JP2005238077A - Pooling method of organic residue and pooling apparatus - Google Patents

Pooling method of organic residue and pooling apparatus Download PDF

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JP2005238077A
JP2005238077A JP2004050124A JP2004050124A JP2005238077A JP 2005238077 A JP2005238077 A JP 2005238077A JP 2004050124 A JP2004050124 A JP 2004050124A JP 2004050124 A JP2004050124 A JP 2004050124A JP 2005238077 A JP2005238077 A JP 2005238077A
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organic residue
residue
organic
liquid
inert gas
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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 a pooling method of an organic residue that prevents the putrefaction of an organic residue and does not inhibit the recycling of the organic residue. <P>SOLUTION: The method comprises pooling the organic residue under deoxidation atmosphere. More specifically, the organic residue such as used tea leaves 5 are pooled under deoxidation atmosphere by immersing in carbonated water 2 of an deoxidizing treatment liquid. The used tea leaves are thrown into an adjustment tank 20 from a residue supply means 10 and mixed with the carbonated water 2 supplied from a liquid supply means 52 and sent to a reservoir 30 for pooling. The carbonated water 2 may be added to the used tea leaves 5 at the adjustment tank 20 equipped with a cutter pump 71 as a crushing means before the leaves 5 are pooled at the reservoir 30. <P>COPYRIGHT: (C)2005,JPO&NCIPI

Description

本発明は、有機物残渣の貯留方法に関し、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植物系の有機物残渣の貯留方法および貯留装置に関する。   The present invention relates to an organic residue storage method, and more particularly to a plant organic residue storage method and storage apparatus for storing a solid plant organic residue such as teacup and coffee cake without rot.

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いため貯留中に腐敗しやすい。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, solid organic residues are likely to rot during storage due to their high water content. Rotated organic residue is difficult to be reused, and generates a foul odor to deteriorate the hygienic condition of the surrounding environment.

そこで、有機物残渣の腐敗を防止する方法として、有機物残渣にソルビン酸カリウム水溶液と酸の水溶液とを添加する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、ミキサーを用いて、ジャガイモ廃棄物やビール滓などの有機物残渣にソルビン酸カリウム水溶液を添加混合し、次いでリン酸などの酸の水溶液を添加混合する。   Therefore, as a method for preventing the decay of organic residue, a method of adding an aqueous potassium sorbate solution and an acid aqueous solution to the organic residue has been proposed (Patent Document 1). In the method disclosed in Patent Document 1, an aqueous potassium sorbate solution is added to and mixed with an organic residue such as potato waste and beer lees using a mixer, and then an aqueous solution of an acid such as phosphoric acid is added and mixed.

有機物残渣にソルビン酸カリウム水溶液を添加することにより、微生物、特に菌類(カビ)の繁殖を抑えることができるため、上記方法によれば、有機物残渣を腐敗させずに2〜3週間、保存することができる。また、ソルビン酸カリウム水溶液の添加混合後、酸の水溶液を添加することにより、ソルビン酸カリウムの活性を高め、ソルビン酸カリウムの添加量を減らすことができる。   By adding an aqueous potassium sorbate solution to the organic residue, it is possible to suppress the growth of microorganisms, particularly fungi (fungi), and according to the above method, the organic residue is stored for 2 to 3 weeks without being spoiled. Can do. Moreover, the activity of potassium sorbate can be improved and the addition amount of potassium sorbate can be reduced by adding the aqueous solution of acid after the addition and mixing of the potassium sorbate aqueous solution.

