JP2005211805A - Method for producing ethanol in waste incineration facility - Google Patents

Method for producing ethanol in waste incineration facility Download PDF

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JP2005211805A
JP2005211805A JP2004022450A JP2004022450A JP2005211805A JP 2005211805 A JP2005211805 A JP 2005211805A JP 2004022450 A JP2004022450 A JP 2004022450A JP 2004022450 A JP2004022450 A JP 2004022450A JP 2005211805 A JP2005211805 A JP 2005211805A
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waste
ethanol
treatment
waste incineration
incineration facility
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Yoshio Nakayama
善雄 中山
Teruhisa Yoshida
輝久 吉田
Hideaki Hamada
英明 浜田
Yasuyuki Okuno
泰幸 奥野
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Hitachi Kiden Kogyo 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
    • Y02E50/00Technologies for the production of fuel of non-fossil origin
    • Y02E50/10Biofuels, e.g. bio-diesel
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W30/00Technologies for solid waste management
    • Y02W30/50Reuse, recycling or recovery technologies
    • Y02W30/78Recycling of wood or furniture waste

Abstract

<P>PROBLEM TO BE SOLVED: To provide a method for producing ethanol in waste incineration facilities, in which ethanol is produced in high production efficiency and the amount of the waste to be incinerated is reduced by adopting an existing waste recovering system and existing waste incineration facilities as they are and mixing recovered woody waste with selectively recovered garbage while incinerating combustible organic matter at the same time. <P>SOLUTION: Ethanol is produced by mixing garbage in the woody waste selectively recovered from the combustible waste to be conveyed in waste incineration facilities, converting the obtained mixture into sugars, biologically converting the obtained sugars, and distilling the biologically converted sugars. <P>COPYRIGHT: (C)2005,JPO&NCIPI

Description

本発明は、廃棄物焼却施設におけるエタノール生産方法に関し、特に、既存の廃棄物焼却施設を利用して、該廃棄物焼却施設に搬入される可燃性の廃棄物より選択的に木質系廃棄物を回収し、これに生ゴミを混合した後、糖化処理、次いで生物変換処理、蒸留を行うことにより、エタノール生産効率を向上させ、かつ廃棄物焼却量の低減を図るようにした廃棄物焼却施設におけるエタノール生産方法に関するものである。   The present invention relates to a method for producing ethanol in a waste incineration facility, and in particular, using an existing waste incineration facility, selectively using wood waste from combustible waste carried into the waste incineration facility. In a waste incineration facility that improves the ethanol production efficiency and reduces the amount of waste incineration by collecting and mixing raw garbage with this, followed by saccharification, then bioconversion, and distillation The present invention relates to an ethanol production method.

従来、建築及び製材工場から排出される廃材や剪定廃棄物、稲わら、麦わら、サトウキビ、トウモロコシ等の農業系廃棄物、パルプスラッジ、繊維工場からの廃棄物、印刷或いは製本工場からの廃棄物、古紙等の木質系産業廃棄物(セルロース系廃棄物)等のバイオマス資源からエタノールを生産する方法が提案されている。
例えば、回収したバイオマス資源を加水分解或いは蒸煮して糖質原料とする糖化工程と、これを発酵させる発酵工程と、さらに蒸留にてエタノールを分離するエタノール分離工程とを経てエタノールを生産する方法、又は回収したバイオマス資源を粉砕し、水を加えてスラリー化した後、これを水の亜臨界状態乃至超臨界状態を保って、該バイオマスに含まれている多糖類を分解、糖化し、その後発酵させてエタノールを生産する方法、さらにはセルロース系廃棄物に酵素液を作用させて糖を生成する糖化工程を行い、この糖化工程で生成した糖含有液を用いて発酵を行う発酵工程、次いで酵素生産工程を経てエタノールを生産する方法等がある。
Conventionally, waste materials and pruning waste discharged from construction and lumber mills, agricultural waste such as rice straw, straw, sugarcane and corn, pulp sludge, waste from textile factories, waste from printing or bookbinding factories, A method for producing ethanol from biomass resources such as woody industrial waste (cellulosic waste) such as waste paper has been proposed.
For example, a method of producing ethanol through a saccharification step in which the recovered biomass resource is hydrolyzed or steamed to obtain a saccharide raw material, a fermentation step in which this is fermented, and an ethanol separation step in which ethanol is further separated by distillation, Alternatively, the recovered biomass resource is pulverized, and water is added to form a slurry, which is then maintained in a subcritical or supercritical state of water to decompose and saccharify the polysaccharide contained in the biomass, and then ferment A method of producing ethanol, a saccharification step in which an enzyme solution is allowed to act on cellulosic waste to produce sugar, and a fermentation step in which fermentation is performed using the sugar-containing solution produced in this saccharification step, followed by an enzyme There is a method of producing ethanol through a production process.

