JP3590884B2 - Organic waste treatment system and treatment method - Google Patents

Organic waste treatment system and treatment method Download PDF

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JP3590884B2
JP3590884B2 JP2000081757A JP2000081757A JP3590884B2 JP 3590884 B2 JP3590884 B2 JP 3590884B2 JP 2000081757 A JP2000081757 A JP 2000081757A JP 2000081757 A JP2000081757 A JP 2000081757A JP 3590884 B2 JP3590884 B2 JP 3590884B2
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carbon dioxide
organic waste
gas
fixing
dioxide gas
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JP2001259589A (en
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伯之 戸倉
隆雄 千秋
幹雄 鈴木
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Hitachi Ltd
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Hitachi Ltd
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    • CCHEMISTRY; METALLURGY
    • C12BIOCHEMISTRY; BEER; SPIRITS; WINE; VINEGAR; MICROBIOLOGY; ENZYMOLOGY; MUTATION OR GENETIC ENGINEERING
    • C12MAPPARATUS FOR ENZYMOLOGY OR MICROBIOLOGY; APPARATUS FOR CULTURING MICROORGANISMS FOR PRODUCING BIOMASS, FOR GROWING CELLS OR FOR OBTAINING FERMENTATION OR METABOLIC PRODUCTS, i.e. BIOREACTORS OR FERMENTERS
    • C12M29/00Means for introduction, extraction or recirculation of materials, e.g. pumps
    • C12M29/24Recirculation of gas
    • CCHEMISTRY; METALLURGY
    • C12BIOCHEMISTRY; BEER; SPIRITS; WINE; VINEGAR; MICROBIOLOGY; ENZYMOLOGY; MUTATION OR GENETIC ENGINEERING
    • C12MAPPARATUS FOR ENZYMOLOGY OR MICROBIOLOGY; APPARATUS FOR CULTURING MICROORGANISMS FOR PRODUCING BIOMASS, FOR GROWING CELLS OR FOR OBTAINING FERMENTATION OR METABOLIC PRODUCTS, i.e. BIOREACTORS OR FERMENTERS
    • C12M43/00Combinations of bioreactors or fermenters with other apparatus

Description

【0001】
【発明の属する技術分野】
本発明は、生ゴミ、食品加工残渣、家畜糞尿等の有機性廃棄物を微生物により発酵・分解処理を行なう有機性廃棄物処理システム及び処理方法に関する。
【0002】
【従来の技術】
従来、生ゴミ、食品加工残渣、家畜糞尿等の有機性廃棄物は焼却または埋立による処理がほとんどであった。近年、処分場の不足、ダイオキシン問題等により、廃棄物の減量化や資源リサイクルが進みつつあり、一般にバイオ式生ごみ処理機と呼ばれる、微生物の働きを利用した有機性廃棄物処理装置が、家庭用や業務用向けに普及し始めている。
【0003】
バイオ式生ごみ処理装置としては、処理後の生成物をコンポスト(堆肥)として再利用するタイプ(コンポスト化型)と、処理物をほとんど残さない超減量タイプ(消滅型)がある。しかし、コンポスト化型によって作られたコンポストは性状が不安定であったり、堆肥として完熟していないため、有効に利用されないことが多い。このため、業務用の廃棄物処理装置としては、上記消滅型のニーズが高まってきている。
