 exceeds the predetermined value, at least one of the valves V4 and V5 is operated to release a part of the superheated steam to the outside, whereby the amount of superheated steam sent to the power generation device 4 Is made constant.

このように、発電装置4に流通させる過熱蒸気量が一定になるように調整することで、例えば図1に示すように、発電装置4が、過熱蒸気とは別の熱媒体を利用して発電するバイナリー発電装置等である場合においても、その応答遅れを緩和することができ、安定した発電電力を得ることができる。   Thus, by adjusting the amount of overheated steam to be circulated to the power generation device 4 to be constant, for example, as shown in FIG. 1, the power generation device 4 generates power using a heat medium different from the overheated steam. Even in the case of a binary power generation device or the like, the response delay can be alleviated and stable generated power can be obtained.

なお、開放路R10及びバルブV4と、迂回路R11及びバルブV5とは、両方設ける必要はなく、このうちの一方のみを設けてもよい。   It is not necessary to provide both the open passage R10 and the valve V4, and the detour R11 and the valve V5, and only one of them may be provided.

(第7実施形態)
図7は、第7実施形態に係る湿潤バイオマス焼却システム1の一部を示す図である。図7に示すように、湿潤バイオマス焼却システム1は、過熱蒸気供給路R2と過熱蒸気排出路R3との間に接続され、過熱蒸気排出路R3を流通する過熱蒸気の一部を過熱蒸気供給路R2に戻す過熱蒸気還流路R12をさらに備える。過熱蒸気還流路R12には、例えば、過熱蒸気を過熱蒸気供給路R2に還流するためのポンプP4が設けられる。
Seventh Embodiment
FIG. 7 is a diagram showing a part of the wet biomass incineration system 1 according to the seventh embodiment. As shown in FIG. 7, the wet biomass incineration system 1 is connected between the superheated steam supply path R2 and the superheated steam discharge path R3, and a part of the superheated steam flowing through the superheated steam discharge path R3 is superheated steam supply path. A superheated steam recirculation path R12 for returning to R2 is further provided. For example, a pump P4 for returning the superheated steam to the superheated steam supply path R2 is provided in the superheated steam return path R12.

このような過熱蒸気還流路R12とポンプP4とを用いることで、例えば、乾燥室2a内の過熱蒸気供給量が不足した場合でも、過熱蒸気還流路R12を介して過熱蒸気を乾燥室2a内に還流でき、過熱蒸気量の不足分を補うことができる。   By using the superheated steam recirculation path R12 and the pump P4, for example, even when the superheated steam supply amount in the drying chamber 2a is insufficient, the superheated steam is supplied into the drying chamber 2a via the superheated steam recirculation path R12. It is possible to reflux and make up for the shortage of superheated steam.

(第8実施形態)
図8は、第8実施形態に係る湿潤バイオマス焼却システム1の一部を示す図である。図8に示すように、湿潤バイオマス焼却システム1は、集塵機3と焼却炉2との間に接続された煤塵流通路R13をさらに備える。煤塵流通路R13は、集塵機3で回収された煤塵を燃焼室2bに供給する目的で用いられる。煤塵流通路R13を用いることにより、煤塵と、燃焼室2bで生じた乾燥バイオマスの燃焼灰とを一カ所(燃焼室2b内)に集約できる。従って、例えば、煤塵と燃焼灰との後処理に関する管理を行い易くすることができる。
Eighth Embodiment
FIG. 8 is a diagram showing a part of the wet biomass incineration system 1 according to the eighth embodiment. As shown in FIG. 8, the wet biomass incineration system 1 further includes a soot dust passage R <b> 13 connected between the dust collector 3 and the incinerator 2. The dust flow passage R13 is used to supply the dust collected by the dust collector 3 to the combustion chamber 2b. By using the dust flow passage R13, the dust and the combustion ash of the dry biomass generated in the combustion chamber 2b can be collected in one place (in the combustion chamber 2b). Therefore, for example, it is possible to facilitate management of post-processing of soot and combustion ash.