ところで、従来の木質系産業廃棄物(セルロース系廃棄物)からエタノールを生産する方法では、一般の生ゴミを収集する既存の廃棄物回収システムやゴミ収集車といった回収設備をそのまま採用せず、木質系廃棄物のみを分別して回収するようにした新たな回収システムを採用している。
また、木質系産業廃棄物(セルロース系廃棄物)からエタノールを生産する場合、糖化処理、発酵処理、蒸留工程でそれぞれ必要な熱エネルギを得てエタノール生産を行うため、これら各工程での加温に外部から化石燃料から生じた熱エネルギを投入するようにしている。
By the way, in the conventional method for producing ethanol from woody industrial waste (cellulosic waste), the existing waste collection system that collects general garbage and a collection facility such as a garbage collection vehicle are not used as they are, but woody. A new collection system that separates and collects only system waste is adopted.
In addition, when ethanol is produced from wood-based industrial waste (cellulosic waste), the necessary heat energy is obtained in the saccharification treatment, fermentation treatment, and distillation steps, respectively. The heat energy generated from the fossil fuel is input to the outside.

このため、この従来の木質系産業廃棄物(セルロース系廃棄物)からエタノールを生産する方法では、木質系廃棄物の新たな回収システム及び運搬費用を要し、また糖化処理、発酵処理及びエタノールの蒸留等の各工程で加温のために外部からの熱エネルギを要し、生産されるエタノールがコスト高になるという問題があった。
さらに、廃棄物処理施設に搬入される生ゴミは、含水率が時には95%以上と高いため、これを焼却させるためには、多くの熱エネルギを要するとともに、燃焼炉内の燃焼温度を低下させ、不完全燃焼となり、またデンプンやセルロースを豊富に含み、貴重なバイオマス資源であるにも関わらず焼却処分されているという問題があった。
特開平11−169188 特開2001−262162 特開2002−159954
For this reason, the conventional method for producing ethanol from woody industrial waste (cellulosic waste) requires a new recovery system and transportation cost for woody waste, and also includes saccharification, fermentation, and ethanol. In each process such as distillation, there is a problem that heat energy from the outside is required for heating and ethanol produced is expensive.
Furthermore, since the garbage contained in the waste treatment facility has a high moisture content of 95% or more, in order to incinerate it, a large amount of heat energy is required and the combustion temperature in the combustion furnace is lowered. However, there was a problem that it was incompletely burned and was incinerated despite being a precious biomass resource that contained abundant starch and cellulose.
JP-A-11-169188 JP 2001-262162 A JP 2002-159954 A

本発明は、上記従来のエタノール生産方法の有する問題点に鑑み、既存の廃棄物回収システム及び廃棄物焼却施設をそのまま採用し、回収した木質系廃棄物に生ゴミを混合して、同時に燃焼可能な有機物の焼却処理を行いつつ、エタノール生産効率を向上させ、かつ廃棄物焼却量の低減を図るようにした廃棄物焼却施設におけるエタノール生産方法を提供することを目的とする。   In view of the problems of the conventional ethanol production method described above, the present invention adopts the existing waste collection system and waste incineration facility as they are, and mixes the collected wooden waste with garbage and burns it at the same time. An object of the present invention is to provide a method for producing ethanol in a waste incineration facility that improves ethanol production efficiency and reduces the amount of waste incineration while performing incineration processing of organic matter.

上記目的を達成するため、本発明の廃棄物焼却施設におけるエタノール生産方法は、廃棄物焼却施設に搬入される可燃性の廃棄物より選択的に回収した木質系廃棄物に選択的に回収した生ゴミを混合し、糖化処理を行った後、生物変換処理及び蒸留を行って、エタノールを生産するようにしたことを特徴とする。   In order to achieve the above object, the ethanol production method in the waste incineration facility according to the present invention is a method of selectively recovering the wood waste selectively recovered from the combustible waste carried into the waste incineration facility. After mixing trash and performing saccharification treatment, biotransformation treatment and distillation are performed to produce ethanol.

