JP2005238076A - Treating method of organic residual dross - Google Patents

Treating method of organic residual dross Download PDF

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JP2005238076A
JP2005238076A JP2004050123A JP2004050123A JP2005238076A JP 2005238076 A JP2005238076 A JP 2005238076A JP 2004050123 A JP2004050123 A JP 2004050123A JP 2004050123 A JP2004050123 A JP 2004050123A JP 2005238076 A JP2005238076 A JP 2005238076A
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organic residue
organic
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crushing
liquid
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Akikazu Yamamoto
明和 山本
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Kurita Water Industries Ltd
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Abstract

<P>PROBLEM TO BE SOLVED: To provide an organic residual dross treating method in which organic residual dross is prevented from decaying and possibility of inhibiting reuse of organic debris is reduced to allow storage of the organic residual dross. <P>SOLUTION: The organic residual dross is crushed in a deoxidizing atmosphere. Actually, the organic residual dross such as tea sludge 5 is crushed in an adjusting tank 20 equipped with a crushing means composed of a cutter pump 71 or the like. Crushing is performed in deoxidizing atmosphere. For example, the tea sludge 5 is dipped into carbonic acid water 2 serving as a deoxidizing treating liquid, thereby the tea sludge 5 is crushed in the deoxidizing atmosphere. <P>COPYRIGHT: (C)2005,JPO&NCIPI

Description

本発明は、有機物残渣の処理方法に関し、特に茶滓、コーヒー滓などの固体状の植物系有機物残渣を腐敗させることなく、一定期間貯留することを可能とする植物系有機物残渣の処理方法に関する。   The present invention relates to a method for treating organic residue, and more particularly, to a method for treating a plant organic residue that can be stored for a certain period of time without decaying solid plant organic residues such as teacups and coffee lees.

従来、食品工場や飲食店、またはスーパーなどで発生する固体有機物残渣は廃棄物として焼却処理されていた。しかし、近年、廃棄物量の削減が要請されるようになってきたことから、有機物残渣を再利用することが求められるようになり、有機物残渣を再利用するための様々な方法が提案されている。有機物残渣の再利用方法としては、有機物残渣を炭化して固形燃料にする方法や、有機物残渣を微生物により分解して肥料(コンポスト)とする方法などが知られている。   Conventionally, solid organic residue generated in food factories, restaurants, supermarkets, and the like has been incinerated as waste. However, in recent years, since reduction of the amount of waste has been demanded, it has been required to reuse organic residue, and various methods for reusing organic residue have been proposed. . As a method for reusing an organic residue, a method of carbonizing the organic residue to form a solid fuel, a method of decomposing the organic residue with microorganisms to make fertilizer (compost), and the like are known.

ところで、有機物残渣は、食品工場、飲食店またはスーパーなどの多数の発生源から発生するものの、各発生源での有機物残渣の発生量は多くない。このため、有機物残渣は一定量が蓄積されるまで各発生源で貯留される。しかし、固形の有機物残渣は含水率が高く、また微小空間に空気が多く入りこむため、貯留中に微生物、特にカビが繁殖しやすい。微生物が繁殖し、さらに腐敗した有機物残渣は、再利用されにくく、また、悪臭を発生して周辺環境の衛生状態を悪化させる。   By the way, although organic residue is generated from many sources such as food factories, restaurants or supermarkets, the amount of organic residue generated at each source is not large. For this reason, organic residue is stored at each source until a certain amount is accumulated. However, the solid organic residue has a high water content and a large amount of air enters the micro space, so that microorganisms, particularly mold, are likely to propagate during storage. The organic matter residue that the microorganisms have propagated and further rotted is difficult to be reused, and generates a foul odor and deteriorates the sanitary condition of the surrounding environment.

そこで、固体有機物残渣に油脂やたんぱく質を溶解する溶剤を添加し、有機物残渣をスラリ化することにより、有機物残渣からの悪臭の発生を防いで一定期間の貯留を可能とする処理方法が提案されている(特許文献1)。特許文献1に開示された方法では、固形の有機物残渣を、一定の粒度となるように破砕および脱水した上で、リモネンのような溶剤を添加して油脂やたんぱく質を溶解して、有機物残渣をスラリ化する。スラリ化された有機物残渣は、リモネンの防腐作用により、腐敗し難く、また、流動性を有するため、取扱いやすく、貯留、収集が容易である。   Therefore, a processing method has been proposed that enables the storage of a certain period of time by preventing the generation of odors from the organic residue by adding a solvent that dissolves fats and oils to the solid organic residue and slurrying the organic residue. (Patent Document 1). In the method disclosed in Patent Document 1, a solid organic residue is crushed and dehydrated so as to have a certain particle size, and then a solvent such as limonene is added to dissolve fats and oils and proteins to remove the organic residue. Slurry. The slurried organic residue is not easily spoiled due to the antiseptic action of limonene and has fluidity, so that it is easy to handle, and can be stored and collected.

しかし、特許文献1記載の方法では、有機物残渣をスラリ化する目的で、リモネンのような溶剤を使用するため、処理コストの高騰を招く。また、有機物残渣に溶剤が適切な量で添加混合されるようにするために、有機物残渣を破砕して脱水する必要があり、処理工程が複雑になる。
特開2002−224638号公報
However, in the method described in Patent Document 1, a solvent such as limonene is used for the purpose of making an organic residue into a slurry, resulting in an increase in processing cost. Further, in order to add and mix the solvent in an appropriate amount to the organic residue, the organic residue needs to be crushed and dehydrated, which complicates the treatment process.
JP 2002-224638 A

本発明は上記のような課題に鑑みてなされたものであり、その目的は、有機物残渣の腐敗を防止し、かつ、有機物残渣の再利用を阻害しない有機物残渣の処理方法を提供することである。より具体的には、本発明は、有機物残渣からの除去が容易で、貯留後の有機物残渣の再利用を阻害しない物質を用い、有機物残渣を腐敗させずに保存することを可能とする有機物残渣の処理方法を提供することを目的とする。   This invention is made | formed in view of the above subjects, The objective is to provide the processing method of the organic substance residue which prevents the decay of an organic substance residue and does not inhibit the reuse of an organic substance residue. . More specifically, the present invention uses an organic residue that is easy to remove from the organic residue and does not inhibit the reuse of the organic residue after storage, and allows the organic residue to be stored without being spoiled. It aims at providing the processing method of.