(第9実施形態)
図9は、第9実施形態に係る湿潤バイオマス焼却システム1の一部を示す図である。湿潤バイオマス焼却システム1は、過熱蒸気供給路R2から分岐して乾燥室2aに接続された過熱蒸気流通路R14をさらに備える。過熱蒸気流通路R14の乾燥室2a側の先端には、複数のノズル口を持つ不図示のノズルが取り付けられている。過熱蒸気流通路R14を流通した過熱蒸気は、乾燥室2a内で、流動床2cに向かって落下する湿潤バイオマスMに対して、分散しながら噴出される。これにより、乾燥室2a内に過熱蒸気が豊富に供給されるとともに、湿潤バイオマスMが分散されて供給される。従って、湿潤バイオマスMの乾燥不足を防止でき、湿潤バイオマスMと過熱蒸気とを効率よく接触させて乾燥を早めることができる。また、乾燥室2a内に湿潤バイオマスMが局所的に堆積するのが抑制され、炉床2iへの負荷が増大するのを防止できる。
The ninth embodiment
FIG. 9 is a view showing a part of the wet biomass incineration system 1 according to the ninth embodiment. The wet biomass incineration system 1 further includes a superheated steam flow path R14 branched from the superheated steam supply path R2 and connected to the drying chamber 2a. A nozzle (not shown) having a plurality of nozzle openings is attached to the tip of the overheated steam flow passage R14 on the drying chamber 2a side. The superheated steam that has flowed through the superheated steam flow passage R14 is ejected while being dispersed to the wet biomass M that falls toward the fluidized bed 2c in the drying chamber 2a. As a result, the superheated steam is abundantly supplied into the drying chamber 2a, and the wet biomass M is dispersed and supplied. Therefore, it is possible to prevent the damp drying of the wet biomass M, and it is possible to accelerate the drying by efficiently contacting the wet biomass M and the superheated steam. In addition, local deposition of the wet biomass M in the drying chamber 2a is suppressed, and an increase in load on the hearth 2i can be prevented.

(第10実施形態)
図10は、第10実施形態に係る湿潤バイオマス焼却システム1の一部を示す図である。焼却炉2に接続された湿潤バイオマス供給路R1は、燃焼室2b内の燃焼ガスと湿潤バイオマスMとが熱交換可能に、燃焼室2b内を経由するように設けられる。このように、湿潤バイオマス供給路R1を配置することで、乾燥室2aに供給する前に、湿潤バイオマスMを予め加熱でき、乾燥室2a内における湿潤バイオマスMの乾燥を早めることができる。よって、乾燥室2a内に供給する過熱蒸気が不足するのを防止できる。また、乾燥室2a内で湿潤バイオマスMを十分に乾燥できるために排過熱蒸気量を増加できるので、豊富な過熱蒸気を発電装置4に豊富に供給し、発電効率の向上も期待できる。
Tenth Embodiment
FIG. 10 is a view showing a part of the wet biomass incineration system 1 according to the tenth embodiment. The wet biomass supply path R1 connected to the incinerator 2 is provided so that the combustion gas in the combustion chamber 2b and the wet biomass M pass through the combustion chamber 2b so that heat exchange is possible. Thus, by arranging the wet biomass supply path R1, the wet biomass M can be preheated before being supplied to the drying chamber 2a, and the drying of the wet biomass M in the drying chamber 2a can be accelerated. Therefore, it is possible to prevent a shortage of superheated steam supplied into the drying chamber 2a. Moreover, since the amount of exhaust superheated steam can be increased because the wet biomass M can be sufficiently dried in the drying chamber 2a, abundant superheated steam can be supplied to the power generation device 4 and improvement in power generation efficiency can be expected.

なお、本発明は、前述した実施形態に限定されるものではなく、本発明の趣旨を逸脱しない範囲でその構成を変更、追加、又は削除することができる。前記各実施形態は、互いに任意に組み合わせてもよく、例えば1つの実施形態中の一部の構成を、他の実施形態に適用してもよい。   The present invention is not limited to the embodiments described above, and the configuration can be changed, added, or deleted without departing from the spirit of the present invention. The above embodiments may be arbitrarily combined with each other. For example, a part of the configuration in one embodiment may be applied to another embodiment.

湿潤バイオマス焼却システム1は、過熱蒸気排出路R3を流通する水蒸気の濃度測定器と、過熱蒸気排出路R3を流通するガスを加圧する加圧装置(一例として、ファンまたはブロア)と、前記濃度測定器及び前記加圧装置に接続された制御部とを備えていてもよい。これにより、過熱蒸気排出路R3を流通するガス中の水蒸気の濃度が一定以下に低下した場合に、前記制御部が前記加圧装置を作動させて過熱蒸気排出路R3を流通するガス中の水蒸気分圧を上昇させ、発電装置4で安定して発電できるように図ることもできる。   The wet biomass incineration system 1 includes a concentration measuring device for water vapor flowing through the superheated steam discharge passage R3, a pressurizing device (for example, a fan or blower) for pressurizing the gas flowing through the superheated steam discharge passage R3, and the concentration measurement And a controller connected to the pressure device. As a result, when the concentration of water vapor in the gas flowing through the superheated steam discharge passage R3 falls below a certain level, the control unit operates the pressurizing device to cause water vapor in the gas flowing through the superheated steam discharge passage R3. It is also possible to increase the partial pressure so that the power generation device 4 can stably generate power.

