JPH07275836A - Garbage dryer and garbage treatment method - Google Patents
Garbage dryer and garbage treatment methodInfo
- Publication number
- JPH07275836A JPH07275836A JP6072178A JP7217894A JPH07275836A JP H07275836 A JPH07275836 A JP H07275836A JP 6072178 A JP6072178 A JP 6072178A JP 7217894 A JP7217894 A JP 7217894A JP H07275836 A JPH07275836 A JP H07275836A
- Authority
- JP
- Japan
- Prior art keywords
- food waste
- processing aid
- drying
- garbage
- heating
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Granted
Links
Landscapes
- Drying Of Solid Materials (AREA)
- Treating Waste Gases (AREA)
- Processing Of Solid Wastes (AREA)
- Refuse Receptacles (AREA)
Abstract
Description
【発明の詳細な説明】Detailed Description of the Invention
【0001】[0001]
【産業上の利用分野】本発明は、水分を多く含む調理屑
や食べ残し等の生ごみ等を対象とした、例えば小型で簡
便にかつ衛生的に使用できる家庭用等に適した生ごみ乾
燥処理装置および生ごみ処理方法に関する。BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention is directed to food waste such as cooking wastes containing a large amount of water and food leftovers, and is suitable for household use, for example, which is small and can be used easily and sanitarily. The present invention relates to a processing device and a garbage disposal method.
【0002】[0002]
【従来の技術】家庭等で発生したごみは、各自治体が収
集車で回収し、埋立あるいは焼却といった方法で一括処
理されている。ごみの排出量は年々増加しており、各自
治体での処理能力が限界にきている。ごみの増加に対応
するためには新規処理場の建設が必要であるが、新規処
理場の建設用地の確保が住民の反対運動等で困難な状況
となっている。そのため、各家庭あるいは個人でごみの
発生量を低減することが必要となってきている。家庭に
おいてもごみはやっかいものである。特に腐敗しいやな
臭気を発生する生ごみは、その処理技術の確立が待望さ
れている。そこで社会トレンドのごみ減量化と家庭での
ニ−ズに基づき、各種の家庭用の生ごみ処理装置が開発
されている。その処理装置として、生ごみを粉砕し排水
とともに下水に流すディスポ−ザ−、生ごみを腐敗させ
肥料にするコンポスト、微生物を使った生ごみ分解消滅
機等がある。また、生ごみを乾燥させて減量化し、且つ
腐敗を防止する生ごみ乾燥装置も開発されている。2. Description of the Related Art Garbage generated at home is collected by a collection vehicle by each municipality and collectively disposed of by landfilling or incineration. The amount of waste generated is increasing year by year, and the processing capacity of each municipality is reaching its limit. Although it is necessary to construct a new treatment plant to deal with the increase in waste, it is difficult to secure land for the construction of the new treatment plant due to opposition movements of residents. Therefore, it has become necessary to reduce the amount of waste generated in each household or individual. At home, garbage is a nuisance. In particular, the establishment of a processing technology for garbage that has a rotten and unpleasant odor is desired. Therefore, various household garbage disposal devices for household use have been developed based on the social trend of waste reduction and household needs. As the processing equipment, there are a disposer that crushes raw garbage and discharges it into sewage together with drainage, a compost that decomposes raw garbage into fertilizer, and a device that decomposes and eliminates garbage using microorganisms. In addition, a food waste drying device has been developed which dries the food waste to reduce the amount thereof and prevents spoilage.
【0003】[0003]
【発明が解決しようとする課題】しかしながら、ディス
ポ−ザ−は、河川等を汚染することから原則的に使用を
禁止されている。コンポストは土壌を必要とするため、
庭のないマンション等では利用できない。また、微生物
を使った生ごみ分解消滅機は、好気性発酵をする条件で
は、ある程度無臭で処理できるが、嫌気性発酵をする条
件になった場合耐えがたい臭気を発生することが課題と
なる。生ごみ乾燥装置は、場所を選ばず生ごみを処理
し、乾燥中の臭気にもある程度対応できる。しかし、乾
燥後のごみ、あるいは加熱分離された凝縮水に臭いが残
る点に問題点があった。However, the disposer is basically prohibited from use because it contaminates rivers and the like. Because compost requires soil,
It cannot be used in apartments without gardens. In addition, the garbage decomposing machine using microorganisms can be processed without odor to some extent under the condition of aerobic fermentation, but it becomes a problem to generate an unbearable odor under the condition of anaerobic fermentation. The food waste dryer treats food waste anywhere and can handle odors during drying to some extent. However, there is a problem in that odor remains in the dust after drying or the condensed water that has been separated by heating.
【0004】本発明は上記従来の問題点を解決するもの
で、生ごみの乾燥処理後のごみ、あるいは生ごみから加
熱分離された凝縮水の臭気を従来に比べてより一層低減
出来る生ごみ乾燥処理装置及び、その処理方法を提供す
ることを目的とする。The present invention solves the above-mentioned conventional problems. Drying of garbage can further reduce the odor of garbage after drying the garbage or condensed water heated and separated from the garbage as compared with the conventional case. An object is to provide a processing device and a processing method thereof.