しかし、上記の方法で処理した有機物残渣から、ソルビン酸カリウムやリン酸などの薬剤を除去することは困難である。このため、上記の添加薬剤が残存した有機物残渣を再利用する場合、これらの添加薬剤が再利用時の処理を阻害し、また、再利用処理後に得られる製品中にこれらの添加薬剤が混入する恐れがある。
特開平8−173058号公報
However, it is difficult to remove chemicals such as potassium sorbate and phosphoric acid from the organic residue treated by the above method. For this reason, when the organic residue in which the above-mentioned additive chemicals remain is reused, these additive chemicals inhibit the processing at the time of reuse, and these additive chemicals are mixed in the product obtained after the reuse treatment. There is a fear.
JP-A-8-173058

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、有機物残渣の再利用を阻害する物質が残存する恐れを低減しながら有機物残渣の腐敗を防止することができる有機物残渣の貯留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する恐れが低い物質を用いて、有機物残渣の腐敗を防止して保存することを可能とする有機物残渣の貯留方法を提供することを目的とする。   The present invention has been made in view of the problems as described above, and the object thereof is an organic residue that can prevent the decay of an organic residue while reducing the possibility that a substance that inhibits the reuse of the organic residue remains. It is to provide a storage method. More specifically, the present invention uses a substance that is easy to remove from the organic residue and has a low risk of inhibiting the reuse of the organic residue after storage, and prevents the organic residue from being spoiled and stored. It aims at providing the storage method of the organic substance residue made possible.

本発明は、有機物残渣を脱酸素雰囲気下で、特に、原水に含まれる溶存酸素を除去する脱酸素処理をした脱酸素処理液に浸漬した状態で、貯留する。より具体的には、本発明は以下のようなものを提供する。   The present invention stores an organic residue in a deoxygenated atmosphere, particularly in a state of being immersed in a deoxygenated liquid that has been deoxygenated to remove dissolved oxygen contained in raw water. More specifically, the present invention provides the following.

(1)有機物残渣を脱酸素雰囲気下で貯留する有機物残渣の貯留方法。   (1) A method for storing an organic residue in which the organic residue is stored 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は、カテキン類などの利用可能な物質を多く含み、また、タンパク質を多く含む肉エキス抽出残渣のような動物系残渣に比べて長く貯留できる。さらに、食品加工工場や、飲料製造工場などでは、近似した品質の植物系加工残渣が定期的に一定量、発生する傾向がある。このため、植物系加工残渣は、残存成分を回収するといった再利用がしやすく、本発明における好適な貯留対象である。中でも、飲料製造過程で発生する茶滓は、カテキン類を多く含み、本発明に従って貯留した後、カテキン類を回収したり飼料に混合したりして再利用できるため、特に好ましい。   Among the above organic residue, food processing residues such as teacups and bean cakes, plant-derived plant-based processing residues are rich in catechins and other available substances, and meat extracts that are rich in protein It can be stored longer than animal residues such as extraction residues. Furthermore, in food processing factories, beverage manufacturing factories, and the like, there is a tendency that a certain amount of plant-based processing residue of approximate quality is regularly generated. For this reason, the plant-based processing residue is easy to reuse such as recovering the remaining components, and is a suitable storage target in the present invention. Among them, the tea bowl generated in the beverage production process is particularly preferable because it contains a large amount of catechins and can be reused by collecting the catechins and mixing them with feed after storage according to the present invention.

「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。酸素を含む気体を脱酸素処理する方法としては、不活性化ガスなどの吹き込みにより酸素を除去する方法、または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 “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. As a method of deoxygenating a gas containing oxygen, a method of removing oxygen by blowing an inert gas or the like, or a method of deoxygenating by containing a gas in a sealed space and putting a deoxidizer in this space and so on.

本発明においては、有機物残渣を脱酸素雰囲気下に置くことにより、有機物残渣と酸素との接触を遮断する。固形状の有機物残渣は、酸素との接触が阻害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することができる。また、本発明によれば、有機物残渣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。   In the present invention, the contact between the organic residue and oxygen is blocked by placing the organic residue in a deoxygenated atmosphere. The solid organic residue is in a state in which aerobic microorganisms are difficult to grow due to inhibition of contact with oxygen. For this reason, according to the present invention, it is possible to prevent and store the organic matter residue. In addition, according to the present invention, since there is no need to add chemicals such as a preservative for preventing corruption to the organic residue, inconvenience caused by the preservative remaining in the organic residue when the organic residue is reused. Can be reduced.