【0004】
上記各有機性廃棄物処理装置において、生ごみ等の有機物が処理されると、多くは水と炭酸ガスに分解される。その分解過程で発生する炭酸ガスは処理されずに大気排出されていることが多い。現在、地球温暖化対策が緊急の課題とされており、温暖化の原因の一つである炭酸ガスについては削減または固定化することが要求されている。
【0005】
また、微生物による有機性廃棄物の発酵・分解によって発生するアンモニア、硫化水素やメチルメルカプタンなどの硫黄系物質などについては悪臭として問題となるため、例えば特開平6−271378号公報に記載されているように、脱臭装置等による臭気対策が施された処理装置が開発されてきている。しかし、このような処理装置においても、処理物や処理条件によっては脱臭が不完全になってしまうこともあった。
【0006】
【発明が解決しようとする課題】
有機性廃棄物の好気性微生物による発酵分解型処理装置において、特に処理物を水と炭酸ガスに分解する消滅型(超減量型)処理装置では、処理過程で処理物の炭素元素がすべて炭酸ガスに変換されたとすると、標準的な生ゴミ1トンあたり約180kgの炭酸ガスが発生すると推定される。ちなみに穀類100%の生ゴミでは1トン当り約600kgの炭酸ガスを発生する。日本での家庭・事業系生ゴミの年間排出量は約5,000万トン(平成8年)と言われており、これがすべて消滅型の処理装置によりすべて分解されたとすると、約900万トンの炭酸ガスが排出される。これは、日本での炭酸ガスの年間排出量(約3億トン)の3%分に相当するため、地球温暖化に対する影響が懸念される。
【0007】
また、平成8年には改正悪臭防止法が施行され、臭気指数規制に関する制度、及び悪臭の防止等についての関係者の責務が新たに規制され、処理過程で発生する臭気対策が重要な課題となってきている。
【0008】
本は発明の目的は、有機性廃棄物を微生物により発酵・分解処理すると共にその処理過程で発生する炭酸ガスの大気への排出を抑制でき、さらに前記処理過程で発生する臭気成分の外部への排出も抑制できる有機性廃棄物処理システム及び処理方法を得ることにある。
【0009】
【課題を解決するための手段】
上記目的を達成するため、本発明の特徴は、生ゴミ、食品加工残渣、家畜糞尿などの有機性廃棄物を微生物により発酵・分解処理を行ないかつ気密構造に構成された処理槽を備える有機性廃棄物処理装置と、炭酸ガスを固定化するための炭酸ガス固定化手段を有しかつ気密構造に構成された炭酸ガス固定化装置と、前記有機性廃棄物の処理過程で発生する炭酸ガスを含む有機性廃棄物処理装置内のガスを前記炭酸ガス固定化装置に供給するための手段と、前記炭酸ガス固定化装置で処理された空気を含むガスを前記有機性廃棄物処理装置の処理槽に戻すための手段とを備え、炭酸ガス固定化手段は、化学的に炭酸ガスを固定する装置である。
【0010】
上記のものにおいて、炭酸ガス固定化装置は、水酸化カルシウム溶液を充填した固定化槽と、この固定化槽内下部に設けられ、有機性廃棄物処理装置からのガスを微細気泡として吐出させるエアレーション管とを備えることが望ましい。
【0016】
【発明の実施の形態】
本発明の一実施例を図1及び図2を参照して説明する。
図は生物的炭酸ガス固定化装置を備えた有機性廃棄物処理システムであり、図において1は微生物による有機性廃棄物処理装置、2は有機性廃棄物処理装置1の処理過程で発生した炭酸ガスを固定化するための生物的炭酸ガス固定化装置である。
【0017】
有機性廃棄物処理装置1は、有機性廃棄物を発酵・分解処理する処理槽(発酵・分解槽)3、処理物(有機性廃棄物)の投入扉4、処理物を攪拌するための攪拌器5、処理を促進させるための加熱ヒーター6、処理槽3内の温度を検出するサーミスタ7、該サーミスタ7からの検出温度を基に処理槽内の温度を調節する温度調節器8などから構成される。
【0018】
処理槽3内には、処理物の水分調整材としての木材チップやおがくず等の基材(または母材)9及び発酵・分解に関与する複数の微生物が存在する種菌が充填されている。基材9は水分調整材としての役割の他、微生物の生息・増殖場所にもなる。また、発酵・分解を行う支配的な微生物としては、一般に、有酸素条件下で、かつ通常の微生物が増殖を行う温度範囲より高い温度条件下で働くことのできる好気性・好熱性のバチルス属微生物が使用される。
【0019】
発酵・分解処理の過程を説明する。まず、有機性廃棄物である生ごみ等が処理装置1の投入扉4から投入される。処理装置内の攪拌器5はその軸がチェーンベルト5aによってモーター5bと連結されており、処理物は攪拌器によって基材9と混合される。この攪拌器5の働きにより、処理物の含水率が、微生物の働きやすい 50〜60%程度となるように水分調整されると共に、攪拌により処理物全体に空気が供給されて好気条件を作り出す。さらに、攪拌と同時に処理槽3の周囲に設けられた加熱ヒータ6と、サーミスタ7及び温度調節器8により、槽内が発酵・分解を行う微生物の最適温度といわれる60℃前後(55〜65℃程度)に均一に調整され、微生物の発酵・分解が活発となる。また、処理物中に病原性などを有した有害微生物が生息していた場合、この加熱処理により死滅または不活性化させることができる。