F 流動媒体
M 湿潤バイオマス
R1 湿潤バイオマス供給路(第1の湿潤バイオマス供給路)
R1a 第2の湿潤バイオマス供給路
R2 過熱蒸気供給路(第1過熱蒸気供給路)
R2a、R2b、R2c 過熱蒸気供給分岐路
R3 過熱蒸気排出路
R4 酸化性ガス供給路
R9 第2過熱蒸気供給路
R10 開放路
R12 過熱蒸気還流路
R13 煤塵流通路
R14 過熱蒸気流通路
S1 乾燥室の空間
S2 燃焼室の空間
V4、V5 低圧バルブ
2 焼却炉
2a 乾燥室
2a1 湿潤バイオマス供給口
2b 燃焼室
2c、2d 流動床
2e 区画壁
2k 仕切壁
3 集塵機
4 発電装置
5 蒸発器(熱交換器)
6 予熱器(熱交換器)
7 発電機
F Flowing medium M Wet biomass R1 Wet biomass feed path (first wet biomass feed path)
R1a second wet biomass feed line R2 superheated steam supply line (first superheated steam supply line)
R2a, R2b, R2c Superheated steam supply branch R3 Superheated steam discharge R4 Oxidizing gas supply R9 Second superheated steam supply R10 Open R12 Superheated steam return R13 Dust dust flow R14 Superheated steam flow S1 Space of drying chamber S2 Combustion chamber space V4, V5 Low pressure valve 2 Incinerator 2a Drying chamber 2a1 Wet biomass supply port 2b Combustion chamber 2c, 2d Fluidized bed 2e Partition wall 2k Partition wall 3 Dust collector 4 Power generator 5 Evaporator (heat exchanger)
6 Preheater (heat exchanger)
7 Generator

Claims (12)