(2)前記脱酸素雰囲気下を、脱酸素処理をした脱酸素処理液に有機物残渣を浸漬することとする(1)記載の有機物残渣の貯留方法。   (2) The organic residue storing method according to (1), wherein the organic residue is immersed in a deoxygenated treatment solution that has been subjected to deoxidation treatment in the deoxygenated atmosphere.

「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。 “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.

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 deoxygenated liquids have a particularly high fungus growth inhibitory effect among microorganisms and are suitable for preserving 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.

(3)前記脱酸素処理液を、不活性化ガスを溶解させて脱酸素処理をした不活性化ガス溶解水とする(2)記載の有機物残渣の貯留方法。   (3) The method for storing organic matter residues according to (2), wherein the deoxygenation treatment liquid is an inert gas-dissolved water obtained by dissolving an inert gas to perform a deoxygenation treatment.

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.

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ガス、窒素ガスおよび炭酸ガスが含まれるものとする。   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, the “inert gas” means a gas that hardly causes an oxidation reaction among chemical reactions, and includes a rare gas group element gas such as helium and argon, nitrogen gas, and carbon dioxide gas. To do.

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、不活性化ガスの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。   Of these inert gases, carbon dioxide gas and nitrogen gas are easy to handle and can be used particularly preferably. An inert gas having a concentration of 99.9% or more is used, and the amount blown so that the oxygen concentration of the liquid after blowing the inert gas is 1 mg / L or less, preferably 0.1 mg / L or less. It is preferable to adjust the blowing time and the like.

(4)前記不活性化ガスを炭酸ガスとし、前記不活性化ガス溶解水を炭酸水とする(3)記載の有機物残渣の貯留方法。   (4) The method for storing organic matter residues according to (3), wherein the inert gas is carbon dioxide, and the inert gas-dissolved water is carbonated water.

有機物残渣を浸漬する脱酸素処理液としては、原水に炭酸ガスを吹き込むという脱酸素処理により得られる炭酸水を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。   As the deoxygenation treatment solution for immersing the organic residue, it is preferable to use carbonated water obtained by deoxygenation treatment in which carbon dioxide gas is blown into the raw water. 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.

(5)有機物残渣を供給する残渣供給手段と、脱酸素処理をした脱酸素処理液を供給する液体供給手段と、有機物残渣を脱酸素処理液に浸漬して貯留する貯留槽と、を備える有機物残渣の貯留装置。   (5) An organic matter comprising: a residue supply means for supplying an organic residue, a liquid supply means for supplying a deoxygenated deoxidized liquid, and a storage tank for immersing and storing the organic residue in the deoxygenated liquid. Residue storage device.

(5)記載の発明に係る有機物残渣貯留装置は、有機物残渣を投入する貯留槽を備え、この貯留槽に残渣供給手段と、液体供給手段とを接続して構成することができる。また、有機物残渣を脱酸素処理液に浸漬して貯留する貯留槽とは別に、有機物残渣と脱酸素処理液とを混合する前処理用の調整槽を設け、この調整槽に残渣供給手段を構成する残渣供給管と、液体供給手段を構成する液体供給管とを接続してもよい。   The organic residue storage device according to the invention described in (5) includes a storage tank into which an organic residue is charged, and can be configured by connecting a residue supply means and a liquid supply means to the storage tank. In addition to the storage tank for storing the organic substance residue by immersing it in the deoxygenation treatment liquid, a pretreatment adjustment tank for mixing the organic residue and the deoxygenation treatment liquid is provided, and the residue supply means is configured in this adjustment tank. The residue supply pipe and the liquid supply pipe constituting the liquid supply means may be connected.

有機物残渣を貯留する貯留槽は、有機物残渣を脱酸素処理液に浸漬して貯留できるものであれば特に制限なく使用できる。しかし、脱酸素処理液に酸素が溶解することを防ぐため、密閉可能な形状であり、酸素を透過させにくい材質で構成されることが好ましい。   The storage tank for storing the organic residue can be used without particular limitation as long as the organic residue can be stored by immersing the organic residue in a deoxygenated liquid. However, in order to prevent the oxygen from being dissolved in the deoxygenation treatment liquid, it is preferable that the oxygen-dissolving solution has a shape that can be sealed and is made of a material that hardly transmits oxygen.