【0020】
微生物による発酵・分解の反応過程は処理物の成分により異なるが、生ごみ中の炭水化物やタンパク質である有機物は、微生物から分泌された酵素により、それぞれブドウ糖やアミノ酸に変化し、微生物によって吸収されるか、または炭酸ガスと水等に分解される。ただし、アミノ酸の分解過程では、アンモニアや硫黄系物質が生成されることもあり、これが臭気成分となる。これら反応の一例は下記で表すことが出来る。
(炭水化物)→(ブドウ糖):C12+ 6O → 6CO + 6H
(タンパク質)→(アミノ酸):CxHyNzOp+aO→CuHvNwOq+bCO+dHO+eNH
この処理後、分解されにくい有機物や分解後に残った無機物などはコンポスト(堆肥)として利用できる。また、発酵・分解に関与した微生物が上記有機物や無機物中に生息していることからこれを種菌として使う場合もある。
【0021】
上記のように、処理後の残渣をコンポストとして再利用するタイプがコンポスト化型処理装置であり、処理後の残渣(コンポスト)がほとんど残らないまでに発酵・分解処理を行うタイプが消滅型処理装置である。両タイプとも処理過程において攪拌、加熱操作を行う点では同じある。なお、発酵・分解処理により発生した水は排水管11を通して外部に排水される。
【0022】
次に、生物的炭酸ガス固定化装置2について説明する。有機性廃棄物処理装置1内で発生した炭酸ガスを含んだガスは、エアポンプ12や給気管13などの供給手段を介して固定化装置2の培養槽14に供給される。培養槽14の材質は透明アクリルやガラスなど光透過性のあるものを使用している。培養槽14内には、炭酸ガスを固定することが可能な光合成微生物(緑色硫黄細菌、へリオバクテリア等)を存在させるか、または藻類(クロレラ、スピルリナ等)などの固定化生物を生息させる。本実施例では、培養槽14内に固定化生物15を、生長を促進させる栄養剤を含んだ液体培地(培養液)16の中に培養する構成としている。培養槽14内に導かれた給気管13の先端にはエアレーション管17を設け、このエアレーション管から微細気泡を吐出させることにより培養槽内の培養液を循環、攪拌させ、炭酸ガスを培養液中に溶解させることができる構成としている。培養槽内の固定化生物は、この炭酸ガスを利用して光合成を行う。この固定化反応は次式で示されるものが代表的であり、有機物の生産と同時に酸素も生成する。
6CO + 6HO → C12+ 6O
培養槽14内の上部には排気管18が設けられており、固定化処理によって生成した酸素や培地に溶解しきれなかった炭酸ガスを含むガスは、この排気管18を通して外部に排気される。
【0023】
また、培養槽14内の培養液や固定化生物15の排出や供給は、それぞれ培養槽の下部および上部に接続した排液管19、或いは給液管20を通して各バルブ19a,20aの開閉により行なわれる。排液管19から回収した固定化生物は飼料として利用したり、固定化生物により生産された有用物質(例えば微細藻類を使用した場合に生産される、抗菌物質、紫外線吸収物質、不飽和脂肪酸、多糖類など)をスクリーニングして利用する。
【0024】
さらに、培養槽14内では、発酵・分解処理過程において発生したアンモニアや硫黄系物質などの臭気成分が、培養槽内の培養液(液体培地)との気液接触、及び光合成微生物や藻類などの固定化生物による吸収により除去することができ、このため大きな脱臭効果が得られる。
【0025】
図3は上記本発明の一実施例における有機性廃棄物の処理フローを示した図である。
本実施例では、生ゴミ、食品加工残渣、家畜糞尿などの有機性廃棄物は、気密構造に構成された有機性廃棄物処理装置1の処理槽内に投入される。処理槽内では、処理物(廃棄物)が基材や種菌等と共に攪拌され、処理物の含水率が、微生物の働きやすい 50〜60%程度となるように水分調整されると共に、攪拌により処理物全体に空気が供給されて好気条件を作り出す。さらに、攪拌と同時に処理槽の周囲に設けられた加熱ヒータ等により槽内が発酵・分解を行う微生物の最適温度といわれる60℃前後に均一に調整し、微生物の発酵・分解が活発となるようにする。この処理後、分解されにくい有機物や分解後に残った無機物などはコンポスト(堆肥)として利用することもできる。本実施例では処理後の残渣(コンポスト)がほとんど残らないまでに発酵・分解処理を行う消滅型処理装置であり、処理過程で多量の炭酸ガスが発生するのでこの炭酸ガスを含むガスは気密構造とされた炭酸ガス固定化装置の培養槽14に供給される。培養槽内では、培養液を循環、攪拌させて、炭酸ガスを培養液中に溶解させ、培養槽内の光合成微生物や藻類などの固定化生物はこの炭酸ガスを利用して光合成を行い、炭酸ガスを固定化する。培養槽内では、発酵・分解処理過程において発生したアンモニアや硫黄系物質などの臭気成分も、培養槽内の培養液(液体培地)との気液接触、及び光合成微生物や藻類などの固定化生物による吸収により除去できる。このようにして臭気成分が除去されたガスは排気ガスとして固定化装置外(外気等)へ排出される。