この場合において、木質系廃棄物と生ゴミとの混合を、この糖化処理に適した80〜95%の含水率に調整することができる。   In this case, the mixing of the wooden waste and the garbage can be adjusted to a water content of 80 to 95% suitable for this saccharification treatment.

また、廃棄物焼却施設での廃棄物燃焼時に発生する余熱を、糖化処理、生物変換処理及び蒸留の熱源に利用することができる。   Moreover, the residual heat generated at the time of waste combustion in the waste incineration facility can be used as a heat source for saccharification treatment, bioconversion treatment and distillation.

また、廃棄物焼却施設での廃棄物燃焼時に発生する余熱を用い、糖化処理及び生物変換処理後の残留物を自燃可能な含水率まで低下させ、廃棄物焼却設備で焼却した後、その焼却灰を埋立処理又は各種資材としてリサイクルすることができる。   In addition, using the residual heat generated during the combustion of waste at the waste incineration facility, the residue after saccharification and bioconversion processing is reduced to a moisture content that can be self-combusted, incinerated at the waste incineration facility, and then the incineration ash Can be recycled as landfill or various materials.

本発明の廃棄物焼却施設におけるエタノール生産方法によれば、廃棄物焼却施設に搬入される可燃性の廃棄物より選択的に回収した木質系廃棄物に、生ゴミを混合し、糖化処理を行った後、生物変換処理及び蒸留を行って、エタノールを生産するようにしているから、廃棄物の回収システム及び廃棄物焼却施設として既存のものを使用できるので、新たな回収システム及び運搬費用を必要とすることなく、高含水率の生ゴミも木質系廃棄物と混合して焼却炉に供給することにより、炉内温度の低下を防止し、生ゴミに含まれるエタノール生産に適した成分を効率的に処理することができ、さらには廃棄物焼却施設での廃棄物焼却量の低減を図ることができる。   According to the ethanol production method in the waste incineration facility of the present invention, raw garbage is mixed with the wooden waste selectively collected from the combustible waste carried into the waste incineration facility, and saccharification treatment is performed. After that, biotransformation treatment and distillation are performed to produce ethanol, so existing waste collection systems and waste incineration facilities can be used, so new collection systems and transportation costs are required. Therefore, by mixing raw waste with a high water content with wooden waste and supplying it to the incinerator, the temperature inside the furnace can be prevented from dropping, and the components suitable for ethanol production contained in the raw waste can be efficiently used. The amount of waste incineration at a waste incineration facility can be reduced.

また、木質系廃棄物と生ゴミとの混合を、この糖化処理に適した80〜95%の含水率に調整することにより、ゴミ焼却量が減少し、炉内温度の低下を防止することが可能となり、効率的にエタノールを生産することができる。   In addition, by adjusting the mixing of wood-based waste and raw garbage to a water content of 80 to 95% suitable for this saccharification treatment, the amount of waste incineration can be reduced and the temperature in the furnace can be prevented from lowering. It becomes possible and can produce ethanol efficiently.

また、廃棄物焼却施設での廃棄物燃焼時に発生する余熱を、糖化処理、生物変換処理及び蒸留の熱源に利用することにより、他の熱源を必要としないので、エタノールの生産コストを低廉することができる。   In addition, by using the residual heat generated during the combustion of waste at a waste incineration facility as a heat source for saccharification, bioconversion and distillation, no other heat source is required, thus reducing the production cost of ethanol. Can do.

また、廃棄物焼却施設での廃棄物燃焼時に発生する余熱を用い、糖化処理及び生物変換処理後の残留物を自燃可能な含水率まで低下させ、廃棄物焼却設備で焼却した後、その焼却灰を埋立処理又は各種資材としてリサイクルすることにより、残留物乾燥のために他の熱エネルギを要しないか、又は可及的に小とすることができ、その焼却も簡易に行える。   In addition, using the residual heat generated during the combustion of waste at the waste incineration facility, the residue after saccharification and bioconversion processing is reduced to a moisture content that can be self-combusted, incinerated at the waste incineration facility, and then the incineration ash By recycling as a landfill or various materials, other thermal energy is not required for drying the residue, or it can be made as small as possible, and incineration can be easily performed.

以下、本発明の廃棄物焼却施設におけるエタノール生産方法の実施の形態を、図1に示すエタノール製造プロセスのフロー図に基づいて説明する。   Hereinafter, an embodiment of an ethanol production method in a waste incineration facility of the present invention will be described based on a flow chart of an ethanol production process shown in FIG.