(5)記載の発明によれば、(1)記載の発明と同様の効果を得ることができる。   According to the invention described in (5), the same effect as that of the invention described in (1) can be obtained.

(6)前記脱酸素処理液を、不活性化ガスを溶解させて脱酸素処理をした不活性化ガス溶解水とする(5)記載の有機物残渣の貯留装置。   (6) The organic residue storage device according to (5), wherein the deoxygenation treatment liquid is an inert gas-dissolved water in which an inert gas is dissolved and deoxygenated.

(6)記載の発明によれば、(3)記載の発明と同様の効果を得ることができる。   According to the invention described in (6), the same effect as in the invention described in (3) can be obtained.

(7)不活性化ガスを供給するガス供給手段をさらに備える(5)または(6)記載の有機物残渣の貯留装置。   (7) The organic residue storage device according to (5) or (6), further comprising a gas supply means for supplying an inert gas.

(7)記載の発明によれば、(4)記載の発明と同様の効果を得ることができる。   According to the invention described in (7), the same effect as that of the invention described in (4) can be obtained.

また、本発明は、前記(5)〜(7)記載の貯留装置を含む有機物残渣の処理装置を用いて、前記(1)〜(4)いずれか記載の貯留方法を適用した貯留工程を含む有機物残渣の処理方法を実施することにより、有機物残渣に含まれる利用可能な成分の回収率を向上させることができる。   Moreover, this invention includes the storage process which applied the storage method in any one of said (1)-(4) using the processing apparatus of the organic substance residue containing the storage apparatus as described in said (5)-(7). By carrying out the organic residue treatment method, the recovery rate of available components contained in the organic residue can be improved.

本発明によれば、有機物残渣を脱酸素処理液に浸漬するなどして脱酸素雰囲気下で貯留することにより、酸素を遮断し、貯留中に有機物残渣内で微生物、特にカビが増殖することを防止する。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。   According to the present invention, by storing the organic substance residue in a deoxygenated treatment solution by immersing the organic substance residue in a deoxygenated treatment solution, the oxygen is blocked, and microorganisms, particularly mold, grow in the organic substance residue during storage. To prevent. 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.

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の貯留槽30を含む有機物残渣処理貯留装置1(以下、「貯留装置1」とする)の模式図である。以下、有機物残渣として茶滓を、脱酸素処理液として炭酸水を用い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 processing storage apparatus 1 (hereinafter referred to as “storage apparatus 1”) including an organic residue storage tank 30 according to the present invention. Hereinafter, a case where tea bowl is used as an organic residue and carbonated water is used as a deoxygenation treatment liquid will be described.

まず、図1を参照して貯留装置1の全体構成について説明する。図1の貯留装置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 storage device 1 will be described with reference to FIG. The storage device 1 shown in FIG. 1 is charged with a teacup 5 and added with carbonated water 2, and then crushes the slurry into a slurry, and the teacup 5 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。引き抜き管70aは、カッタポンプ71の入り口側と接続され、カッタポンプ71の出口側には戻し管70bの一端が接続され、戻し管70bの他端は調整槽20と接続され、循環路70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 extraction pipe 70 a is connected to the inlet side of the cutter pump 71, one end of the return pipe 70 b is connected to the outlet side of the cutter pump 71, and the other end of the return pipe 70 b is connected to the adjustment tank 20, Constitute.

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。   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.

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、上記の貯留装置1を用い、有機物残渣としての茶滓5を、脱酸素処理液としての炭酸水2に浸漬するという脱酸素雰囲気下で貯留する方法について説明する。   Next, a method of storing the tea bowl 5 as an organic residue in the deoxygenated atmosphere of immersing in the carbonated water 2 as the deoxygenation treatment liquid using the above-described storage device 1 will be described.

まず、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。   First, 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、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 teacup 5 is finely crushed in a deoxygenated atmosphere immersed in the carbonated water 2, and a slurry containing the crushed teacup is obtained.