【0026】
なお、臭気成分が除去された排気ガス(炭酸ガス固定化装置で処理された空気を含むガス)を外気に排出せずに、有機性廃棄物を処理している処理槽に戻すようにしても良く、このように構成すれば、外気への臭気成分の漏洩をほぼ完全に抑制することが可能となる。
【0027】
上記実施例では生物的固定化装置を使用しているが、炭酸ガスを炭酸カルシウムにすることで炭酸ガスを固定化する化学的炭酸ガス固定化装置としても良い。すなわち、有機性廃棄物の処理装置内で発生した炭酸ガスを含んだガスは、エアポンプ12により給気管13を介して固定化装置2の固定化槽(培養槽14に相当)に供給される。固定化槽内には、水酸化カルシウム溶液を充填させておき、固定化槽内下部に導かれた給気管の先端にはエアレーション管17を設け、このエアレーション管から微細気泡を吐出させる。このようにすることにより、炭酸ガスを固定化槽内の水酸化カルシウム溶液に溶解させ、化学反応させることにより固定化することができる。炭酸ガス固定化の反応は次式で表わすことができる。
Ca(OH)+ CO → CaCO + H
化学的炭酸ガス固定化装置とした場合にも図1と同様に、固定化槽内の上部に排気管18を接続し、固定化処理によって炭酸ガスが除去されたガスを、この排気管を通して外部に排気する。また、固定化槽内の水酸化カルシウム溶液の供給や炭酸カルシウムの排出は、それぞれ培養槽の上部および下部に接続した給液管20および排液管19を通して行うことができる。
【0028】
本発明の他の実施例を図4及び図5により説明する。この実施例は、炭酸ガス固定化装置内で処理された空気を、発酵・分解処理を行なっている処理槽3内に戻す通路(排気管)18を設け、処理過程で発生する臭気を外部へ放出せずに処理システム内に閉じ込めるようにしたものである。
【0029】
本実施例においても、炭酸ガスの固定化には生物的炭酸ガス固定化装置を用いている。システム構成は、微生物による有機性廃棄物処理装置1、処理過程で発生した炭酸ガスを固定化する生物的炭酸ガス固定化装置2、有機性廃棄物処理装置1において発酵・分解処理をする処理槽3と生物的炭酸ガス固定化装置2の培養槽14とを互いに連通する給気管13及び排気管18等から構成されている。
【0030】
有機性廃棄物処理装置および生物的炭酸ガス固定化装置の構成は、前記一実施例と同様であるが、固定化装置は気密構造とされ、また培養槽内で炭酸ガス固定化処理および臭気成分が除去されたガスは外部に排気されず、排気管18を通して有機性廃棄物処理装置1内の処理槽3内に再び戻される構成としている。さらに、発酵・分解を行なう処理槽も気密構造とすることにより、有機性廃棄物の発酵・分解処理過程と炭酸ガスの固定化処理過程においてガスが循環するため、固定化処理で除去できなかった炭酸ガスの固定化をより完全にすることができ、臭気の外部への排出も抑制することができる。
【0031】
【発明の効果】
本発明によれば、有機性廃棄物処理装置により発酵・分解過程で発生した炭酸ガスを、固定化装置により固定化するので、炭酸ガスの大気への排出量を削減することができる。また、固定化処理と同時に脱臭が行われるので、処理過程で発生する臭気を含む空気を外部へ排出されるのも抑えることができる効果がある。
【0032】
さらに、炭酸ガス固定化装置で処理された空気を含むガスを前記有機性廃棄物処理装置の処理槽に戻すための手段を備える本発明によれば、発酵・分解処理過程で発生する臭気を含むガスが外部に放出されず、臭気漏洩をより完全に抑制できるばかりでなく、炭酸ガスの固定化をより完全にすることができる効果もある。
【図面の簡単な説明】
【図1】本発明の有機性廃棄物処理システムの一実施例を示す断面図である。
【図2】図1の斜視図である。
【図3】本発明の有機性廃棄物処理における処理フローの例を示す図である。
【図4】本発明の有機性廃棄物処理システムの他の実施例を示す断面図である。
【図5】図4の斜視図である。
【符号の説明】
1…有機性廃棄物処理装置、2…炭酸ガス固定化装置、3…処理槽(発酵・分解槽)、4…投入扉、5…攪拌器、5a…チェーンベルト、5b…モータ、6…加熱ヒータ、7…サーミスタ、8…温度調節器、9…基材(母材)、11…排水管、12,13…供給手段(12…エアポンプ、13…給気管)、14…培養槽(固定化槽)、15…固定化生物、16…液体体培地(培養液)、17…エアレーション管、18…排気管(処理槽に戻す手段)、19…排液管、19a…排液管バルブ、20…給液管、20a…給液管バルブ。
[0001]
TECHNICAL FIELD OF THE INVENTION
The present invention relates to an organic waste treatment system and a treatment method for fermenting and decomposing organic waste such as garbage, food processing residues, and livestock manure using microorganisms.