【0005】[0005]
【課題を解決するための手段】第1発明は、生ごみを収
納する収納部と、その収納部に収納された前記生ごみを
加熱乾燥するための加熱手段とを備えた生ごみ乾燥処理
装置を用いて、前記生ごみを前記収納部に収納し加熱乾
燥をする際に、前記生ごみの前記収納と同時期及び/又
は異なる時期に前記収納部へ脱臭のための処理助剤を投
入する生ごみ処理方法である。A first aspect of the present invention is a food waste drying apparatus comprising a storage unit for storing food waste, and a heating means for heating and drying the food waste stored in the storage unit. When the food waste is stored in the storage portion and heated and dried using, the processing aid for deodorization is put into the storage portion at the same time and / or at a different time from the storage of the food waste. It is a garbage disposal method.
【0006】第2発明は、生ごみを収納する収納部と、
その収納部に収納された前記生ごみを加熱乾燥するため
の加熱手段と、前記収納部の外側に設けられ、前記加熱
手段により前記生ごみから分離された気体及び/又は前
記気体が凝縮されて生成された液体が通過する通路部
と、前記液体を貯留する貯留部とを備えた生ごみ乾燥処
理装置を用いて、前記生ごみを前記収納部に収納し加熱
乾燥をする際に、前記生ごみの前記収納と同時期及び/
又は異なる時期に前記通路部及び/又は前記貯留部へ脱
臭のための処理助剤を投入する生ごみ処理方法である。A second aspect of the invention is a storage section for storing food waste,
A heating means for heating and drying the food waste stored in the storage portion, and a gas provided on the outside of the storage portion and separated from the food waste by the heating means and / or the gas is condensed. When using a food waste drying treatment apparatus having a passage portion through which the generated liquid passes and a storage portion that stores the liquid, when storing the food waste in the storage portion and performing heat drying, the raw food At the same time as the storage of garbage and /
Alternatively, it is a method of treating food waste, in which a processing aid for deodorization is added to the passage portion and / or the storage portion at different times.
【0007】第3発明は、上記処理助剤の前記投入後、
前記生ごみが塩基性を示す場合は、他の処理助剤として
酸性物質を投入し、又前記生ごみが酸性又は中性を示す
場合は、他の処理助剤として塩基性物質を投入すること
により、前記生ごみを中和させる第1発明、又は第2発
明としての生ごみ処理方法である。A third invention is, after the above-mentioned addition of the processing aid,
If the food waste is basic, add an acidic substance as another treatment aid, and if the food waste is acidic or neutral, add a basic substance as another treatment aid. According to the first aspect of the present invention, there is provided a method for treating raw garbage according to the first or second aspect of the present invention.
【0008】第4発明は、上記処理助剤が、塩基性電解
質を1成分とする処理助剤である第1発明、第2発明、
又は第3発明としての生ごみ処理方法である。A fourth invention is the above-mentioned processing aid, which is a processing aid containing a basic electrolyte as one component.
Alternatively, it is a method for treating food waste as a third invention.
【0009】第5発明は、上記処理助剤が、水溶性過酸
化物を1成分とする処理助剤である第1発明、第2発
明、又は第3発明としての生ごみ処理方法である。A fifth aspect of the invention is the method of treating food waste as the first aspect, the second aspect, or the third aspect, wherein the treatment aid is a treatment aid containing a water-soluble peroxide as one component.
【0010】第6発明は、上記水溶性過酸化物が、ペル
オキソ酸塩である第5発明としての生ごみ処理方法であ
る。A sixth invention is a method of treating food waste as the fifth invention, wherein the water-soluble peroxide is a peroxo acid salt.
【0011】第7発明は、上記ペルオキソ酸塩は、ペル
オキソ炭酸塩、ペルオキソほう酸塩、または他の無機弱
酸塩の過酸化水素付加物の中から選ばれた1種あるいは
2種以上の成分の混合物を1成分とする第6発明として
の生ごみ処理方法である。In a seventh aspect of the invention, the peroxo acid salt is a mixture of one or more components selected from peroxocarbonates, peroxoborates, and hydrogen peroxide adducts of other inorganic weak acid salts. Is a method of treating food waste as a sixth invention.
【0012】第8発明は、上記水溶性過酸化物が、過酸
化水素水である第5発明としての生ごみ処理方法であ
る。An eighth invention is a method of treating food waste as the fifth invention, wherein the water-soluble peroxide is hydrogen peroxide solution.
【0013】第9発明は、上記塩基性電解質が、アルカ
リ金属の水酸化物塩又はアルカリ土類金属の水酸化物塩
である第4発明としての生ごみ処理方法である。A ninth invention is the method for treating food waste as the fourth invention, wherein the basic electrolyte is an alkali metal hydroxide salt or an alkaline earth metal hydroxide salt.
【0014】第10発明は、上記水酸化物塩が、水酸化
カルシウムである第9発明としての生ごみ処理方法であ
る。A tenth invention is a method for treating food waste as a ninth invention, wherein the hydroxide salt is calcium hydroxide.