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。   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、散気管やエジェクター、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、貯留槽30に貯留される液状物のpHが5.5以下とな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. The carbonated water adjustment tank 40 and the carbonated water supply pipe 52 are provided with an acid addition means (not shown) for adding acid as necessary, and the pH of the liquid substance stored in the storage tank 30 is 5.5 or less. It may be made to become. The amount of acid added can be adjusted using a pH meter 75 or the like.

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.

なお、処理の再開前に洗浄液管90から水などの洗浄用液を供給し、調整槽20内を洗浄してもよい。調整槽20を洗浄する場合は、引き抜き管70aに接続した排液管91を介して洗浄排液を排出する。調整槽20を洗浄することにより、異なる種類の有機物残渣を処理することができる。   In addition, before the process is restarted, a cleaning liquid such as water may be supplied from the cleaning liquid pipe 90 to clean the inside of the adjustment tank 20. When the adjustment tank 20 is washed, the washing drainage is discharged through the drainage pipe 91 connected to the drawing pipe 70a. By washing the adjustment tank 20, different types of organic residue can be treated.

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に浸漬された状態で貯留される。すなわち、本実施形態では、調整槽20において茶滓5に炭酸水2が添加混合されているため、貯留槽30内に送給された茶滓5は、炭酸水2に浸漬された脱酸素雰囲気下で貯留されることになる。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は確実に脱酸素雰囲気下で貯留されることになる。   In the storage tank 30, the teacup 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. That is, in this embodiment, since the carbonated water 2 is added and mixed to the teacup 5 in the adjustment tank 20, the teacup 5 fed into the storage tank 30 is deoxidized atmosphere immersed in the carbonated water 2. Will be stored below. In this 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 surely stored in a deoxygenated atmosphere.

貯留槽30の内部は、液面からの酸素の溶け込みを防止するため、密閉することが好ましい。さらに、密閉した貯留槽30内に、炭酸ガスなどの不活性化ガスを充填することが好ましい。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上部に供給する。   The inside of the storage tank 30 is preferably sealed in order to prevent oxygen from dissolving from the liquid surface. Furthermore, it is preferable to fill the sealed storage tank 30 with an inert gas such as carbon dioxide. In the present embodiment, carbon dioxide gas is supplied to the upper portion of the storage tank 30 from the gas branch pipe 53 b branched from the gas supply pipe 53.

なお、調整槽20の内部にも、炭酸ガスなどの不活性化ガスを充填することが好ましい。調整槽20内部に不活性化ガスを充填することにより、調整槽20内が脱酸素雰囲気となるため、液面から酸素がスラリに溶け込むことを防止できる。また、調整槽20の密閉状態が不完全であってもよいことになる。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 addition, it is preferable to fill the inside of the adjustment tank 20 with an inert gas such as carbon dioxide gas. By filling the inside of the adjustment tank 20 with an inert gas, the inside of the adjustment tank 20 becomes a deoxygenated atmosphere, so that oxygen can be prevented from being dissolved into the slurry from the liquid surface. Moreover, the sealing state of the adjustment tank 20 may be incomplete. In the present embodiment, carbon dioxide gas is supplied from the gas supply pipe 53 to the adjustment tank 20.

貯留槽30および調整槽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 storage tank 30 and the adjustment tank 20 is preferably a gas having a specific gravity heavier than air and difficult to cause a chemical reaction, such as carbon dioxide gas or nitrogen gas. The concentration of the inert gas is preferably 99.9% or more.

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により行うことができる。また、貯留装置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 above-described valve opening / closing and flow rate control can be performed by the controller 50. In addition, the storage device 1 is provided with one or two or more preliminary storage tanks (not shown), a flow path switching valve is provided in the slurry feed pipe 80, and the teacup 5 is stored in the spare storage tank. Also good.

[実施例1]
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 1]
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%の濃度の炭酸ガス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. The carbonated water was obtained by blowing 100 ml of 99.99% carbon dioxide gas into 50 ml of city water having an oxygen concentration of 8 mg / L for 30 seconds.