本発明は、有機物残渣を脱酸素雰囲気下で破砕する。より具体的には、本発明は以下のようなものを提供する。   In the present invention, organic residue is crushed under a deoxygenated atmosphere. More specifically, the present invention provides the following.

(1)有機物残渣を脱酸素雰囲気下で破砕する破砕工程を含む有機物残渣の処理方法。   (1) A method for treating an organic residue including a crushing step of crushing the organic residue in a deoxygenated atmosphere.

ここで、本明細書において「有機物残渣」とは、植物、動物、または微生物由来の廃棄物であり、工業上利用可能な生物体含有成分を含む有機物を意味する。具体的には、食品加工過程で発生する茶滓、豆滓、および醸造滓などの食品加工残渣、生ゴミなどの食品残渣、並びに有機性汚泥が挙げられる。   Here, the “organic residue” in the present specification refers to an organic substance that is a plant, animal, or microorganism-derived waste and contains an organism-containing component that can be used industrially. Specifically, food processing residues such as tea cakes, bean cakes, and brewed rice cakes generated in the food processing process, food residues such as raw garbage, and organic sludge can be mentioned.

上記の有機物残渣のうち、茶滓や豆滓などの食品加工残渣であって、植物由来の植物系加工残渣には、植物性ポリフェノール類が含まれており、破砕処理によりこれらの物質を利用して腐敗防止を行なうことができる。特に、飲料製造過程で発生する茶滓は、カテキン類を多く含むため、本発明に従って処理することにより、腐敗を防止して貯留した後、種々の用途に再利用できるため、本発明の特に好適な処理対象である。   Among the above organic residue, food processing residues such as teacups and bean cakes, plant-based processing residues contain plant polyphenols, and these substances are used by crushing treatment. To prevent corruption. In particular, the tea bowl generated in the beverage production process contains a large amount of catechins, and therefore, it can be reused for various purposes after being stored according to the present invention to prevent spoilage. It is a processing target.

「脱酸素雰囲気」とは、好気性微生物の増殖が不可能な程度に脱酸素処理がされた環境であることを意味し、完全無酸素状態に限られない。具体的には、酸素を含む気体、もしくは液体が、脱酸素処理されることにより酸素濃度が1mg/L(1ppm)以下、好ましくは0.1mg/L(0.1ppm)以下とされていることを意味する。脱酸素雰囲気下で有機物残渣を破砕する方法としては、脱酸素処理した気体中、または脱酸素処理した液体中で有機物残渣を破砕する方法が挙げられる。   The “deoxygenated atmosphere” means an environment that has been deoxygenated to such an extent that aerobic microorganisms cannot grow, and is not limited to a completely oxygen-free state. Specifically, the oxygen concentration is 1 mg / L (1 ppm) or less, preferably 0.1 mg / L (0.1 ppm) or less by deoxidizing a gas or liquid containing oxygen. Means. Examples of the method for crushing the organic residue in a deoxygenated atmosphere include a method for crushing the organic residue in a deoxygenated gas or a deoxygenated liquid.

本発明においては、有機物残渣を脱酸素雰囲気下で破砕することにより、有機物残渣表面または内部に保持された酸素を除去する。固形状の有機物残渣は、酸素が除去されることにより好気性微生物が増殖しにくい状態となる。このため、本発明によれば、有機物残渣の腐敗を防止して貯留できるようになる。   In the present invention, the organic residue is crushed in a deoxygenated atmosphere to remove oxygen retained on or inside the organic residue. The solid organic residue is in a state in which aerobic microorganisms hardly grow by removing oxygen. For this reason, according to the present invention, it becomes possible to prevent and store the organic residue.

また、本発明によれば、有機物残渣を貯留する際に腐敗防止のための防腐剤などの薬品を添加する必要がないため、有機物残渣を再利用する際に、防腐剤が有機物残渣に残存することにより生じる不都合を低減できる。さらに、本発明によれば、有機物残渣を植物性ポリフェノールなどの可溶性成分の抽出がしやすく、ハンドリング性に優れた状態に改質することができる。   Further, according to the present invention, it is not necessary to add chemicals such as a preservative for preventing corruption when storing the organic residue, so that when the organic residue is reused, the preservative remains in the organic residue. Inconvenience caused by this can be reduced. Furthermore, according to the present invention, the organic residue can be easily extracted into soluble components such as plant polyphenols, and can be modified to a state excellent in handling properties.

(2)前記脱酸素雰囲気を、密閉可能な空間に不活性化ガスを充填することにより構成する(1)記載の有機物残渣の処理方法。   (2) The method for treating an organic residue according to (1), wherein the deoxygenating atmosphere is configured by filling an inert gas in a sealable space.

有機物残渣は、脱酸素処理された気体が充填された密閉空間で破砕することができる。脱酸素処理された気体の酸素濃度は、1mg/L以下であることが好ましい。脱酸素処理された気体を得る方法としては、酸素を含む気体に不活性化ガスなどを吹き込んで酸素を除去する方法、および酸素を含む気体を密閉空間に収容し、この空間に脱酸素剤を入れることにより脱酸素する方法などがある。   The organic residue can be crushed in a sealed space filled with a deoxygenated gas. The oxygen concentration of the deoxygenated gas is preferably 1 mg / L or less. As a method for obtaining a deoxygenated gas, a method of removing oxygen by blowing an inert gas or the like into a gas containing oxygen, and a gas containing oxygen in an enclosed space, and a deoxidizer in the space There is a method to deoxygenate by putting in.