【0015】第11発明は、上記塩基性電解質が、アル
カリ金属の無機弱酸塩またはアルカリ土類金属の無機弱
酸塩である第4発明としての生ごみ処理方法である。The eleventh invention is a method for treating food waste as the fourth invention, wherein the basic electrolyte is an inorganic weak acid salt of an alkali metal or an inorganic weak acid salt of an alkaline earth metal.
【0016】第12発明は、上記無機弱酸塩が、炭酸塩
である第11発明としての生ごみ処理方法である。A twelfth invention is a method for treating food waste as the eleventh invention, wherein the inorganic weak acid salt is a carbonate.
【0017】第13発明は、上記炭酸塩が、炭酸カリウ
ムである第12発明としての生ごみ処理方法である。A thirteenth invention is a method for treating food waste as a twelfth invention, wherein the carbonate is potassium carbonate.
【0018】第14発明は、上記塩基性電解質が、アル
カリ土類金属である第4発明としての生ごみ処理方法で
ある。A fourteenth invention is a method of treating food waste as a fourth invention, in which the basic electrolyte is an alkaline earth metal.
【0019】第15発明は、香料を前記処理助剤の他の
1成分として加えた第9発明〜第14発明の何れか1つ
の発明としての生ごみ処理方法である。A fifteenth invention is a method for treating food waste as an invention according to any one of the ninth invention to the fourteenth invention, wherein a fragrance is added as another component of the treatment aid.
【0020】第16発明は、生ごみを収納する収納部
と、その収納部に収納された前記生ごみを加熱乾燥する
ための加熱手段と、前記生ごみに対して前記加熱乾燥を
する際に、塩基性電解質を1成分とする処理助剤を前記
収納部に所定の時期に投入するための投入手段と、その
投入手段に供給される前記処理助剤を貯めておく貯め部
と、前記投入手段の動作を制御するための制御部とを備
えた生ごみ乾燥処理装置である。A sixteenth aspect of the present invention is a storage part for storing food waste, a heating means for heating and drying the food waste stored in the storage part, and a method for heating and drying the food waste. A charging means for charging a processing aid containing one component of a basic electrolyte into the storage part at a predetermined time, a storage part for storing the processing aid supplied to the charging means, and the charging part. And a control unit for controlling the operation of the means.
【0021】第17発明は、生ごみを収納する収納部
と、その収納部に収納された前記生ごみを加熱乾燥する
ための加熱手段と、前記収納部の外側に設けられ、前記
加熱手段により前記生ごみから分離された気体及び/又
は前記気体が凝縮されて生成された液体が通過する通路
部と、前記液体を貯留する貯留部とを備え、前記通路部
の全部又は一部、及び/又は前記貯留部に脱臭のための
処理助剤を配設可能とした生ごみ乾燥処理装置である。A seventeenth aspect of the present invention is a storage section for storing food waste, a heating means for heating and drying the food waste stored in the storage section, and a heating means provided outside the storage section. The gas separated from the garbage and / or a passage part through which a liquid generated by condensing the gas passes, and a storage part that stores the liquid, and all or part of the passage part, and / or Alternatively, it is a food waste drying apparatus in which a processing aid for deodorization can be arranged in the storage section.
【0022】第18発明は、上記処理助剤が、塩基性電
解質を1成分とする処理助剤である第17発明としての
生ごみ乾燥処理装置である。The eighteenth invention is the apparatus for drying food waste as the seventeenth invention, wherein the processing aid is a processing aid containing a basic electrolyte as one component.
【0023】第19発明は、上記処理助剤が、水溶性過
酸化物を1成分とする処理助剤である第17発明として
の生ごみ乾燥処理装置である。A nineteenth aspect of the present invention is the food waste drying treatment apparatus according to the seventeenth aspect, wherein the treatment aid is a treatment aid containing a water-soluble peroxide as one component.
【0024】第20発明は、上記通路部の一部とは、そ
の底部に設けられた排水口であり、前記処理助剤を前記
液体中に溶解させるようにした第18発明、又は第19
発明としての生ごみ乾燥処理装置である。In a twentieth aspect of the invention, a part of the passage portion is a drain port provided at a bottom portion thereof, and the processing aid is dissolved in the liquid.
It is an apparatus for drying food waste as an invention.
【0025】第21発明は、上記通路部の全部とは、そ
の内壁部の全部であり、前記通路部の一部とは、その内
壁側面上部又は、内壁側面部の少なくとも一部であり、
前記処理助剤を前記液体中に溶解させるようにした第1
8発明、又は第19発明としての生ごみ乾燥処理装置で
ある。In the twenty-first aspect of the invention, the entire passage portion is the entire inner wall portion thereof, and the portion of the passage portion is the upper portion of the inner wall side surface or at least a portion of the inner wall side surface portion,
A first processing aid for dissolving the processing aid in the liquid;
It is an apparatus for drying food waste as an eighth invention or a nineteenth invention.