廃棄物焼却施設に搬入される廃棄物としては、一般家庭から排出される生ゴミのほかに、建築及び製材工場からの廃材や剪定廃棄物、稲わら、麦わら、サトウキビ、トウモロコシ等の農業系廃棄物、パルプスラッジ、繊維工場からの廃棄物、印刷或いは製本工場からの廃棄物、古紙等の木質系産業廃棄物(セルロース系廃棄物)等がある。
このうち、木質系産業廃棄物は、バイオマス資源として利用されているが、本発明ではこの木質系産業廃棄物に、デンプンやセルロース分を豊富に含む良質な糖資源としての生ゴミをも加えて、可燃性の廃棄物としてともに既存のシステムを利用して糖化処理により、グルコース等の糖を生成処理するものである。
なお、これら可燃性の廃棄物を焼却する施設に搬入される生ゴミや木質系廃棄物等の廃棄物の収集回収システムとしては、既存のシステムを使用して収集するもので、各収集ステーションで時間もしくは場所を分けて回収することにより、新たな廃棄物回収システムの創設を必要としないものである。
As waste to be brought into the waste incineration facility, in addition to raw garbage discharged from ordinary households, agricultural waste such as waste and pruning waste from construction and sawmills, rice straw, straw, sugarcane, corn, etc. Waste, pulp sludge, waste from textile factories, waste from printing or bookbinding factories, wood-based industrial waste (cellulosic waste) such as waste paper.
Of these, wood-based industrial waste is used as a biomass resource, but in the present invention, this wood-based industrial waste is also added with raw garbage as a high-quality sugar resource rich in starch and cellulose. In addition, saccharides such as glucose are generated and processed by saccharification using existing systems as flammable waste.
In addition, the collection and collection system for waste such as garbage and wood-based waste brought into facilities that incinerate these combustible wastes is collected using existing systems. By collecting by time or place, it is not necessary to create a new waste collection system.

可燃性の廃棄物を焼却する施設に搬入、特に限定されるものではないが、例えばゴミ収集車等を用いて搬入される回収廃棄物Aは、生ゴミ・木質系廃棄物Bと、これら以外のその他の焼却廃棄物Cとが混合された状態であるが、これを廃棄物焼却施設内にて、生ゴミ・木質系廃棄物Bとその他の焼却廃棄物Cとに分類される。
その他の焼却廃棄物Cは、所要の容量を有するゴミピット1内で一時貯留し、かつ攪拌された後、焼却炉2へ送り、ここで焼却される。この焼却された焼却廃棄物Cの残渣物としての焼却灰は、灰ピット3に一時貯留された後、灰溶融設備4でスラグDとされ、建設資材等にリサイクルされるか、或いは埋め立て地において該焼却灰を埋立処分する。
Carrying in combustible waste to a facility that incinerates, but not limited, for example, recovered waste A carried in using a garbage truck, etc., is garbage / woody waste B and others The other incineration waste C is mixed and is classified into garbage / woody waste B and other incineration waste C in the waste incineration facility.
Other incineration waste C is temporarily stored in the garbage pit 1 having a required capacity and stirred, and then sent to the incinerator 2 where it is incinerated. The incinerated ash as a residue of the incinerated waste C that has been incinerated is temporarily stored in the ash pit 3 and then converted into slag D in the ash melting facility 4 and recycled to construction materials or in landfills. The incineration ash is disposed of in landfill.