これらの方法の中で、特に、不活性化ガスを充填することにより脱酸素雰囲気を作り出す方法は、脱酸素条件の制御が容易で好ましい。密閉空間に充填する不活性化ガスとしては、還元性ガスに比べて取り扱いが容易である不活性ガスを用いることが好ましい。   Among these methods, a method of creating a deoxygenated atmosphere by filling with an inert gas is particularly preferable because it is easy to control deoxygenation conditions. As the inert gas that fills the sealed space, it is preferable to use an inert gas that is easier to handle than the reducing gas.

ここで、「不活性化ガス」とは、有機物の酸化分解反応を抑制するガスを意味し、具体的には、水素ガスや一酸化炭素ガスのような還元性ガス、及び不活性ガスを意味する。また、本明細書において「不活性ガス」とは、化学反応の中でも特に酸化反応を起こしにくい気体を意味し、ヘリウム、アルゴンなどの希ガス族元素に限らず、窒素ガスおよび炭酸ガスを含む。これらの不活性化ガスのうち、炭酸ガスおよび窒素ガスは取り扱いが容易で、特に好適に使用できる。不活性化ガスは、濃度が99.9%以上のものを用いることが好ましい。   Here, “inert gas” means a gas that suppresses the oxidative decomposition reaction of organic substances, and specifically means a reducing gas such as hydrogen gas or carbon monoxide gas, and an inert gas. To do. In the present specification, “inert gas” means a gas that hardly causes an oxidation reaction among chemical reactions, and is not limited to a rare gas group element such as helium or argon, but includes nitrogen gas and carbon dioxide gas. Of these inert gases, carbon dioxide gas and nitrogen gas are easy to handle and can be used particularly preferably. It is preferable to use an inert gas having a concentration of 99.9% or more.

(3)前記破砕工程において、脱酸素処理をした脱酸素処理液に有機物残渣を浸漬して破砕する(1)記載の有機物残渣の処理方法。   (3) The organic residue processing method according to (1), wherein in the crushing step, the organic residue is immersed and crushed in a deoxygenated treatment solution that has been subjected to deoxygenation treatment.

有機物残渣は、脱酸素処理された液体(脱酸素処理液)に浸漬された状態で破砕してもよい。有機物残渣を脱酸素処理液に浸漬して破砕する場合、有機物残渣を破砕する空間は脱酸素雰囲気下でなくともよく、この空間には酸素を含有する気体が存在していてもよい。しかし、有機物残渣と脱酸素処理液を密閉空間に投入して、この空間を脱酸素雰囲気下とすると、液面からの酸素の溶け込みが防止できるため、好ましい。   The organic substance residue may be crushed in a state where it is immersed in a liquid subjected to deoxygenation treatment (deoxygenation liquid). When the organic residue is crushed by immersing it in a deoxygenation treatment solution, the space for pulverizing the organic residue need not be in a deoxygenated atmosphere, and a gas containing oxygen may exist in this space. However, it is preferable to put the organic substance residue and the deoxygenated treatment liquid into a sealed space and to put this space in a deoxygenated atmosphere because it is possible to prevent oxygen from being dissolved from the liquid surface.

ここで、「脱酸素処理液」とは、酸素を含む原水を脱酸素処理して得られる液体を意味する。脱酸素処理液の溶存酸素濃度は1mg/L以下、さらには0.1mg/L以下であることが好ましい。脱酸素処理液の原水としては市水や工業用水などを用いることができる。また、脱酸素処理としては、原水への不活性化ガスの吹き込み処理、原水を脱気膜と接触させて脱酸素処理をする脱気膜処理、および硫酸水素ナトリウム(NaHSO)などの薬剤添加処理などが挙げられる。不活性化ガスの吹き込みにより脱酸素処理液を調整する場合、吹き込み後の液体の酸素濃度が1mg/L以下、好ましくは0.1mg/L以下となるように吹き込み量や吹き込み時間などを調整することが好ましい。 Here, the “deoxygenated liquid” means a liquid obtained by deoxygenating raw water containing oxygen. The dissolved oxygen concentration in the deoxygenation treatment solution is preferably 1 mg / L or less, more preferably 0.1 mg / L or less. City water, industrial water, or the like can be used as raw water for the deoxygenated liquid. In addition, as the deoxygenation treatment, an inert gas blowing treatment into the raw water, a degassing membrane treatment in which the raw water is brought into contact with the degassing membrane, and a chemical addition such as sodium hydrogen sulfate (NaHSO 3 ) are added. Processing. When adjusting the deoxygenated treatment liquid by blowing an inert gas, the blow amount and blow time are adjusted so that the oxygen concentration of the blown liquid is 1 mg / L or less, preferably 0.1 mg / L or less. It is preferable.

脱酸素処理液は、pHが5.5以下、好ましくは3.5〜4.5であることが好ましい。酸性ないし弱酸性の酸性側脱酸素処理液は、微生物の中でも特にカビの増殖抑制効果が高く、さらに茶ポリフェノール類の保存に適している。脱酸素処理液を酸性側とするため、脱酸素処理液には必要に応じて塩酸、硫酸、および酢酸などの有機酸を添加することができる。   The deoxidation treatment liquid has a pH of 5.5 or less, preferably 3.5 to 4.5. Acidic or weakly acidic side deoxygenation treatment liquid has a particularly high fungus growth inhibitory effect among microorganisms and is suitable for preservation of tea polyphenols. In order to make the deoxygenated liquid acidic, an organic acid such as hydrochloric acid, sulfuric acid, and acetic acid can be added to the deoxygenated liquid as necessary.