【0026】第22発明は、上記処理助剤が、前記通路
部の内壁部の形状に一致するように加圧成型されている
第20発明、又は第21発明としての生ごみ乾燥処理装
置である。A twenty-second aspect of the invention is the apparatus for drying food waste as the twentieth aspect or the twenty-first aspect of the invention, wherein the treatment aid is pressure-molded so as to match the shape of the inner wall of the passage. .
【0027】第23発明は、上記処理助剤が、紙または
不織布の通水性材料内に納られている第20発明、又は
第21発明としての生ごみ乾燥処理装置である。A twenty-third aspect of the invention is a food waste drying apparatus as the twentieth aspect or the twenty-first aspect, wherein the treatment aid is contained in a water-permeable material such as paper or nonwoven fabric.
【0028】第24発明は、上記処理助剤が、コルゲ−
ト状に成型した不織布内に納められている第20発明、
又は第21発明としての生ごみ乾燥処理装置である。In a twenty-fourth aspect of the invention, the above-mentioned processing aid is a corrugated
The twentieth invention contained in a non-woven fabric molded into a tongue,
Alternatively, the food waste drying apparatus according to the twenty-first invention.
【0029】第25発明は、上記処理助剤が、溶出口を
有する樹脂製の処理助剤収納部材に納められている第2
0発明、又は第21発明としての生ごみ乾燥処理装置で
ある。A twenty-fifth aspect of the present invention is the second invention, wherein the processing aid is contained in a resin-made processing aid storage member having an elution port.
It is a garbage drying processing apparatus as 0th invention or 21st invention.
【0030】[0030]
【作用】本発明は、上述の生ごみを乾燥処理する処理方
法および装置をもって、乾燥処理後のごみあるいは凝縮
水からの臭気を低減する乾燥処理方法等を提供すること
を目的とする。It is an object of the present invention to provide a drying treatment method and the like for reducing the odor from the dust or condensed water after the drying treatment, by using the above-mentioned treatment method and apparatus for drying the garbage.
【0031】生ごみを加熱して乾燥処理する過程におい
て、生ごみに塩基性電解質を1成分とする処理助剤を添
加することにより、乾燥後のごみ臭気を低減する。食品
の酸化は含水状態に依存し、乾燥の進行にともない酸化
反応も進行することが分かっている。生ごみの乾燥処理
過程では、乾燥の進行にともない生ごみは酸化されやす
くなり、さらに加熱状態なので反応自体も進行しやす
い。乾燥生ごみの有機物が酸化されると、酢酸、プロピ
オン酸、吉草酸等の低分子の揮発性有機酸となる。乾燥
した処理後期は、悪臭有機酸多量に発生しごみに残留す
る。このことが、乾燥生ごみの臭気発生原因の1つとな
っている。生ごみ乾燥過程において、塩基性電解質を1
成分とする処理助剤を加えることで、酸化により発生し
た有機酸と添加した塩基成分が反応する。その結果、有
機酸が不揮発性となり、乾燥生ごみから発生する臭気を
大幅に低減する。In the process of heating and drying raw garbage, a processing aid having a basic electrolyte as one component is added to the raw garbage to reduce the odor of the dried garbage. It is known that the oxidation of food depends on the water content and the oxidation reaction also progresses as the drying progresses. In the process of drying food waste, the food waste is more likely to be oxidized with the progress of drying, and the reaction itself is more likely to proceed because it is in a heated state. When organic matter in dried food waste is oxidized, it becomes low molecular volatile organic acids such as acetic acid, propionic acid, and valeric acid. A large amount of malodorous organic acids are generated and remain in the waste in the latter stage of the treatment after drying. This is one of the causes of the odor generation of dry food waste. 1 basic electrolyte in the garbage drying process
By adding the processing aid as a component, the organic acid generated by the oxidation reacts with the added base component. As a result, the organic acid becomes non-volatile, and the odor generated from dried food waste is significantly reduced.
【0032】又、例えば、生ごみの収納部と、生ごみを
加熱する加熱手段と、水蒸気の凝縮部と、塩基性電解質
を1成分とする処理助剤の貯め部と、処理助剤の投入手
段を有する生ごみ乾燥処理装置では、生ごみに、処理中
に処理助剤を投入手段で最適条件で添加する。前記のよ
うに乾燥後期では、生ごみより有機酸が多量に発生す
る。しかしながら、乾燥後期に処理助剤を添加した場
合、水分が少ないため塩基性電解質と有機酸が効果的に
反応しない。又、乾燥処理前に添加した場合、有機酸成
分を多く含むごみでは、加熱乾燥初期で中和し効果が半
減する可能性がある。そこで投入手段で自動的に添加す
ることで、塩基性電解質が溶解できる最適条件での添加
が行える。さらに、処理助剤を添加する手間もはぶけ
る。Further, for example, a storage section for food waste, a heating means for heating the food waste, a condensation section for water vapor, a storage section for a processing aid containing one component of a basic electrolyte, and the introduction of the processing aid. In the food waste drying apparatus having a means, the processing aid is added to the food waste during processing by the charging means under the optimum conditions. As described above, in the latter stage of drying, a large amount of organic acid is generated from raw garbage. However, when the processing aid is added in the latter stage of drying, the basic electrolyte and the organic acid do not react effectively because the water content is small. If added before the drying treatment, the waste containing a large amount of organic acid components may be neutralized at the initial stage of heating and drying, and the effect may be halved. Therefore, by automatically adding by the charging means, the addition can be performed under the optimum conditions in which the basic electrolyte can be dissolved. Furthermore, the trouble of adding the processing aid can be saved.