この場合、生ゴミは、デンプンやセルロース分を豊富に含む良質な糖資源であるが、高含水率(95%を超える場合もある。)のため、後工程の糖化処理、生物変換処理後も、グルコース濃度が低くなるので、生産されるエタノール濃度も低く、蒸留工程での蒸留効率が悪化する。これを防ぐため、生ゴミの含水率を調整する必要がある。これは一般的に低含水率(回収物種、回収時の天候等によっても異なるが、50%以下の場合が多い。)の木質系廃棄物と、前記高含水率の生ゴミとの、それぞれ含水率を基準に混合比率を調節することで、生ゴミ・木質系廃棄物Bの含水率を糖化処理に適した80〜95%の含水率となるように調整し、エタノール生産効率が向上するようにする。
ここで、1分子のグルコースから2分子のエタノールが酵母菌により生物変換されることが既に知られている。このことから糖化処理前の原料が高含水率の場合、糖化処理によりグルコースに分解される固形物濃度が低いことを意味し、当然ながら生物変換され、生じるエタノール濃度も低濃度になる。従って、低濃度のエタノール混合溶液の蒸留を行うためには過大なエネルギが必要となる。また、糖化処理前の原料が低含水率の場合、糖化処理工程での硫酸又は酵素剤との攪拌混合が不十分になり糖化処理効率が低下する。これらのことから、高含水率の生ゴミと低含水率の木質系廃棄物を混合し、その混合物の含水率を95〜80%程度に保ち、糖化処理を行うのが望ましい。
In this case, raw garbage is a high-quality sugar resource that contains abundant starch and cellulose. However, because of its high water content (may exceed 95%), saccharification treatment and bioconversion treatment in the subsequent steps are also required. Since the glucose concentration is lowered, the ethanol concentration produced is also low, and the distillation efficiency in the distillation process is deteriorated. In order to prevent this, it is necessary to adjust the moisture content of raw garbage. This is generally low water content (depending on the type of recovered material, the weather at the time of recovery, etc., but often less than 50%) and each of the above-mentioned high-water content garbage. By adjusting the mixing ratio based on the rate, the water content of raw garbage / woody waste B is adjusted to a water content of 80-95% suitable for saccharification, so that ethanol production efficiency is improved. To.
Here, it is already known that two molecules of ethanol are bioconverted from one molecule of glucose by yeast. From this, when the raw material before the saccharification treatment has a high water content, it means that the solid matter concentration decomposed into glucose by the saccharification treatment is low, and naturally, bioconversion is performed, and the resulting ethanol concentration is also low. Therefore, excessive energy is required to perform distillation of a low-concentration ethanol mixed solution. Moreover, when the raw material before a saccharification process is a low water content, stirring and mixing with a sulfuric acid or an enzyme agent in a saccharification process process becomes inadequate, and saccharification process efficiency falls. For these reasons, it is desirable to mix saccharification treatment by mixing raw garbage with a high water content and woody waste with a low water content, keeping the water content of the mixture at about 95 to 80%.

一方、分別回収した生ゴミ・木質系廃棄物Bは、後工程で行われる糖化処理に適した大きさに、破砕機などを用いて破砕処理7を行い、この破砕処理をした生ゴミ・木質系廃棄物Bを糖化処理槽8内に供給してここで必要な糖化処理を行う。
この場合、グルコース等の糖を生成することが可能な生ゴミ・木質系廃棄物B中の生ゴミ分は、場合によっては直接糖化処理を行ってもよいが、前記建築・古紙・剪定・稲わら等の木質系廃棄物の場合は、原料の破砕処理を行い微細化する必要がある。
この糖化処理槽8で糖化処理を行う方法としては、硫酸を用いて加熱及び加圧する方法、セルラーゼ系及び/又はアミラーゼ系の酵素剤を用いる方法等があるが、これは特に限定するものではなく、酵素剤を用いる場合、原料を事前にアルカリ浸漬処理、もしくは希酸を添加し、加熱処理を行う、もしくは蒸煮爆砕処理を行うことにより、酵素反応が促進される。
On the other hand, the separated garbage / wood waste B is crushed using a crusher etc. to a size suitable for saccharification performed in the subsequent process, and this crushed garbage / wood The system waste B is supplied into the saccharification treatment tank 8 and necessary saccharification treatment is performed here.
In this case, the garbage in the garbage / woody waste B capable of producing sugar such as glucose may be subjected to direct saccharification in some cases, but the construction / used paper / pruning / rice In the case of wooden waste such as straw, it is necessary to crush the raw material to make it finer.
As a method for performing saccharification treatment in this saccharification treatment tank 8, there are a method of heating and pressurizing with sulfuric acid, a method of using a cellulase-based and / or amylase-based enzyme agent, etc., but this is not particularly limited. In the case of using an enzyme agent, the enzyme reaction is promoted by subjecting the raw material to an alkali dipping treatment or a dilute acid in advance and performing a heat treatment or a steaming explosion treatment.