[0002]
[Prior art]
Conventionally, organic wastes such as garbage, food processing residues, and livestock manure have been mostly treated by incineration or landfill. In recent years, due to the shortage of disposal sites, dioxin problems, etc., waste reduction and resource recycling have been progressing.Organic waste treatment equipment that uses the action of microorganisms, commonly called bio-type garbage disposal, It has begun to spread for business and business use.
[0003]
As bio-type garbage processing apparatuses, there are a type (composting type) in which a product after processing is reused as compost (compost) and an ultra-reduced type (extinction type) that hardly leaves any processed material. However, the compost made by the composting type is often not used effectively because its properties are unstable and it is not mature as compost. For this reason, there is an increasing need for the extinguishing-type waste disposal apparatus for business use.
[0004]
When organic matter such as garbage is treated in each of the above organic waste treatment apparatuses, most of the organic waste is decomposed into water and carbon dioxide gas. The carbon dioxide gas generated during the decomposition process is often discharged to the atmosphere without being treated. At present, measures against global warming are regarded as an urgent issue, and it is required to reduce or fix carbon dioxide, which is one of the causes of global warming.
[0005]
Further, ammonia and sulfur-based substances such as hydrogen sulfide and methyl mercaptan generated by fermentation and decomposition of organic wastes by microorganisms cause a problem as offensive odor, and are described in, for example, JP-A-6-271378. As described above, a processing apparatus in which odor countermeasures are taken by a deodorizing apparatus or the like has been developed. However, even with such a processing apparatus, the deodorization may be incomplete depending on the processed material and processing conditions.
[0006]
[Problems to be solved by the invention]
In an aerobic microorganism-type fermentation-decomposition type treatment device for organic waste, especially in an annihilation type (ultra-reduction type) treatment device that decomposes the treated material into water and carbon dioxide gas, all carbon elements in the treated material are carbon dioxide It is estimated that about 180 kg of carbon dioxide gas is generated per ton of standard garbage. Incidentally, 100% cereal garbage produces about 600 kg of carbon dioxide gas per ton. The annual emission of household and business garbage in Japan is said to be about 50 million tons (1996). Carbon dioxide gas is emitted. This is equivalent to 3% of the annual carbon dioxide emission in Japan (approximately 300 million tons), so there is concern about its impact on global warming.
[0007]
In addition, the revised Offensive Odor Control Law was enacted in 1996, and the odor index regulation system and the responsibilities of stakeholders for the prevention of odors were newly regulated. It has become to.
[0008]
An object of the present invention is to ferment and decompose organic waste by using microorganisms and to suppress the emission of carbon dioxide gas generated in the process to the atmosphere, and to further suppress odor components generated in the process to the outside. An object of the present invention is to provide an organic waste treatment system and a treatment method capable of suppressing discharge.
[0009]
[Means for Solving the Problems]
In order to achieve the above object, a feature of the present invention is that an organic waste including an organic waste such as garbage, food processing residue, and livestock manure is fermented and decomposed by microorganisms and has a treatment tank configured in an airtight structure. A waste treatment apparatus, a carbon dioxide fixing apparatus having a carbon dioxide fixing means for fixing carbon dioxide and having an airtight structure, and a carbon dioxide gas generated in the process of treating the organic waste. Means for supplying a gas in the organic waste treatment apparatus containing the gas to the carbon dioxide gas fixing apparatus, and a treatment tank of the organic waste treatment apparatus containing a gas containing air treated by the carbon dioxide gas fixing apparatus. And a means for fixing carbon dioxide gas. The carbon dioxide gas fixing means is a device for chemically fixing carbon dioxide gas.
[0010]
In the above, the carbon dioxide gas fixation device is provided with a fixation tank filled with a calcium hydroxide solution, and aeration provided at a lower portion of the fixation tank and discharging gas from the organic waste treatment device as fine bubbles. Preferably, a tube is provided.
[0016]
BEST MODE FOR CARRYING OUT THE INVENTION
One embodiment of the present invention will be described with reference to FIGS.
The figure shows an organic waste treatment system provided with a biological carbon dioxide fixing device. In the figure, reference numeral 1 denotes an organic waste treatment device using microorganisms, and reference numeral 2 denotes a carbon dioxide generated in a process of the organic waste treatment device 1. It is a biological carbon dioxide fixing device for fixing gas.
[0017]
The organic waste treatment apparatus 1 includes a treatment tank (fermentation / decomposition tank) 3 for fermenting / decomposing organic waste, a charging door 4 for a treated substance (organic waste), and stirring for stirring the treated substance. It comprises a heater 5, a heater 6 for accelerating the processing, a thermistor 7 for detecting the temperature in the processing tank 3, and a temperature controller 8 for adjusting the temperature in the processing tank based on the temperature detected from the thermistor 7. Is done.