【0033】生ごみを加熱して乾燥処理する過程におい
て、生ごみを加熱した時に発生した水蒸気の凝縮水に塩
基性電解質を1成分とする処理助剤を添加することによ
り、凝縮水臭を低減する。前記のように生ごみ乾燥過程
では、悪臭有機酸多量に発生する。これら有機酸は、生
ごみより加熱分離した水蒸気を凝縮する時、凝縮水に溶
解する。そのため、凝縮水は悪臭を発生することにな
る。そこで、凝縮水に塩基性電解質を1成分とする処理
助剤を添加することにより、溶解した有機酸と塩基成分
が反応する。その結果、有機酸が不揮発性となり、凝縮
水から発生する臭気を大幅に低減することができる。In the process of heating and drying raw garbage, the odor of condensed water is reduced by adding a processing aid having a basic electrolyte as one component to condensed water of steam generated when the raw garbage is heated. To do. As described above, a large amount of malodorous organic acids are generated in the process of drying food waste. These organic acids dissolve in condensed water when the steam separated by heating from food waste is condensed. Therefore, the condensed water produces a bad odor. Therefore, the dissolved organic acid and the basic component are reacted by adding a processing aid containing the basic electrolyte as one component to the condensed water. As a result, the organic acid becomes non-volatile, and the odor generated from condensed water can be significantly reduced.
【0034】又、例えば、生ごみの収納部と、生ごみを
加熱する加熱手段と、水蒸気の凝縮部と、凝縮水の貯水
部を有し、凝縮部底部排水口、貯水部のいずれかの場所
に塩基性電解質を1成分とする処理助剤を設けた生ごみ
乾燥処理装置では、凝縮水が処理助剤を通過することに
より、処理助剤が凝縮水中に溶解する。その結果、凝縮
水の臭気を低減するとともに、処理助剤凝縮水中に添加
する手間を省く。Further, for example, it has a storage section for food waste, a heating means for heating the food waste, a condensation section for water vapor, and a water storage section for the condensed water, and either of the bottom drain port of the condensation section or the water storage section. In a food waste drying treatment apparatus in which a treatment aid having a basic electrolyte as one component is provided at a location, the treatment aid dissolves in the condensed water when the condensed water passes through the treatment aid. As a result, the odor of condensed water is reduced and the time and effort of adding the processing aid to the condensed water is saved.
【0035】さらに、例えば、凝縮部の全面、側面上部
あるいは側面の少なくとも一部に塩基性電解質を1成分
とする処理助剤を設けた構成では、水蒸気が凝縮する
時、塩基性電解質が凝縮水に溶解する。その結果、前記
のように凝縮水の臭気を低減する。さらに、乾燥後のご
みの臭気も大幅に低減する。乾燥処理後に凝縮部に凝縮
水が残存する場合、凝縮水中に溶解した有機酸が揮発し
乾燥ごみに再付着する。加熱分離した水蒸気は凝縮部上
部より凝縮していく。そのため凝縮部上部あるいは全面
に塩基性電解質がある場合、凝縮と同時に凝縮水中の有
機酸成分を不揮発性にする。その結果、凝縮部に存在す
る凝縮水中の有機酸がほとんど不揮発性となり、乾燥ご
みに再付着することを防止するからである。Further, for example, in a structure in which a processing aid containing one component of a basic electrolyte is provided on the entire surface of the condensation section, the upper side surface or at least a part of the side surface, when the water vapor is condensed, the basic electrolyte is condensed water. Dissolve in. As a result, the odor of condensed water is reduced as described above. Furthermore, the odor of dust after drying is also significantly reduced. When the condensed water remains in the condensing part after the drying treatment, the organic acid dissolved in the condensed water is volatilized and redeposits on the dry dust. The steam separated by heating is condensed from the upper part of the condenser. Therefore, when the basic electrolyte is present in the upper part or the entire surface of the condensation part, the organic acid component in the condensed water is made non-volatile at the same time as the condensation. As a result, the organic acid in the condensed water existing in the condensation section becomes almost non-volatile, and it is prevented from reattaching to the dry dust.