脱酸素処理液としては、原水に不活性化ガスを吹き込み、原水中の溶存酸素を不活性化ガスで置換した不活性化ガス溶解水を用いることが好ましい。不活性化ガスは、曝気処理を行なうことにより容易に液中から除去できる。このため、有機物残渣を不活性化ガス溶解水に浸漬した状態で貯留した後、再利用するに際し、酸素ガスや空気を吹き込む曝気処理を行なうことにより、有機物残渣からこれらの不活性化ガスを容易に除去できる。   As the deoxidation treatment liquid, it is preferable to use an inert gas-dissolved water in which an inert gas is blown into the raw water and dissolved oxygen in the raw water is replaced with the inert gas. The inert gas can be easily removed from the liquid by performing an aeration process. For this reason, after storing the organic substance residue immersed in the inert gas-dissolved water, it is possible to easily remove the inert gas from the organic substance residue by performing an aeration process in which oxygen gas or air is blown for reuse. Can be removed.

特に、原水に炭酸ガスを吹き込んで脱酸素処理をして得られる炭酸水を脱酸素処理液として用いることが好ましい。炭酸水は、pHが4〜6であるため、微生物、特に菌類(カビ)の増殖抑制効果が高く、また、カテキン類を含む有機物残渣を貯留する場合、有機物残渣に含まれるカテキン類の分解を防止できる。   In particular, it is preferable to use carbonated water obtained by blowing carbon dioxide into raw water for deoxidation treatment as the deoxygenation treatment liquid. Since carbonated water has a pH of 4 to 6, it has a high effect of suppressing the growth of microorganisms, particularly fungi (molds), and when storing organic residues containing catechins, decomposition of catechins contained in organic residues is prevented. Can be prevented.

本発明によれば、有機物残渣を脱酸素雰囲気下で破砕することにより、有機物残渣内で微生物、特にカビが増殖することを防止できる。このため、有機物残渣の腐敗などの変質を防止し、また、カテキン類などの分解を抑制して貯留することができる。また、本発明によれば、貯留後の有機物残渣から、不活性化ガスなどの添加物質を容易に除去し、添加物質が除去された有機物残渣を様々な方法で加工、または処理して再利用することができる。さらに、本発明は、有機物残渣を再利用し易い状態とすることができる。   According to the present invention, the organic residue can be prevented from growing in the organic residue by crushing the organic residue in a deoxygenated atmosphere. For this reason, alterations such as decay of organic residue can be prevented, and decomposition of catechins and the like can be suppressed and stored. Further, according to the present invention, an additive substance such as an inert gas is easily removed from the organic residue after storage, and the organic residue from which the additive substance has been removed is processed or reused by various methods. can do. Furthermore, the present invention can make the organic residue easily reusable.

以下、図面を参照して本発明について具体的に説明する。図1は、本発明に係る有機物残渣を破砕する破砕手段を備えた調整槽20を含む有機物残渣処理貯留装置1(以下、「処理装置」とする)の模式図である。以下、有機物残渣として茶滓を、脱酸素雰囲気下として脱酸素処理液である炭酸水に浸漬する場合について説明する。   Hereinafter, the present invention will be specifically described with reference to the drawings. FIG. 1 is a schematic view of an organic residue treatment storage device 1 (hereinafter referred to as “treatment device”) including an adjustment tank 20 provided with a crushing means for crushing an organic residue according to the present invention. Hereinafter, a case where a teacup is immersed as an organic residue in carbonated water, which is a deoxygenation treatment liquid, under a deoxygenated atmosphere will be described.

まず、図1を参照して処理装置1の全体構成について説明する。図1の処理装置1は、茶滓5を投入し、炭酸水2を添加したのち、これを破砕してスラリ状とする調整槽20と、この調整槽20でスラリ状とされた茶滓5を炭酸水2に浸漬させた状態で貯留する貯留槽30とを備える。   First, the overall configuration of the processing apparatus 1 will be described with reference to FIG. The processing apparatus 1 of FIG. 1 introduces a teacup 5 and, after adding carbonated water 2, crushes the slurry into a slurry, and a teacup 5 that is slurried in the adjustment tank 20. Is stored in the carbonated water 2.

調整槽20には、残渣供給手段を構成するベルトコンベア10と、液体供給手段を構成する炭酸水供給管52と、ガス供給手段を構成するガス供給管53と、調整槽20の内容物を調整槽20から排出して貯留槽30に送給する引き抜き管70aとが接続されている。調整槽20は、引き抜き管70aと、戻し管70bとで構成された循環路70を備える。循環路70には破砕手段であるカッタポンプ71が設けられ、循環路70とカッタポンプ71とは循環破砕手段を構成する。   The adjustment tank 20 adjusts the content of the belt conveyor 10 constituting the residue supply means, the carbonated water supply pipe 52 constituting the liquid supply means, the gas supply pipe 53 constituting the gas supply means, and the adjustment tank 20. An extraction pipe 70 a that is discharged from the tank 20 and fed to the storage tank 30 is connected. The adjustment tank 20 includes a circulation path 70 constituted by a drawing pipe 70a and a return pipe 70b. The circulation path 70 is provided with a cutter pump 71 which is a crushing means, and the circulation path 70 and the cutter pump 71 constitute a circulation crushing means.

なお、破砕手段としては、任意の構成を採用することができ、例えば、調整槽20にカッタ刃を備えた攪拌機を設けてもよい。   In addition, arbitrary structures can be employ | adopted as a crushing means, for example, you may provide the stirrer provided with the cutter blade in the adjustment tank 20. FIG.