[0018]
The processing tank 3 is filled with a base material (or base material) 9 such as wood chips and sawdust as a moisture adjusting material for the processed product, and a seed bacterium containing a plurality of microorganisms involved in fermentation and decomposition. The base material 9 not only functions as a water conditioning material but also serves as a place where microorganisms live and grow. In addition, dominant microorganisms that perform fermentation / decomposition generally include aerobic and thermophilic Bacillus species that can work under aerobic conditions and at a temperature higher than the temperature range in which ordinary microorganisms grow. Microorganisms are used.
[0019]
The process of the fermentation / decomposition process will be described. First, organic waste, such as garbage, is thrown in from the throw-in door 4 of the processing apparatus 1. The shaft of the stirrer 5 in the processing apparatus is connected to the motor 5b by a chain belt 5a, and the processed material is mixed with the base material 9 by the stirrer. By the function of the stirrer 5, the water content of the processed product is adjusted so that the water content of the processed product is about 50 to 60%, which is easy for microorganisms to work, and air is supplied to the entire processed product by stirring to create an aerobic condition. . Further, at the same time as the stirring, the heater 6 provided around the processing tank 3, the thermistor 7 and the temperature controller 8 allow the inside of the tank to be around 60 ° C. (55-65 ° C.) which is said to be the optimum temperature of the microorganisms that perform fermentation and decomposition. ) And the fermentation / decomposition of microorganisms becomes active. Further, when harmful microorganisms having pathogenicity or the like inhabit in the processed product, the heat treatment can kill or inactivate the harmful microorganism.
[0020]
The reaction process of fermentation / decomposition by microorganisms differs depending on the components of the processed material, but organic substances such as carbohydrates and proteins in garbage are converted into glucose and amino acids by enzymes secreted from microorganisms, and are absorbed by microorganisms Or it is decomposed into carbon dioxide and water. However, in the process of decomposing amino acids, ammonia or sulfur-based substances may be generated, and these become odor components. An example of these reactions can be shown below.
(Carbohydrate) → (glucose): C 6 H 12 O 6 + 6O 2 → 6CO 2 + 6H 2 O
(Protein) → (amino acid): CxHyNzOp + aO 2 → CuHvNwOq + bCO 2 + dH 2 O + eNH 3
After this treatment, organic substances that are hardly decomposed and inorganic substances that remain after the decomposition can be used as compost (compost). In addition, since microorganisms involved in fermentation / decomposition live in the above organic and inorganic substances, they may be used as inoculum.
[0021]
As described above, composting-type processing equipment is a type that reuses the residue after processing as compost, and an extinguishing-type processing apparatus that performs fermentation / decomposition processing until almost no residue (compost) remains after processing. It is. Both types are the same in that stirring and heating operations are performed in the process. The water generated by the fermentation / decomposition process is drained to the outside through the drain pipe 11.
[0022]
Next, the biological carbon dioxide fixing device 2 will be described. The gas containing carbon dioxide gas generated in the organic waste treatment apparatus 1 is supplied to the culture tank 14 of the immobilization apparatus 2 via supply means such as an air pump 12 and an air supply pipe 13. The material of the culture tank 14 is made of a material having optical transparency such as transparent acrylic or glass. In the culture tank 14, a photosynthetic microorganism (green sulfur bacteria, helobacteria, etc.) capable of fixing carbon dioxide gas is present, or immobilized organisms such as algae (chlorella, spirulina, etc.) are inhabited. In the present embodiment, the immobilized organism 15 is cultured in a culture medium 14 in a liquid medium (culture liquid) 16 containing a nutrient for promoting growth. An aeration tube 17 is provided at the end of the air supply tube 13 led into the culture tank 14, and the culture solution in the culture tank is circulated and agitated by discharging fine bubbles from the aeration tube, thereby causing carbon dioxide gas to be added to the culture solution. It can be dissolved in water. The immobilized organism in the culture tank performs photosynthesis using the carbon dioxide gas. This immobilization reaction is typically represented by the following formula, and oxygen is produced simultaneously with the production of organic substances.
6CO 2 + 6H 2 O → C 6 H 12 O 6 + 6O 2
An exhaust pipe 18 is provided in the upper part of the culture tank 14, and a gas containing oxygen generated by the immobilization process and carbon dioxide gas that could not be completely dissolved in the medium is exhausted to the outside through the exhaust pipe 18.
[0023]
The discharge and supply of the culture solution and the immobilized organism 15 in the culture tank 14 are performed by opening and closing the valves 19a and 20a through a drain pipe 19 or a supply pipe 20 connected to the lower and upper parts of the culture tank, respectively. It is. The immobilized organisms recovered from the drainage pipe 19 can be used as feed or useful substances produced by the immobilized organisms (for example, antibacterial substances, ultraviolet absorbing substances, unsaturated fatty acids, produced when microalgae are used). And polysaccharides).