【0036】生ごみを加熱して乾燥処理する過程におい
て、生ごみより加熱分離した凝縮水に水溶性過酸化物を
1成分とする処理助剤を添加することでも、凝縮水臭を
低減する。生ごみ乾燥過程では、有機酸のほかにも多量
に臭気が発生する。水溶性のあるアルデヒド類等の臭気
も、有機酸とともに凝縮水に溶解している。そのため、
凝縮水は悪臭を発生する。そこで、凝縮水に水溶性過酸
化物を1成分とする処理助剤を添加することで、凝縮水
中に活性酸素を発生させ、アルデヒドといった酸化しや
すい臭気成分を酸化させ、臭気強度の低い物質に反応さ
せる。その結果、凝縮水中の臭気成分を低減し、発生臭
気も抑えることができる。In the process of heating and drying raw garbage, the odor of condensed water can also be reduced by adding a processing aid containing water-soluble peroxide as one component to the condensed water that is heated and separated from the raw garbage. In the process of drying food waste, a large amount of odor is generated in addition to organic acids. The odors of water-soluble aldehydes and the like are also dissolved in the condensed water together with the organic acid. for that reason,
Condensed water gives off a bad odor. Therefore, by adding a processing aid containing a water-soluble peroxide as one component to the condensed water, active oxygen is generated in the condensed water to oxidize easily oxidizable odorous components such as aldehydes, and a substance with low odor intensity is formed. React. As a result, it is possible to reduce the odor component in the condensed water and suppress the generated odor.
【0037】生ごみを加熱して乾燥処理する過程におい
て、生ごみより加熱分離した凝縮水に水溶性過酸化物を
1成分とする処理助剤を添加した後、処理助剤添加後の
凝縮水が塩基性ならば酸性物質、酸性又は中性ならば塩
基性物質を付加し凝縮水を中和することで、凝縮水臭を
大幅に低減する。前記のように、水溶性過酸化物を凝縮
水に添加することで、凝縮水中の臭気成分を低減でき
る。しかし、水溶性過酸化物を溶解させた凝縮水が酸性
ならば、有機酸系の臭気成分が凝縮水より揮発する。
又、凝縮水が塩基性ならば、アンモニア、アミン類とい
った塩基性臭気成分が揮発してくる可能性がある。そこ
で過酸化物で中性臭気を低減した後に凝縮水を中性にす
ることで、塩基性および酸性臭気の揮発を抑えることが
できる。その結果、凝縮水中からの発生臭気を大幅に抑
えることができる。In the process of heating and drying the food waste, after adding a processing aid having a water-soluble peroxide as one component to the condensed water heated and separated from the food waste, the condensed water after the addition of the processing aid is added. If is basic, an acidic substance is added, and if acidic or neutral, a basic substance is added to neutralize the condensed water, thereby significantly reducing the odor of condensed water. As described above, by adding the water-soluble peroxide to the condensed water, the odor component in the condensed water can be reduced. However, if the condensed water in which the water-soluble peroxide is dissolved is acidic, the organic acid-based odorous component is volatilized from the condensed water.
If the condensed water is basic, basic odor components such as ammonia and amines may volatilize. Therefore, by reducing the neutral odor with a peroxide and then making the condensed water neutral, it is possible to suppress the volatilization of basic and acidic odors. As a result, the odor generated from the condensed water can be significantly suppressed.
【0038】以上のように処理することで、生ごみ乾燥
処理装置で処理したごみあるいは凝縮水からの臭気を低
減する乾燥処理を達成することができる。By performing the above-mentioned treatment, it is possible to achieve the drying treatment for reducing the odor from the dust or condensed water treated by the food waste drying treatment apparatus.
【0039】[0039]
【実施例】以下、本発明の実施例について図面とともに
説明する。 (実施例1)図1は本発明にかかる一実施に用いる生ご
み乾燥処理装置の要部縦断面図である。図1において、
1はステンレスで構成し空気断熱層をもつ断熱容器であ
る。2は試料の収納部で、ポリフェニルスルファイド樹
脂からなり断熱容器1から脱着が可能としてある。3は
試料を収納部2に出し入れするときに開閉する扉、4は
発生した水蒸気を凝縮させる凝縮部、5は凝縮部4下部
に配置した試料の撹はん部であり、駆動部5bとブレ−
ド5aからなる。6aは加熱部6に設けられたヒ−タ−
であり、収納部2の上部に位置し扉3に取り付けてあ
る。6bは扉3に取り付けた加熱部6のファンである。
7は凝縮水の排水口、8は収納部上部に位置するよう扉
3に設けた温度検出部である。9は加熱部6と駆動部5
bの動作制御部である。10は凝縮水の貯水部、11は
酸化触媒を用いた脱臭部である。Embodiments of the present invention will be described below with reference to the drawings. (Embodiment 1) FIG. 1 is a vertical cross-sectional view of a main part of a food waste drying apparatus used for carrying out the present invention. In FIG.
Reference numeral 1 is a heat insulating container made of stainless steel and having an air heat insulating layer. Reference numeral 2 denotes a sample storage portion, which is made of polyphenyl sulfide resin and can be detached from the heat insulating container 1. Reference numeral 3 is a door that opens and closes when the sample is taken in and out of the storage unit 2, 4 is a condensing unit for condensing the generated water vapor, and 5 is a stirring unit of the sample arranged under the condensing unit 4, which is a drive unit 5b and a shaker. −
Do 5a. 6a is a heater provided in the heating section 6
It is located at the upper part of the storage part 2 and is attached to the door 3. 6b is a fan of the heating unit 6 attached to the door 3.