[実施例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。
[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1]
炭酸水に代えて、脱酸素処理していない市水(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: 8 mg / L) that was not subjected to deoxygenation instead 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]
炭酸水に代えて比較例1で用いた市水を用いた他は実施例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 2]
The experiment was performed under the same conditions as in 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 2005238077
Figure 2005238077

表1に示すように、実施例1では、7日間経過してもカビや腐敗臭の発生はなかった。実施例2については、7日後にカビが発生した。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。   As shown in Table 1, in Example 1, no mold or rot odor occurred even after 7 days. In Example 2, mold occurred 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.

一方、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5日経過後にカビの発生が認められ、5日後には比較例1で、7日後には比較例2で腐敗臭も発生した。   On the other hand, for Comparative Example, generation of mold was observed after 3 days in Comparative Example 1 and after 5 days in Comparative Example 2, and in Example 1 after 5 days, and in Example 2 after 7 days, rot odor was also observed. Occurred.

本発明は、茶滓などの有機物残渣を腐敗させることなく、一定期間貯留し、一定量の有機物残渣が貯留された時点で、これらの貯留有機物残渣からカテキン類などの物質を回収して再利用するために利用できる。   The present invention stores organic residues such as teacups without decaying for a certain period, and when a certain amount of organic residues are stored, collects and reuses substances such as catechins from these stored organic residues. Available to do.

本発明の一実施形態である貯留装置を示す模式図である。It is a mimetic diagram showing the storage device which is one embodiment of the present invention.

符号の説明Explanation of symbols

1 有機物残渣処理貯留装置(貯留装置)
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)
1 Organic residue treatment storage device (storage 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)

Claims (7)

有機物残渣を脱酸素雰囲気下で貯留する有機物残渣の貯留方法。   An organic residue storage method for storing an organic residue in a deoxygenated atmosphere. 前記脱酸素雰囲気下を、脱酸素処理をした脱酸素処理液に有機物残渣を浸漬することとする請求項1記載の有機物残渣の貯留方法。   The organic residue storage method according to claim 1, wherein the organic residue is immersed in a deoxygenation treatment liquid that has been subjected to deoxygenation treatment in the deoxygenation atmosphere. 前記脱酸素処理液を、不活性化ガスを溶解させて脱酸素処理をした不活性化ガス溶解水とする請求項2記載の有機物残渣の貯留方法。   The method for storing an organic substance residue according to claim 2, wherein the deoxygenation treatment liquid is an inert gas-dissolved water in which an inert gas is dissolved to perform deoxygenation treatment. 前記不活性化ガスを炭酸ガスとし、
前記不活性化ガス溶解水を炭酸水とする請求項3記載の有機物残渣の貯留方法。
The inert gas is carbon dioxide,
The organic residue storage method according to claim 3, wherein the inert gas-dissolved water is carbonated water.
有機物残渣を供給する残渣供給手段と、
脱酸素処理をした脱酸素処理液を供給する液体供給手段と、
有機物残渣を脱酸素処理液に浸漬して貯留する貯留槽と、を備える有機物残渣の貯留装置。
A residue supplying means for supplying an organic residue;
A liquid supply means for supplying a deoxygenated liquid after deoxygenation;
An organic matter residue storage apparatus comprising: a storage tank that immerses and stores an organic matter residue in a deoxygenated liquid.
前記脱酸素処理液を、不活性化ガスを溶解させて脱酸素処理をした不活性化ガス溶解水とする請求項5記載の有機物残渣の貯留装置。   The organic-residue storage device according to claim 5, wherein the deoxygenation treatment liquid is an inert gas-dissolved water in which an inert gas is dissolved to perform deoxygenation treatment. 不活性化ガスを供給するガス供給手段をさらに備える請求項5または6記載の有機物残渣の貯留装置。   The organic residue storage device according to claim 5 or 6, further comprising a gas supply means for supplying an inert gas.
JP2004050124A 2004-02-25 2004-02-25 Pooling method of organic residue and pooling apparatus Pending JP2005238077A (en)

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Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2015203146A (en) * 2014-04-15 2015-11-16 株式会社ショウワ Turning cleaning recovery device

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2015203146A (en) * 2014-04-15 2015-11-16 株式会社ショウワ Turning cleaning recovery device

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