戻し管70bの途中には、スラリ送り管80の一端が接続され、スラリ送り管80の他端は貯留槽30と接続されている。貯留槽30には、スラリ送り管80の他に、ガス供給管53から分岐したガス分岐管53bと、貯留槽30の内容物を排出する排出管92とが接続されている。   In the middle of the return pipe 70 b, one end of the slurry feed pipe 80 is connected, and the other end of the slurry feed pipe 80 is connected to the storage tank 30. In addition to the slurry feed pipe 80, a gas branch pipe 53 b branched from the gas supply pipe 53 and a discharge pipe 92 that discharges the contents of the storage tank 30 are connected to the storage tank 30.

次に、調整槽20の構成について詳細に説明する。調整槽20は、側壁20bと、蓋壁20aと、底壁20cとを有する密閉容器で、蓋壁20aが上面となるように設置される。蓋壁20aの一部に開口部25が設けられ、この開口部25に、投入部21が調整槽20の上方に突出する形で設けられている。   Next, the configuration of the adjustment tank 20 will be described in detail. The adjustment tank 20 is a sealed container having a side wall 20b, a lid wall 20a, and a bottom wall 20c, and is installed so that the lid wall 20a is an upper surface. An opening 25 is provided in a part of the lid wall 20 a, and the insertion portion 21 is provided in the opening 25 so as to protrude above the adjustment tank 20.

投入部21は、茶滓5が投入される投入口21aを有し、この投入口21aにベルトコンベア10が接続されている。投入口21aは開放され、空気が出入りするが、調整槽20内部に開口部25を覆う落下板22が設けられ、開口部25が落下板22で覆われることにより、調整槽20は密閉可能に構成されている。なお、落下板22はバネ23によって支持され、上下に動く。なお、本実施形態のように、ガス供給管53から常に炭酸ガスを調整槽20に供給する場合は、落下板22による密閉は厳密なものでなくてもよい。   The input unit 21 has an input port 21a into which the teacup 5 is input, and the belt conveyor 10 is connected to the input port 21a. Although the inlet 21a is opened and air enters and exits, the adjusting tank 20 is provided with a dropping plate 22 that covers the opening 25, and the opening 25 is covered with the dropping plate 22 so that the adjusting tank 20 can be sealed. It is configured. The dropping plate 22 is supported by a spring 23 and moves up and down. Note that when the carbon dioxide gas is always supplied from the gas supply pipe 53 to the adjustment tank 20 as in the present embodiment, the sealing by the dropping plate 22 may not be strict.

調整槽20には、洗浄用の洗浄用液を供給する洗浄液管90が必要に応じて接続され、調整槽20内の液面を計測する第1の液面計26が設けられている。調整槽20に接続された循環路70には、必要に応じてpH計75、電気伝導度計76、プレカッタ77、第1の流量計79、第1の流量調整弁78などを設けることができる。同様に、炭酸水供給管52や洗浄液管90などにも、必要応じて第2の流量調整弁55などを設けてよい。   A cleaning liquid pipe 90 for supplying a cleaning liquid for cleaning is connected to the adjustment tank 20 as necessary, and a first liquid level gauge 26 for measuring the liquid level in the adjustment tank 20 is provided. In the circulation path 70 connected to the adjustment tank 20, a pH meter 75, an electrical conductivity meter 76, a pre-cutter 77, a first flow meter 79, a first flow rate adjustment valve 78, and the like can be provided as necessary. . Similarly, the carbonated water supply pipe 52, the cleaning liquid pipe 90, and the like may be provided with a second flow rate adjusting valve 55 and the like as necessary.

一方、貯留槽30は、金属製のタンクなどの密閉可能な容器で構成され、引き抜き管70a、戻し管70bおよびスラリ送り管80を介して調整槽20から送られたスラリ状の茶滓5を炭酸水2に浸漬した状態で貯留する。調整槽20と同様に、貯留槽30にも、内部の液体の液面を計測する第2の液面計86などを必要に応じて設けることができる。   On the other hand, the storage tank 30 is configured by a sealable container such as a metal tank, and the slurry-like teacup 5 sent from the adjustment tank 20 through the extraction pipe 70a, the return pipe 70b, and the slurry feed pipe 80 is stored. Store in a state immersed in carbonated water 2. Similar to the adjustment tank 20, the storage tank 30 can be provided with a second liquid level gauge 86 for measuring the liquid level of the liquid inside as necessary.

次に、上記の処理装置1を用い、有機物残渣としての茶滓5を脱酸素雰囲気下で破砕する処理方法について説明する。   Next, a processing method for crushing the teacup 5 as an organic residue in a deoxygenated atmosphere using the processing apparatus 1 will be described.

茶滓5を、ベルトコンベア10により、調整槽20に投入する。調整槽20内に投入された茶滓5は落下板22上に堆積し、堆積量が一定量以上となると茶滓5の重みで落下板22が調整槽20下方に動いて開口部25が開き、落下板22上の茶滓5は落下する。茶滓5が落下した後、落下板22はバネ23の復元力により、開口部25を覆う。   The tea bowl 5 is put into the adjustment tank 20 by the belt conveyor 10. The teacup 5 thrown into the adjustment tank 20 is deposited on the dropping plate 22, and when the amount of accumulation reaches a certain amount or more, the falling plate 22 moves below the adjustment tank 20 by the weight of the teacup 5, and the opening 25 is opened. The bowl 5 on the falling plate 22 falls. After the tea bowl 5 falls, the dropping plate 22 covers the opening 25 by the restoring force of the spring 23.