Reference numeral 7 is a drainage port for condensed water, and 8 is a temperature detection unit provided on the door 3 so as to be located above the storage unit. 9 is a heating unit 6 and a driving unit 5
It is an operation control unit of b. Reference numeral 10 is a water storage section for condensed water, and 11 is a deodorization section using an oxidation catalyst.
【0040】次に動作を説明する。最初に扉3を開け、
収納部2に生ごみを入れる。この時、水酸化カルシウム
を1成分とする処理助剤も同時に投入した。次に加熱部
のヒ−タ−6aに通電して収納部2に入れた試料を加熱
し、さらにファン6bを作動させ熱風でも加熱し乾燥処
理を行った。熱風温度を温度検出部8により検出し、一
定温度で試料を加熱するように制御部9でヒ−タ−への
入力を調整した。この様に、生ごみ処理装置を作動さ
せ、生ごみの加熱乾燥をした。Next, the operation will be described. First open the door 3,
Put garbage in storage 2. At this time, a processing aid containing calcium hydroxide as one component was also added at the same time. Next, the heater 6a in the heating section was energized to heat the sample contained in the housing section 2, and the fan 6b was operated to heat the sample with hot air for drying treatment. The hot air temperature was detected by the temperature detection unit 8, and the input to the heater was adjusted by the control unit 9 so that the sample was heated at a constant temperature. In this way, the garbage processing device was operated to heat and dry the garbage.
【0041】食品の酸化は含水状態に依存し、乾燥の進
行にともない酸化反応も進行することが分かっている。
すなわち、乾燥生ごみは酸化されやすくなっており、か
つ、加熱条件下なので酸化反応も進行しやすい状態とな
る。乾燥生ごみの有機物が酸化し、酢酸、プロピオン
酸、吉草酸等の低分子の揮発性有機酸となる反応が起き
る。It is known that the oxidation of food depends on the water content and that the oxidation reaction also progresses as the drying progresses.
That is, the dried food waste is easily oxidized, and the oxidation reaction easily progresses under the heating condition. The organic matter in the dry food waste is oxidized, and a reaction occurs which becomes a low-molecular volatile organic acid such as acetic acid, propionic acid, and valeric acid.
【0042】乾燥処理後期では、これらの悪臭有機酸多
量に発生するため、ごみに残留することになる。これ
が、乾燥後生ごみの臭気発生の1原因となっている。そ
こで生ごみ乾燥過程において、塩基性電解質を1成分と
する処理助剤を加えて処理することにより、酸化により
発生した有機酸と塩基成分を反応させる。その結果、有
機酸が不揮発性となり、乾燥後の生ごみから発生する臭
気を大幅に低減する。In the latter stage of the drying treatment, a large amount of these malodorous organic acids are generated, so that they remain in the dust. This is one of the causes of the odor generation of raw garbage after drying. Therefore, in the process of drying food waste, a treatment aid having a basic electrolyte as one component is added for treatment to react the organic acid generated by oxidation with the base component. As a result, the organic acid becomes non-volatile, and the odor generated from the dried garbage is greatly reduced.
【0043】本実施例では、処理助剤の塩基性電解質と
して水酸化カルシウムを生ごみ700gに対して10g
添加し、乾燥処理した。乾燥処理後の臭気を官能評価し
た結果、処理助剤を添加しない同じ生ごみ処理時と比較
して、大幅に低減できることが分かった。In this example, calcium hydroxide was used as a basic electrolyte as a processing aid in an amount of 10 g per 700 g of garbage.
Added and dried. As a result of sensory evaluation of the odor after the drying treatment, it was found that the odor can be significantly reduced as compared with the same garbage treatment without the addition of the treatment aid.
【0044】処理助剤添加時の乾燥生ごみを水につけた
場合(乾燥ごみ10gに対して水100g)、PHが4
付近となった。処理助剤を用いたものは、PHが9付近
であった。ごみ全体が塩基性となり、有機酸が減少して
いることが分かる。又、処理助剤として炭酸カリウムを
用いた場合も同様に、乾燥ごみの臭気減少することが分
かった。When the dry food waste added with the processing aid is soaked in water (10 g of dry waste to 100 g of water), the PH is 4
It became the neighborhood. With the treatment aid, the pH was around 9. It can be seen that the entire waste becomes basic and the organic acid is reduced. Also, it was found that when potassium carbonate was used as a processing aid, the odor of dry waste was similarly reduced.
【0045】乾燥後のごみは、地中に生めることで堆肥
化し、肥料として用いることができる。処理助剤添加で
乾燥ごみを塩基性にすることで、土壌改良の効果ももつ
ことになる。さらにカルシウム、カリウム、マグネシウ
ム塩等の植物の必須元素化合物を塩基性電解質として用
いた場合、肥料としての利用価値も向上させることがで
きる。The dried waste can be composted by growing it underground and used as a fertilizer. By adding a processing aid to make dry waste basic, it also has the effect of improving soil. Further, when a plant essential element compound such as calcium, potassium or magnesium salt is used as the basic electrolyte, the utility value as a fertilizer can be improved.