[0024]
Furthermore, in the culture tank 14, odor components such as ammonia and sulfur-based substances generated during the fermentation / decomposition process are brought into gas-liquid contact with a culture solution (liquid medium) in the culture tank, and the odor components such as photosynthetic microorganisms and algae It can be removed by absorption by immobilized organisms, and therefore a large deodorizing effect can be obtained.
[0025]
FIG. 3 is a diagram showing a processing flow of the organic waste in the embodiment of the present invention.
In the present embodiment, organic waste such as garbage, food processing residues, livestock manure, and the like are put into the treatment tank of the organic waste treatment apparatus 1 having an airtight structure. In the treatment tank, the treated material (waste) is stirred together with the base material and the inoculum, and the water content is adjusted so that the moisture content of the treated material is about 50 to 60%, which is easy for microorganisms to work on. Air is supplied throughout the object to create aerobic conditions. Furthermore, the inside of the tank is uniformly adjusted to around 60 ° C., which is said to be the optimum temperature of the microorganisms to be fermented and decomposed, by a heater or the like provided around the treatment tank at the same time as stirring, so that the fermentation and decomposition of the microorganisms become active. To After this treatment, organic substances that are hardly decomposed and inorganic substances that remain after the decomposition can also be used as compost (compost). In this embodiment, the destruction type processing apparatus performs the fermentation / decomposition processing until almost no residue (compost) remains after the processing. Since a large amount of carbon dioxide gas is generated in the process, the gas containing the carbon dioxide gas has an airtight structure. Is supplied to the culture tank 14 of the carbon dioxide immobilization apparatus. In the culture tank, the culture solution is circulated and stirred to dissolve carbon dioxide in the culture solution, and immobilized organisms such as photosynthetic microorganisms and algae in the culture tank perform photosynthesis using the carbon dioxide gas, Immobilize the gas. In the culture tank, odor components such as ammonia and sulfur-based substances generated during the fermentation / decomposition process are also in gas-liquid contact with the culture solution (liquid medium) in the culture tank, and immobilized organisms such as photosynthetic microorganisms and algae. Can be removed by absorption. The gas from which the odor component has been removed in this way is discharged outside the fixing device (outside air or the like) as exhaust gas.
[0026]
It should be noted that the exhaust gas from which the odor component has been removed (the gas including the air processed by the carbon dioxide fixing device) may not be discharged to the outside air, but may be returned to the processing tank for processing the organic waste. With such a configuration, it is possible to almost completely suppress leakage of the odor component into the outside air.
[0027]
Although the biological immobilization device is used in the above embodiment, a chemical carbon dioxide immobilization device for immobilizing carbon dioxide gas by converting carbon dioxide gas into calcium carbonate may be used. That is, the gas containing carbon dioxide gas generated in the organic waste treatment apparatus is supplied to the immobilization tank (corresponding to the culture tank 14) of the immobilization apparatus 2 via the air supply pipe 13 by the air pump 12. The fixation tank is filled with a calcium hydroxide solution, and an aeration pipe 17 is provided at the tip of an air supply pipe led to the lower part of the fixation tank, and fine bubbles are discharged from the aeration pipe. By doing so, the carbon dioxide gas can be fixed by dissolving it in the calcium hydroxide solution in the fixing tank and causing a chemical reaction. The reaction of carbon dioxide fixation can be represented by the following equation.
Ca (OH) 2 + CO 2 → CaCO 3 + H 2 O
Also in the case of a chemical carbon dioxide fixing device, similarly to FIG. 1, an exhaust pipe 18 is connected to the upper part of the fixing tank, and the gas from which the carbon dioxide has been removed by the fixing process is passed through the exhaust pipe to the outside. Exhaust. Further, the supply of the calcium hydroxide solution and the discharge of calcium carbonate in the immobilization tank can be performed through a liquid supply pipe 20 and a drain pipe 19 connected to the upper and lower parts of the culture tank, respectively.
[0028]
Another embodiment of the present invention will be described with reference to FIGS. In this embodiment, a passage (exhaust pipe) 18 is provided for returning the air treated in the carbon dioxide fixing device to the treatment tank 3 in which the fermentation / decomposition treatment is performed, and the odor generated in the treatment process is discharged to the outside. It is intended to be trapped in the processing system without being released.
[0029]
Also in this embodiment, a biological carbon dioxide fixing device is used for fixing carbon dioxide. The system configuration includes an organic waste treatment apparatus 1 using microorganisms, a biological carbon dioxide fixation apparatus 2 for fixing carbon dioxide generated in a treatment process, and a treatment tank for performing fermentation and decomposition processing in the organic waste treatment apparatus 1. 3 and a culture tank 14 of the biological carbon dioxide fixing device 2 are constituted by an air supply pipe 13 and an exhaust pipe 18 and the like.