落下板22には、落下板22の開閉を感知するセンサ24が設けられている。このセンサ24により、茶滓5が調整槽20内に投下されたことが検知されると、炭酸水供給管52に設けられた第2の流量調整弁55が作動し、炭酸水2が調整槽20に供給されるとともに、カッタポンプ71が稼動する。これにより、茶滓5は炭酸水2に浸漬された脱酸素雰囲気下で細かく破砕される破砕工程が実施され、破砕された茶滓を含有するスラリが得られる。   The drop plate 22 is provided with a sensor 24 that senses opening and closing of the drop plate 22. When it is detected by the sensor 24 that the tea bowl 5 has been dropped into the adjustment tank 20, the second flow rate adjustment valve 55 provided in the carbonated water supply pipe 52 is activated, and the carbonated water 2 is adjusted to the adjustment tank. 20 and the cutter pump 71 is operated. Thereby, the crushing process in which the teacup 5 is finely crushed in a deoxygenated atmosphere immersed in the carbonated water 2 is performed, and a slurry containing the crushed teacup is obtained.

茶滓5は、カッタポンプ71その他の破砕手段を用い、脱酸素雰囲気下で5〜20分間、破砕処理し、粒径を0.4〜200μm程度とすることが好ましい。破砕時間が短いと、茶滓5は十分に破砕されず、また、酸素が十分に除去されない。一方、破砕時間を必要以上に長くすると破砕のための動力が無駄になる。破砕は、電気伝導度計76などを用いて脱酸素雰囲気が維持されていることを監視しながら行なうとよい。   The tea bowl 5 is preferably crushed for 5 to 20 minutes in a deoxygenated atmosphere using a cutter pump 71 or other crushing means, and the particle size is preferably about 0.4 to 200 μm. When the crushing time is short, the teacup 5 is not sufficiently crushed and oxygen is not sufficiently removed. On the other hand, if the crushing time is longer than necessary, the power for crushing is wasted. The crushing is preferably performed while monitoring that the deoxygenated atmosphere is maintained using an electric conductivity meter 76 or the like.

茶滓は、本実施形態のように、脱酸素処理液である炭酸水2に浸漬した状態で破砕することが好ましい。茶滓5を液体に浸漬することにより、茶滓5が膨張して破砕しやすくなるためである。炭酸水2の供給量は、茶滓5に対し、50〜100重量%とすることが好ましい。炭酸水2は、炭酸水調整槽40において、工業用水などの原水に炭酸ガスが吹き込まれて調整される。   As in this embodiment, the tea bowl is preferably crushed in a state of being immersed in carbonated water 2 that is a deoxygenation treatment liquid. This is because, by immersing the teacup 5 in the liquid, the teacup 5 expands and is easily crushed. The supply amount of the carbonated water 2 is preferably 50 to 100% by weight with respect to the teacup 5. The carbonated water 2 is adjusted in a carbonated water adjustment tank 40 by blowing carbon dioxide into raw water such as industrial water.

ここで、炭酸水調整槽40は、原水が供給される原水供給管41と、炭酸ガスが供給される溶解ガス供給管42とを備えている。炭酸水調整槽40においては、原水供給管41から供給された原水に、散気管、エジェクター、または溶解ポンプなどを用いて炭酸ガスを溶解することにより、炭酸水2を得る。炭酸水調整槽40や炭酸水供給管52には必要に応じて、酸を添加する酸添加手段(図示せず)を設け、茶滓5がpH5.5以下の状態で破砕されるようにしてもよい。酸の添加量は、pH計75などを用いて調整できる。   Here, the carbonated water adjustment tank 40 includes a raw water supply pipe 41 to which raw water is supplied and a dissolved gas supply pipe 42 to which carbon dioxide gas is supplied. In the carbonated water adjustment tank 40, carbonated water 2 is obtained by dissolving carbon dioxide gas in the raw water supplied from the raw water supply pipe 41 using an air diffuser, an ejector, a dissolution pump, or the like. If necessary, the carbonated water adjustment tank 40 and the carbonated water supply pipe 52 are provided with an acid addition means (not shown) for adding an acid so that the teacup 5 is crushed at a pH of 5.5 or less. Also good. The amount of acid added can be adjusted using a pH meter 75 or the like.

本実施形態では、茶滓5は炭酸水2に浸漬されることにより脱酸素雰囲気下で処理されることになるが、液面からの酸素の混入を防ぐため、破砕処理を行なう空間も脱酸素雰囲気とすることが好ましい。本実施形態においては、ガス供給管53から、炭酸ガスを調整槽20に供給する。   In this embodiment, the teacup 5 is treated in a deoxygenated atmosphere by being immersed in the carbonated water 2. However, in order to prevent oxygen from entering from the liquid surface, the space for the crushing treatment is also deoxygenated. An atmosphere is preferable. In the present embodiment, carbon dioxide gas is supplied from the gas supply pipe 53 to the adjustment tank 20.

調整槽20内に充填する不活性化ガスとしては、空気より比重が重く、化学反応を起こしがたいガス、例えば炭酸ガスや窒素ガスであることが好ましい。不活性化ガスの濃度は、99.9%以上であることが好ましい。   The inert gas filled in the adjustment tank 20 is preferably a gas having a specific gravity heavier than air and hardly causing a chemical reaction, such as carbon dioxide gas or nitrogen gas. The concentration of the inert gas is preferably 99.9% or more.

調整槽20には、第1の液面計26を設けて調整槽20内の液面を計測し、調整槽20内のスラリが所定量に達するまで、茶滓5と炭酸水2とを供給し、茶滓5と炭酸水2の混合物を循環破砕してスラリ状とする。炭酸水2を添加して茶滓5を破砕することで、茶滓5の粒径を均質化するとともに茶滓5に保持された酸素を除去することができる。   The adjustment tank 20 is provided with a first liquid level gauge 26 to measure the liquid level in the adjustment tank 20 and supply tea bowl 5 and carbonated water 2 until the slurry in the adjustment tank 20 reaches a predetermined amount. Then, the mixture of tea bowl 5 and carbonated water 2 is circulated and crushed into a slurry. By adding the carbonated water 2 and crushing the teacup 5, it is possible to homogenize the particle size of the teacup 5 and remove oxygen retained in the teacup 5.