この糖化処理槽8で、原料中のセルロース及び/又はデンプンがグルコースヘ糖化される。このグルコースを含んだ糖化処理後の溶液は加熱又は紫外線又はオゾン処理といった滅菌又は減菌処理がなされるが、硫酸を添加した後、加熱処理を行った場合、滅菌又は減菌処理を要しない場合もある。この滅菌又は減菌処理は、原料中の細菌が死滅又は大半が死滅すればその手法にはこだわらないが、糖化処理前に行うのが好ましい。なお、至適温度が70度以上の耐熱性酵素剤を用いた場合、特に滅菌又は減菌処理を要しない。
この糖化処理を行い、滅菌又は減菌処理されたグルコース含有溶液を、次に生物変換処理槽9内に供給し、この生物変換処理槽9でエタノール混合液に変換する。この生物変換処理槽9内では酵母菌等を用い、生物変換処理槽9内でエタノールに変換される。
エタノール発酵では、酵母菌を用いてもよいが、アルコール耐性を強めた又はエタノール生産能を高められたエタノールを生産するミュータント又は遺伝子組替え菌を使用するのも有効な手段である。
In this saccharification treatment tank 8, the cellulose and / or starch in the raw material is saccharified into glucose. The solution after saccharification treatment containing glucose is sterilized or sterilized by heating, ultraviolet ray or ozone treatment, but when sterilization or sterilization treatment is not required when sulfuric acid is added and heat treatment is performed. There is also. This sterilization or sterilization treatment is not limited to the method if the bacteria in the raw material are killed or most of them are killed, but it is preferably performed before the saccharification treatment. In addition, when a thermostable enzyme agent having an optimum temperature of 70 ° C. or higher is used, sterilization or sterilization treatment is not particularly required.
The glucose-containing solution that has been subjected to the saccharification treatment and sterilized or sterilized is then supplied into the bioconversion treatment tank 9 and converted into an ethanol mixed solution in the bioconversion treatment tank 9. In this bioconversion treatment tank 9, yeast or the like is used and is converted into ethanol in the bioconversion treatment tank 9.
In ethanol fermentation, yeast may be used, but it is also an effective means to use a mutant or genetically modified bacterium that produces ethanol with enhanced alcohol tolerance or increased ethanol production ability.

なお、生物変換処理槽9で酵母菌等のエタノール生産菌を用いた場合、エタノールEが回収されるが、本発明を用いれば、生物変換処理槽9で、乳酸生産菌を用い生分解性プラスチックの原料となる乳酸を生産することも可能である。また、同様に、本システムを用いれば、他の微生物を用い、有用物質を生産することも可能である。   In addition, when ethanol-producing bacteria such as yeast are used in the bioconversion treatment tank 9, ethanol E is recovered. However, if the present invention is used, a biodegradable plastic using lactic acid-producing bacteria is used in the bioconversion treatment tank 9. It is also possible to produce lactic acid as a raw material. Similarly, if this system is used, other microorganisms can be used to produce useful substances.

このエタノール混合液は、エタノール濃度も低いため、これを所要の濃度になるように、蒸留工程10に送られる。この蒸留工程10に送られたエタノール混合液は、ここで蒸留され、所要濃度のエタノールEとして回収される。   Since this ethanol mixed solution has a low ethanol concentration, it is sent to the distillation step 10 so as to have a required concentration. The ethanol mixed solution sent to the distillation step 10 is distilled here and recovered as ethanol E having a required concentration.

また、糖化処理槽8及び生物変換槽9内にて行われる糖化処理及び生物変換処理により発生する残留物(残渣物)Fは、高含水率であるため、そのままでは自燃しないので、自燃できる程度の所要の含水率まで低下するようにする。このため、この残留物(残渣物)Fを脱水・乾燥処理工程11に送り、ここで脱水・乾燥処理を行って自燃できる所定の含水率まで低下させた後、ゴミピット1に戻され、焼却処理される。   Moreover, since the residue (residue) F generated by the saccharification treatment and the bioconversion treatment performed in the saccharification treatment tank 8 and the bioconversion tank 9 has a high water content, it does not self-combust as it is, so that it can self-combust. To the required moisture content. For this reason, this residue (residue) F is sent to the dehydration / drying process step 11 where the dehydration / drying process is performed to reduce the moisture content to a predetermined level at which it can burn, and then returned to the garbage pit 1 for incineration. Is done.