[0030]
The configurations of the organic waste treatment apparatus and the biological carbon dioxide fixing apparatus are the same as those in the above-described embodiment, but the fixing apparatus has an airtight structure, and the carbon dioxide fixing processing and the odor component in the culture tank. The gas from which is removed is not exhausted to the outside, but is returned to the treatment tank 3 in the organic waste treatment apparatus 1 through the exhaust pipe 18 again. Furthermore, the treatment tank for fermentation / decomposition also has an airtight structure, so that gas is circulated in the fermentation / decomposition treatment process of organic waste and the fixation treatment process of carbon dioxide gas, so that it could not be removed by immobilization treatment. The fixation of carbon dioxide gas can be made more complete, and the emission of odor to the outside can be suppressed.
[0031]
【The invention's effect】
According to the present invention, the carbon dioxide gas generated in the fermentation / decomposition process by the organic waste treatment device is fixed by the fixing device, so that the amount of carbon dioxide gas emitted to the atmosphere can be reduced. In addition, since deodorization is performed simultaneously with the immobilization process, there is an effect that air containing odor generated in the process can be prevented from being discharged to the outside.
[0032]
Further, according to the present invention, which includes means for returning the gas containing air treated by the carbon dioxide fixing device to the treatment tank of the organic waste treatment device, the gas containing odor generated during the fermentation / decomposition treatment process is included. The gas is not released to the outside, so that not only the odor leakage can be more completely suppressed, but also the carbon dioxide gas can be more completely fixed.
[Brief description of the drawings]
FIG. 1 is a sectional view showing one embodiment of an organic waste treatment system of the present invention.
FIG. 2 is a perspective view of FIG.
FIG. 3 is a diagram showing an example of a processing flow in the organic waste processing of the present invention.
FIG. 4 is a sectional view showing another embodiment of the organic waste treatment system of the present invention.
FIG. 5 is a perspective view of FIG. 4;
[Explanation of symbols]
DESCRIPTION OF SYMBOLS 1 ... Organic waste treatment apparatus, 2 ... Carbon dioxide fixation apparatus, 3 ... Processing tank (fermentation / decomposition tank), 4 ... Input door, 5 ... Stirrer, 5a ... Chain belt, 5b ... Motor, 6 ... Heating Heater, 7: Thermistor, 8: Temperature controller, 9: Base material (base material), 11: Drain pipe, 12, 13: Supply means (12: Air pump, 13: Air supply pipe), 14: Culture tank (fixed) Tank), 15: immobilized organism, 16: liquid medium (culture solution), 17: aeration pipe, 18: exhaust pipe (means for returning to the processing tank), 19: drain pipe, 19a: drain pipe valve, 20 ... Supply pipe, 20a ... Supply pipe valve.

Claims (2)

生ゴミ、食品加工残渣、家畜糞尿などの有機性廃棄物を微生物により発酵・分解処理を行ないかつ気密構造に構成された処理槽を備える有機性廃棄物処理装置と、炭酸ガスを固定化するための炭酸ガス固定化手段を有しかつ気密構造に構成された炭酸ガス固定化装置と、前記有機性廃棄物の処理過程で発生する炭酸ガスを含む有機性廃棄物処理装置内のガスを前記炭酸ガス固定化装置に供給するための手段と、前記炭酸ガス固定化装置で処理された空気を含むガスを前記有機性廃棄物処理装置の処理槽に戻すための手段とを備え、前記炭酸ガス固定化手段は、化学的に炭酸ガスを固定する装置であることを特徴とする有機性廃棄物処理システム。Organic waste treatment equipment that performs fermentation and decomposition treatment of organic waste such as garbage, food processing residue, livestock manure, etc. by microorganisms and has a treatment tank configured in an airtight structure, and to fix carbon dioxide gas A carbon dioxide gas fixing device having a carbon dioxide gas fixing means and having an airtight structure, and a gas in the organic waste treatment device containing carbon dioxide gas generated in the process of treating the organic waste, is treated with the carbon dioxide gas. and means for supplying the gas immobilization device, and means for a gas containing air which has been treated with the carbon dioxide fixing apparatus back into the treatment tank of the organic waste treatment apparatus, wherein the carbon dioxide fixing The organic waste treatment system is characterized in that the conversion means is a device for chemically fixing carbon dioxide gas . 請求項において、前記炭酸ガス固定化装置は、水酸化カルシウム溶液を充填した固定化槽と、この固定化槽内下部に設けられ、前記有機性廃棄物処理装置からのガスを微細気泡として吐出させるエアレーション管とを備えることを特徴とする有機性廃棄物処理システム。2. The carbon dioxide gas fixing device according to claim 1 , wherein the carbon dioxide gas fixing device is provided with a fixing bath filled with a calcium hydroxide solution, and a gas is discharged from the organic waste treatment device as fine bubbles provided in a lower portion of the fixing bath. An organic waste treatment system, comprising:
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