調整槽20内のスラリが所定量に達したところで、スラリ送り管80に設けられた貯留弁85を開く。これにより、調整槽20内のスラリを、引き抜き管70a、戻し管70bおよびスラリ送り管80を介して、調整槽20から貯留槽30に供給する。スラリを引き抜いた調整槽20には、引き続いて茶滓5と炭酸水2とを投入して前記の処理を継続する。   When the slurry in the adjustment tank 20 reaches a predetermined amount, the storage valve 85 provided in the slurry feed pipe 80 is opened. Thereby, the slurry in the adjustment tank 20 is supplied from the adjustment tank 20 to the storage tank 30 via the extraction pipe 70a, the return pipe 70b, and the slurry feed pipe 80. Subsequently, the tea bowl 5 and carbonated water 2 are introduced into the adjustment tank 20 from which the slurry has been pulled out, and the above-described processing is continued.

貯留槽30では、調整槽20を介してベルトコンベア10から供給された茶滓5を、貯留する。茶滓5は、調整槽20を介して炭酸水供給管52から供給された炭酸水2に浸漬した状態で貯留する。本実施形態では、調整槽20での破砕処理により、茶滓5表面および内部に保持された酸素が除去されるため、茶滓5は脱酸素雰囲気下で貯留される。   In the storage tank 30, the tea bowl 5 supplied from the belt conveyor 10 through the adjustment tank 20 is stored. The teacup 5 is stored in a state of being immersed in the carbonated water 2 supplied from the carbonated water supply pipe 52 through the adjustment tank 20. In the present embodiment, the crushing process in the adjustment tank 20 removes oxygen retained on the surface and inside of the teacup 5, so that the teacup 5 is stored in a deoxygenated atmosphere.

茶滓2を貯留する場合、腐敗などの品質変化を防ぐため、上記のように脱酸素雰囲気下で貯留することが好ましい。すなわち、破砕した茶滓2は、脱酸素処理した気体または液体中で貯留することが好ましい。例えば、本実施形態では、破砕された茶滓2は、炭酸水に浸漬した脱酸素雰囲気下で貯留する。さらに、本実施形態では、ガス供給管53から分岐させたガス分岐管53bから炭酸ガスを貯留槽30上部に供給して、貯留槽30内部をも脱酸素雰囲気としている。   When storing the teacup 2, it is preferable to store it in a deoxygenated atmosphere as described above in order to prevent quality changes such as decay. That is, the crushed teacup 2 is preferably stored in a deoxygenated gas or liquid. For example, in this embodiment, the crushed teacup 2 is stored in a deoxygenated atmosphere immersed in carbonated water. Furthermore, in this embodiment, carbon dioxide gas is supplied to the upper part of the storage tank 30 from the gas branch pipe 53b branched from the gas supply pipe 53, and the inside of the storage tank 30 is also made into a deoxygenated atmosphere.

貯留槽30には、貯留槽30内の液面を計測する第2の液面計86が設けられており、貯留槽30内の貯留液が所定量に達した場合、排出管92から内部の貯留液を排出する。排出された貯留液は、タンクローリーなどを用いて回収する。回収された貯留液は、腐敗が防止され、また、ポリフェノール類などの分解も抑制されており、さらに、曝気処理などによって容易に炭酸を除去することができる。このため、回収後の貯留液は、ポリフェノール類の精製や粉末茶の製造等に利用できる。   The storage tank 30 is provided with a second liquid level gauge 86 for measuring the liquid level in the storage tank 30. When the stored liquid in the storage tank 30 reaches a predetermined amount, the storage tank 30 is provided with Drain the stored liquid. The discharged stored liquid is collected using a tank lorry or the like. The collected stored liquid is prevented from being spoiled, and the decomposition of polyphenols and the like is suppressed, and furthermore, carbon dioxide can be easily removed by aeration treatment or the like. For this reason, the storage liquid after collection | recovery can be utilized for refinement | purification of polyphenols, manufacture of powdered tea, etc.

なお、上述した弁の開閉や流量の制御は、コントローラ50により行なうことができる。また、処理装置1には、1または2以上の予備貯留槽(図示せず)を設けるとともに、スラリ送り管80に流路切り替え弁を設け、予備の貯留槽で、茶滓5を貯留してもよい。   The valve opening / closing and flow rate control described above can be performed by the controller 50. In addition, the processing apparatus 1 is provided with one or two or more preliminary storage tanks (not shown), and a flow path switching valve is provided in the slurry feed pipe 80 to store the teacup 5 in the preliminary storage tank. Also good.

[実施例]
煎茶を原料とする緑茶飲料の製造過程で発生した茶滓(含水率85重量%)50gをミキサーに入れ、炭酸水(炭酸濃度0.01容積%、pH4.0)50mlを添加して茶滓を破砕し、スラリを得た。スラリは、酸素濃度0.1mg/L未満、pH4.5であった。このスラリをガラス製の密閉容器に入れた。ついで、この密閉容器に濃度99.99%の炭酸ガス50mlを吹き込んだ後、蓋をして35℃の無菌箱内に放置した。
[Example]
50 g of teacup (moisture content of 85% by weight) generated in the process of manufacturing green tea beverages using sencha as a raw material is put in a mixer, and 50 ml of carbonated water (carbonic acid concentration 0.01 vol%, pH 4.0) is added to the teacup. Was crushed to obtain a slurry. The slurry had an oxygen concentration of less than 0.1 mg / L and a pH of 4.5. This slurry was placed in a closed glass container. Next, 50 ml of carbon dioxide gas having a concentration of 99.99% was blown into the sealed container, and the lid was covered and left in a sterile box at 35 ° C.