また、エタノールの生産工程は、糖化処理、生物変換処理、蒸留の3工程に大きく分けることができるが、何れの工程でも熱エネルギを要する。このエタノール生産に要する熱源として、廃棄物焼却施設で廃棄物燃焼時に発生する余熱を利用することにより、化石燃料等の外部からのエネルギの投入を要しない又は最小に押さえることができる。
これにより、従来の技術では、主に糖化処理槽8等で発生する残留物Fの処分システムの新設、費用を要していたが、本発明のように、廃棄物焼却施設でエタノールを生産した場合、焼却、埋立処分を行ったり、又は建設資材等へリサイクルする施設を既に有しているので、新設する必要がなく、完成している処理システムを使用することができる。
さらに、廃棄物焼却施設での廃棄物燃焼時に発生する余熱を用いることにより、安価な方法で、糖化処理及び生物変換処理後の残留物を自燃可能な含水率まで低下させることができ、かつ既存の廃棄物焼却設備で焼却し、埋立処理又は各種資材としてリサイクルすることも可能である。
In addition, the ethanol production process can be broadly divided into three processes of saccharification treatment, bioconversion treatment, and distillation, but any process requires heat energy. By utilizing the residual heat generated during the combustion of the waste in the waste incineration facility as the heat source required for this ethanol production, it is not necessary or suppressed to input energy from the outside such as fossil fuel.
As a result, in the prior art, a new disposal system for the residue F generated mainly in the saccharification treatment tank 8 and the like was required, but as in the present invention, ethanol was produced in a waste incineration facility. In this case, since a facility for incineration, landfill disposal, or recycling to construction materials or the like is already provided, it is not necessary to establish a new one, and a completed processing system can be used.
Furthermore, by using the residual heat generated during waste combustion at the waste incineration facility, the residue after saccharification treatment and bioconversion treatment can be reduced to a moisture content capable of self-combustion by an inexpensive method. It is also possible to incinerate with a waste incineration facility and recycle as landfill or various materials.

この残留物Fを脱水・乾燥処理後、焼却処理されるとき、この焼却炉2で発生した余熱aは、ボイラ5で蒸気に変換され、糖化処理槽8、生物変換処理槽9、蒸留工程10、脱水・乾燥処理工程11へ送られ、ここで熱源として利用される。
なお、余熱aに変換された焼却炉2より発生した排気ガスは、排気ガス処理設備6で有害物質を除去した後、排気ガスbとして大気中に放出される。
When this residue F is subjected to incineration after dehydration and drying, the residual heat a generated in the incinerator 2 is converted into steam by the boiler 5 and is converted into a saccharification treatment tank 8, a bioconversion treatment tank 9, and a distillation step 10. Then, it is sent to the dehydration / drying process step 11 where it is used as a heat source.
The exhaust gas generated from the incinerator 2 converted into the residual heat a is released into the atmosphere as exhaust gas b after removing harmful substances by the exhaust gas treatment facility 6.

以上、本発明の廃棄物焼却施設におけるエタノール生産方法について、実施例に基づいて説明したが、本発明は上記実施例に記載した構成に限定されるものではなく、その趣旨を逸脱しない範囲において適宜その構成を変更することができるものである。   As mentioned above, although the ethanol production method in the waste incineration facility of the present invention has been described based on the examples, the present invention is not limited to the configurations described in the above examples, and appropriately within a range not departing from the gist thereof. The configuration can be changed.

以上、本発明の廃棄物焼却施設におけるエタノール生産方法は、低含水率の木質系廃棄物と高含水率の生ゴミとを、その含水率を指標に混合比率を調節し、糖化処理、生物変換処理、エタノールの蒸留工程を得ることにより、エタノール生産効率を向上させるという特性を有していることから、既存の廃棄物焼却施設を用いたエタノール生産を安価に行う用途に好適に用いることができるほか、例えば、乳酸生産菌を用いて生分解性プラスチックの原料となる乳酸を生産する用途に、また、他の微生物を用いて有用物質を生産する用途にも用いることができる。   As described above, the ethanol production method in the waste incineration facility according to the present invention adjusts the mixing ratio of woody waste with low water content and raw garbage with high water content using the water content as an index, saccharification treatment, bioconversion Since it has the characteristic of improving ethanol production efficiency by obtaining a process and a distillation process of ethanol, it can be suitably used for applications in which ethanol production using existing waste incineration facilities is inexpensive. In addition, for example, it can be used for the purpose of producing lactic acid as a raw material for biodegradable plastics using lactic acid-producing bacteria, and for the purpose of producing useful substances using other microorganisms.

廃棄物焼却施設を利用したエタノール製造プロセスのフロー図である。It is a flowchart of the ethanol manufacturing process using a waste incineration facility.