炉床の上方の空間が区画壁で区画されてなる乾燥室及び燃焼室を有し、かつ前記乾燥室内の下方と前記燃焼室内の下方とにわたって、流動媒体が流動する流動床が設けられた焼却炉と、
前記焼却炉の排ガスを用いて発電する発電装置と、
前記乾燥室側の前記流動床の下方に接続され、前記乾燥室内で湿潤バイオマスを前記流動媒体と混合しながら乾燥するための過熱蒸気を前記乾燥室内に供給する過熱蒸気供給路と、
前記燃焼室側の前記流動床の下方に接続され、前記湿潤バイオマスを乾燥して生成した乾燥バイオマスを前記燃焼室内で前記流動媒体と混合しながら燃焼するための酸化性ガスを前記燃焼室内に供給する酸化性ガス供給路と、
前記乾燥室に接続され、前記湿潤バイオマスの乾燥に用いられた過熱蒸気を前記乾燥室外に排出して前記発電装置に送る過熱蒸気排出路と、を備え、
前記乾燥室内の前記流動床の温度が、前記乾燥バイオマスの熱分解温度未満に設定され、前記排ガスが、前記過熱蒸気排出路を流通する過熱蒸気となり、前記発電装置が、前記乾燥バイオマスの熱分解に伴って生じるガスを用いることなく前記過熱蒸気により発電する、湿潤バイオマス焼却システム。
An incineration having a drying chamber and a combustion chamber in which the space above the hearth is partitioned by a partition wall, and provided with a fluidized bed in which a fluid medium flows over the lower portion of the drying chamber and the lower portion of the combustion chamber. A furnace,
A power generation device that generates power using the exhaust gas of the incinerator;
A superheated steam supply path connected to the lower side of the fluidized bed on the drying chamber side and supplying superheated steam for drying while mixing wet biomass with the fluidized medium in the drying chamber;
An oxidizing gas connected to the lower side of the fluidized bed on the combustion chamber side for burning the dried biomass produced by drying the wet biomass while mixing with the fluidized medium in the combustion chamber is supplied into the combustion chamber. An oxidizing gas supply channel,
A superheated steam discharge passage connected to the drying chamber and discharging the superheated steam used for drying the wet biomass to the outside of the drying chamber,
The temperature of the fluidized bed in the drying chamber is set to be lower than the thermal decomposition temperature of the dry biomass, and the exhaust gas becomes superheated steam that circulates in the superheated steam discharge path, and the power generation device generates heat of the dry biomass. A wet biomass incineration system , which generates power by the superheated steam without using a gas generated by decomposition .
炉床の上方の空間が区画壁で区画されてなる乾燥室及び燃焼室を有し、かつ前記乾燥室内の下方と前記燃焼室内の下方とにわたって、流動媒体が流動する流動床が設けられた焼却炉と、
前記焼却炉の排ガスを用いて発電する発電装置と、
前記乾燥室側の前記流動床の下方に接続され、前記乾燥室内で湿潤バイオマスを前記流動媒体と混合しながら乾燥するための過熱蒸気を前記乾燥室内に供給する過熱蒸気供給路と、
前記燃焼室側の前記流動床の下方に接続され、前記湿潤バイオマスを乾燥して生成した乾燥バイオマスを前記燃焼室内で前記流動媒体と混合しながら燃焼するための酸化性ガスを前記燃焼室内に供給する酸化性ガス供給路と、
前記乾燥室に接続され、前記湿潤バイオマスの乾燥に用いられた過熱蒸気を前記乾燥室外に排出して前記発電装置に送る過熱蒸気排出路と、
前記焼却炉に接続され、前記湿潤バイオマスを前記乾燥室内に直接供給する第1の湿潤バイオマス供給路と、
前記過熱蒸気排出路に接続され、前記湿潤バイオマスを前記過熱蒸気排出路の一部を経由して前記乾燥室内に供給する第2の湿潤バイオマス供給路と、を備え、
前記乾燥室内の前記流動床の温度が、前記乾燥バイオマスの熱分解温度未満に設定され、前記排ガスが、前記過熱蒸気排出路を流通する過熱蒸気である、湿潤バイオマス焼却システム。
An incinerator having a drying chamber and a combustion chamber in which a space above the hearth is divided by partition walls, and a fluidizing medium flowing between the lower inside of the drying chamber and the lower inside of the combustion chamber. A furnace,
A power generation device that generates power using exhaust gas of the incinerator;
A superheated steam supply path connected below the fluidized bed on the drying chamber side and supplying superheated steam into the drying chamber for drying while mixing wet biomass with the fluid medium in the drying chamber;
It is connected to the lower part of the fluidized bed on the combustion chamber side, and supplies an oxidizing gas into the combustion chamber for burning the dry biomass generated by drying the wet biomass while mixing it with the fluid medium in the combustion chamber. The oxidizing gas supply
A superheated steam discharge path which is connected to the drying chamber and discharges the superheated steam used for drying the wet biomass out of the drying chamber and sends it to the power generation apparatus;
A first wet biomass supply path connected to the incinerator and supplying the wet biomass directly into the drying chamber;
A second wet biomass supply passage connected to the superheated steam discharge passage and supplying the wet biomass into the drying chamber via a part of the superheated steam discharge passage;
The wet biomass incineration system, wherein the temperature of the fluidized bed in the drying chamber is set to less than the thermal decomposition temperature of the dry biomass, and the exhaust gas is superheated steam flowing through the superheated steam discharge channel.