容器内のスラリの液面から1cm程度は緑がかった茶色の懸濁液で覆われており、破砕された茶滓は液体に浸漬された状態であった。なお、炭酸水は、酸素濃度8mg/Lの市水50mlに99.99%濃度の炭酸ガス100mlを30秒間、吹き込むことにより得たものである。   About 1 cm from the surface of the slurry in the container was covered with a greenish brown suspension, and the crushed teacup was in a state of being immersed in the liquid. Carbonated water was obtained by blowing 100 ml of 99.99% carbon dioxide into 50 ml of city water having an oxygen concentration of 8 mg / L for 30 seconds.

[比較例1]
炭酸水に代えて、脱酸素処理していない市水(酸素濃度酸素濃度8mg/L)を用い、実施例1と同じ処理を行った。得られたスラリは、ポリエチレン製の容器に入れ、実施例1と同様に無菌箱内に放置した。なお、容器には蓋をせず、通気可能とした。
[Comparative Example 1]
The same treatment as in Example 1 was performed using city water (oxygen concentration oxygen concentration 8 mg / L) which was not deoxygenated in place of carbonated water. The obtained slurry was put in a polyethylene container and left in a sterile box as in Example 1. In addition, the container was not covered and was allowed to vent.

[比較例2]
実施例1で用いた茶滓50gを破砕せずに実施例1で用いた容器に入れ、炭酸水50mlを添加した。容器には、濃度99.99%の炭酸ガス50mlを吹き込み、蓋をして実施例1と同様に無菌箱内に放置した。
[Comparative Example 2]
50 g of tea bowl used in Example 1 was put into the container used in Example 1 without crushing, and 50 ml of carbonated water was added. The container was blown with 50 ml of carbon dioxide gas having a concentration of 99.99%, covered, and left in a sterile box as in Example 1.

[比較例3]
炭酸水に代えて比較例1で用いた市水を用いた他は比較例2と同様の条件で実験を行なった。なお、容器には蓋をせずに無菌箱内に放置した。
[Comparative Example 3]
The experiment was performed under the same conditions as in Comparative Example 2 except that the city water used in Comparative Example 1 was used instead of carbonated water. The container was left in a sterile box without a lid.

3〜7日間経過後の容器内の貯留液表面または液内部でのカビの発生の有無、および腐敗臭の有無を表1に示す。   Table 1 shows the presence or absence of mold on the surface of the stored liquid in the container after 3 to 7 days and the presence or absence of rot odor.

Figure 2005238076
Figure 2005238076

表1に示すように、実施例では、7日間経過してもカビや腐敗臭の発生はなかった。比較例については、比較例1では3日経過後、比較例2では7日経過後、比較例3では5日経過後にカビの発生が認められ、3日後には比較例1で、7日後には比較例3で腐敗臭も発生した。   As shown in Table 1, in the examples, no mold or rot odor occurred even after 7 days. About the comparative example, generation | occurrence | production of mold | fungi was recognized after the lapse of 3 days in the comparative example 1, the lapse of 7 days in the comparative example 2, and the lapse of 5 days in the comparative example 3, and the comparative example 1 after 3 days and the comparison after 7 days. In Example 3, a rotting odor was also generated.

比較例2については、脱酸素雰囲気下で貯留したため、一定の微生物増殖抑制効果が得られたが、7日経過後にカビの発生が認められた。これは、茶滓を破砕しなかったことにより、茶滓内に酸素が保持された部分が生じ、かかる部分でカビが増殖したことによると考えられる。   Since Comparative Example 2 was stored in a deoxygenated atmosphere, a certain microbial growth inhibitory effect was obtained, but generation of mold was observed after 7 days. This is considered to be due to the fact that oxygen was retained in the teacup due to the fact that the teacup was not crushed, and that mold grew in this portion.

本発明は、茶滓などの有機物残渣を腐敗しにくく、また取り扱いが容易で再利用しやすい形態とし、カテキン類の製造原料などを調整することに利用できる。   INDUSTRIAL APPLICABILITY The present invention can be used to adjust the raw materials for producing catechins, etc., in a form in which organic residue such as tea bowl is not easily spoiled and is easy to handle and easy to reuse.

本発明の一実施形態である処理装置を示す模式図である。It is a schematic diagram which shows the processing apparatus which is one Embodiment of this invention.

符号の説明Explanation of symbols

1 有機物残渣処理貯留装置(処理装置)
10 ベルトコンベア(残渣供給手段)
20 調整槽
30 貯留槽
52 炭酸水供給管(液体供給手段)
53 ガス供給管(ガス供給手段)
71 カッタポンプ(破砕手段)
1 Organic residue treatment storage device (treatment device)
10 Belt conveyor (residue supply means)
20 Adjustment tank 30 Storage tank 52 Carbonated water supply pipe (liquid supply means)
53 Gas supply pipe (gas supply means)
71 Cutter pump (crushing means)

Claims (3)

有機物残渣を脱酸素雰囲気下で破砕する破砕工程を含む有機物残渣の処理方法。   A method for treating an organic residue comprising a crushing step of crushing the organic residue in a deoxygenated atmosphere. 前記脱酸素雰囲気を、密閉可能な空間に不活性化ガスを充填することにより構成する請求項1記載の有機物残渣の処理方法。   The method for treating an organic matter residue according to claim 1, wherein the deoxygenating atmosphere is configured by filling an inert gas in a sealable space. 前記破砕工程において、脱酸素処理をした脱酸素処理液に有機物残渣を浸漬して破砕する請求項1記載の有機物残渣の処理方法。   The processing method of the organic substance residue of Claim 1 which immerses and crushes an organic substance residue in the deoxidation process liquid which deoxidized in the said crushing process.
JP2004050123A 2004-02-25 2004-02-25 Treating method of organic residual dross Pending JP2005238076A (en)

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