符号の説明Explanation of symbols

A 回収廃棄物
B 生ゴミ・木質系廃棄物
C その他の焼却廃棄物
D スラグ
E エタノール
a 余熱
b 排気ガス
1 ゴミピット
2 焼却炉
3 灰ピット
4 灰溶融設備
5 ボイラ
6 排気ガス処理設備
7 破砕処理
8 糖化処理槽
9 生物変換処理槽
10 蒸留工程
11 脱水・乾燥処理設備
A Recovered waste B Garbage / woody waste C Other incineration waste D Slag E Ethanol a Residual heat b Exhaust gas 1 Garbage pit 2 Incinerator 3 Ash pit 4 Ash melting equipment 5 Boiler 6 Exhaust gas treatment equipment 7 Crushing treatment 8 Saccharification treatment tank 9 Bioconversion treatment tank 10 Distillation process 11 Dehydration and drying treatment equipment

Claims (4)

廃棄物焼却施設に搬入される可燃性の廃棄物より選択的に回収した木質系廃棄物に生ゴミを混合し、糖化処理を行った後、生物変換処理及び蒸留を行って、エタノールを生産するようにしたことを特徴とする廃棄物焼却施設におけるエタノール生産方法。   Mixing garbage with wood waste selectively collected from flammable waste carried into a waste incineration facility, saccharification treatment, biotransformation treatment and distillation to produce ethanol A method for producing ethanol in a waste incineration facility characterized by the above. 木質系廃棄物と生ゴミとの混合を、この糖化処理に適した80〜95%の含水率に調整するようにしたことを特徴とする請求項1記載の廃棄物焼却施設におけるエタノール生産方法。   The method for producing ethanol in a waste incineration facility according to claim 1, wherein the mixing of the woody waste and the garbage is adjusted to a water content of 80 to 95% suitable for the saccharification treatment. 廃棄物焼却施設での廃棄物燃焼時に発生する余熱を、糖化処理、生物変換処理及び蒸留の熱源に利用するようにしたことを特徴とする請求項1又は2記載の廃棄物焼却施設におけるエタノール生産方法。   The ethanol production in the waste incineration facility according to claim 1 or 2, wherein the residual heat generated during the combustion of the waste in the waste incineration facility is used as a heat source for saccharification treatment, bioconversion treatment and distillation. Method. 廃棄物焼却施設での廃棄物燃焼時に発生する余熱を用い、糖化処理及び生物変換処理後の残留物を自燃可能な含水率まで低下させ、廃棄物焼却設備で焼却した後、その焼却灰を埋立処理又は各種資材としてリサイクルするようにしたことを特徴とする請求項1、2又は3記載の廃棄物焼却施設におけるエタノール生産方法。   Using the residual heat generated during the combustion of waste at a waste incineration facility, the residue after saccharification and bioconversion treatment is reduced to a moisture content that can be combusted, and incinerated at the waste incineration facility, and then the incineration ash is landfilled. The method for producing ethanol in a waste incineration facility according to claim 1, 2 or 3, characterized in that it is treated or recycled as various materials.
JP2004022450A 2004-01-30 2004-01-30 Method for producing ethanol in waste incineration facility Pending JP2005211805A (en)

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Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2010246421A (en) * 2009-04-13 2010-11-04 Hitachi Zosen Corp Method for producing cellulose-based ethanol in refuse incineration facility
CN103205467A (en) * 2012-01-13 2013-07-17 日立造船株式会社 Method of producing ethanol by using biomass
JP2017006891A (en) * 2015-06-26 2017-01-12 日立造船株式会社 Waste treating method for providing useful substance by using biomass in waste as raw material
EP3335809A4 (en) * 2015-08-10 2019-03-27 Hitachi Zosen Corporation Method for effectively utilizing energy in waste-incineration facility with ethanol production equipment

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2010246421A (en) * 2009-04-13 2010-11-04 Hitachi Zosen Corp Method for producing cellulose-based ethanol in refuse incineration facility
CN103205467A (en) * 2012-01-13 2013-07-17 日立造船株式会社 Method of producing ethanol by using biomass
JP2013143915A (en) * 2012-01-13 2013-07-25 Hitachi Zosen Corp Method for producing ethanol using biomass
JP2017006891A (en) * 2015-06-26 2017-01-12 日立造船株式会社 Waste treating method for providing useful substance by using biomass in waste as raw material
EP3335809A4 (en) * 2015-08-10 2019-03-27 Hitachi Zosen Corporation Method for effectively utilizing energy in waste-incineration facility with ethanol production equipment

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