前記焼却炉は、前記乾燥室近傍の前記燃焼室側の前記流動床の内部に、前記燃焼室側の前記流動床の下方から、前記燃焼室の流動床の層高よりも低い高さまで延びるように設けられた仕切壁をさらに有する、請求項1または2に記載の湿潤バイオマス焼却システム。   The incinerator extends from the lower side of the fluidized bed on the combustion chamber side to a height lower than the bed height of the fluidized bed in the combustion chamber, inside the fluidized bed on the combustion chamber side near the drying chamber. The wet biomass incineration system according to claim 1 or 2, further comprising a partition wall provided in. 前記乾燥室に前記過熱蒸気供給路が複数接続され、いずれかの前記過熱蒸気供給路同士の蒸気流量が異なっている、請求項1〜3のいずれか1項に記載の湿潤バイオマス焼却システム。   The wet biomass incineration system according to any one of claims 1 to 3, wherein a plurality of the superheated steam supply paths are connected to the drying chamber, and a steam flow rate of any of the superheated steam supply paths is different. 前記乾燥室内で、前記湿潤バイオマス及び前記流動媒体が循環するように、複数の前記過熱蒸気供給路の蒸気流量が設定されている、請求項4に記載の湿潤バイオマス焼却システム。   The wet biomass incineration system according to claim 4, wherein steam flow rates of the plurality of superheated steam supply paths are set such that the wet biomass and the fluid medium circulate in the drying chamber. 前記過熱蒸気供給路は、第1過熱蒸気供給路であり、
前記乾燥室の側壁に接続され、前記流動床に対し、前記乾燥室から前記燃焼室に向けて前記流動媒体及び前記乾燥バイオマスの移動を促すように前記乾燥室内に過熱蒸気を供給する第2過熱蒸気供給路をさらに備える、請求項1〜5のいずれか1項に記載の湿潤バイオマス焼却システム。
The superheated steam supply path is a first superheated steam supply path,
A second superheater connected to a side wall of the drying chamber and supplying superheated steam into the drying chamber so as to promote movement of the fluid medium and the dried biomass from the drying chamber toward the combustion chamber. The wet biomass incineration system according to any one of claims 1 to 5, further comprising a steam supply channel.
前記発電装置は、前記過熱蒸気排出路を流通する過熱蒸気と熱媒体とが熱交換する熱交換器と、前記熱交換器に接続され、前記熱媒体により発電する発電機とを有するバイナリー発電装置である、請求項1〜6のいずれか1項に記載の湿潤バイオマス焼却システム。   The power generating apparatus is a binary power generating apparatus including: a heat exchanger in which the overheated steam flowing through the overheated vapor discharge path exchanges heat with a heat medium; and a generator connected to the heat exchanger and generating electricity from the heat medium The wet biomass incineration system according to any one of claims 1 to 6, which is 前記過熱蒸気排出路から前記発電装置を迂回するように分岐する迂回路と、前記過熱蒸気排出路の前記発電装置が設けられた位置よりも上流側から分岐し、かつ前記過熱蒸気排出路を流通した過熱蒸気を大気中に開放する開放路とのいずれかを含む分岐路をさらに備え、
前記分岐路には、前記発電装置に供給する過熱蒸気量を一定にするためのバルブが設けられている、請求項7に記載の湿潤バイオマス焼却システム。
A detour that branches to bypass the power generation device from the superheated steam discharge channel, and a branch from the upstream side of the position where the power generation device of the superheated steam discharge channel is provided, and flows through the superheated steam discharge channel Further comprising a branch path including one of an open path for opening the overheated steam to the atmosphere,
The wet biomass incineration system according to claim 7, wherein a valve for making the amount of superheated steam supplied to the power generation device constant is provided in the branch path.
前記過熱蒸気供給路と前記過熱蒸気排出路との間に接続され、前記過熱蒸気排出路を流通する過熱蒸気の一部を前記過熱蒸気供給路に戻す過熱蒸気還流路をさらに備える、請求項1〜8のいずれか1項に記載の湿潤バイオマス焼却システム。   The superheated steam recirculation path which is connected between the superheated steam supply path and the superheated steam discharge path, and returns a part of the superheated steam flowing through the superheated steam discharge path to the superheated steam supply path. The wet biomass incineration system according to any one of -8. 前記過熱蒸気排出路の途中に設けられ、過熱蒸気に含まれる煤塵を回収する集塵機と、
前記集塵機と前記焼却炉の間に接続され、前記集塵機で回収された煤塵を前記燃焼室に戻す煤塵流通路と、をさらに備える、請求項1〜9のいずれか1項に記載の湿潤バイオマス焼却システム。
A dust collector provided in the middle of the superheated steam discharge path for collecting soot contained in the superheated steam,
The wet biomass incineration according to any one of claims 1 to 9, further comprising: a dust flow passage connected between the dust collector and the incinerator and returning the dust collected by the dust collector to the combustion chamber. system.
前記過熱蒸気供給路から分岐して前記乾燥室に接続された過熱蒸気流通路をさらに備え、
前記過熱蒸気流通路を流通した過熱蒸気が、前記乾燥室内で、前記流動床に向かって落下する前記湿潤バイオマスに対して分散しながら噴出される、請求項1〜10のいずれか1項に記載の湿潤バイオマス焼却システム。
It further comprises a superheated steam flow passage branched from the superheated steam supply passage and connected to the drying chamber,
The superheated steam which distribute | circulated the said superheated steam flow channel | path is spouted in the said drying chamber, disperse | distributing with respect to the said wet biomass falling toward the said fluidized bed. Wet biomass incineration system.
前記焼却炉に接続され、前記乾燥室に前記湿潤バイオマスを供給する湿潤バイオマス供給路をさらに備え、
前記湿潤バイオマス供給路は、前記燃焼室内を経由して設けられている、請求項1〜11のいずれか1項に記載の湿潤バイオマス焼却システム。
It further comprises a wet biomass supply path connected to the incinerator and supplying the wet biomass to the drying chamber,
The wet biomass incineration system according to any one of claims 1 to 11, wherein the wet biomass supply path is provided via the combustion chamber.
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