【0046】なお、本実施例では処理助剤として水酸化
カルシウムを10g添加したが、添加量はごみの量に応
じ、処理後のごみが塩基性となる範囲で調整し添加すれ
ば前記の効果が得られる。In this example, 10 g of calcium hydroxide was added as a processing aid. However, the addition amount should be adjusted according to the amount of dust within the range in which the dust after treatment becomes basic, and the above effect is obtained. Is obtained.
【0047】又、処理助剤成分が水溶し塩基性を示すも
のならば、どのようなものでも良い。例えば、アルカリ
金属又はアルカリ土類金属の水酸化物塩、アルカリ金属
又はアルカリ土類金属の無機弱酸塩、アルカリ金属の炭
酸塩、等、要するにアルカリ金属の化合物やアルカリ土
類金属の化合物、あるいは、アルカリ土類金属でも良
く、本実施例と同様の効果が得られる。Any treatment aid component may be used as long as it is water-soluble and basic. For example, a hydroxide salt of an alkali metal or an alkaline earth metal, an inorganic weak acid salt of an alkali metal or an alkaline earth metal, a carbonate of an alkali metal, etc., that is, a compound of an alkali metal or a compound of an alkaline earth metal, or, Alkaline earth metal may be used, and the same effect as this embodiment can be obtained.
【0048】さらに、これらの塩基性電解質を2成分以
上に混合して添加しても良い。Further, these basic electrolytes may be added as a mixture of two or more components.
【0049】又、塩基性電解質の他にバニリン、シネオ
−ル等の香料を含む処理助剤を添加した場合、乾燥ごみ
臭をマスキングし悪臭を感覚的に防止できる。When a processing aid containing a fragrance such as vanillin or cineole is added in addition to the basic electrolyte, dry odor can be masked and malodor can be sensuously prevented.
【0050】これら、処理助剤の1成分あるいは2成分
以上を混合し、錠剤として成型したものを添加すること
で、処理助剤の取扱い性を向上できる。The handling property of the processing aid can be improved by mixing one or two or more of these processing aids and adding the one molded into a tablet.
【0051】又、塩基性電解質を1成分とする処理助剤
に限らず、例えば、水溶性過酸化物を1成分とする処理
助剤を添加しても良く、生ごみ又は乾燥ごみが塩基性を
示す場合は、上記と同様の効果を得る。 (実施例2)次に、他の本発明の実施例を図面を用いて
説明する。Further, the processing aid is not limited to the one containing a basic electrolyte as a component, and for example, a processing aid containing one component of a water-soluble peroxide may be added. In case of, the same effect as above is obtained. (Embodiment 2) Next, another embodiment of the present invention will be described with reference to the drawings.
【0052】図2は、本発明にかかる一実施例の生ごみ
乾燥処理装置の要部縦断面図である。FIG. 2 is a longitudinal sectional view of the essential parts of a food waste drying apparatus according to an embodiment of the present invention.
【0053】実施例1とほぼ同一構成部の装置を用いた
ので、その部分の詳細な説明は省略する。実施例1と異
なる主な点は、処理助剤の投入手段として、処理助剤の
貯め部のボンベ部12を有し、ノズル13を扉3内に有
する点である。なお、ボンベ部12はボンベ内部を高圧
にしており、圧力差を利用して処理助剤をノズル13よ
り吹き出す。又、ボンベ部12はボンベ12aと制御部
12bからなり、自動的にノズル13に処理助剤を送る
構成となっている。Since a device having substantially the same structure as that of the first embodiment is used, detailed description of that part is omitted. The main difference from the first embodiment is that as a means for introducing the processing aid, it has a cylinder part 12 as a storage part of the processing aid and a nozzle 13 in the door 3. The inside of the cylinder 12 has a high pressure, and the processing aid is blown out from the nozzle 13 by utilizing the pressure difference. Further, the cylinder unit 12 is composed of a cylinder 12a and a control unit 12b, and is configured to automatically send the processing aid to the nozzle 13.
【0054】実施例2では、実施例1とほぼ同様に生ご
みを処理した。異なる点は、生ごみ乾燥過程でボンベ部
12の処理助剤を、ノズル13より生ごみに吹き付ける
過程を設けた点である。なお、今回は炭酸カリウム水溶
液を処理助剤として用いた。In Example 2, raw garbage was treated in substantially the same manner as in Example 1. The difference is that a process of spraying the processing aid of the cylinder portion 12 onto the raw garbage from the nozzle 13 is provided in the raw garbage drying process. In addition, this time, the potassium carbonate aqueous solution was used as a processing aid.
【0055】実施例1で示すように、乾燥後期では、生
ごみより有機酸が多量に発生する。しかしながら、乾燥
後期に処理助剤を加えるた場合、水分が少ないため塩基
性電解質と有機酸が効果的に反応しなかった。又、ごみ
中に酢酸を多くふくむドレッシング等が多量に混入する
場合がある。このようなごみでは乾燥処理前に添加した
場合、生ゴミ中の有機酸成分と乾燥初期で中和し、効果
が半減することがあった。さらに、乾燥処理前に粉末状
の処理助剤を生ごみ上部にふりかけた場合、生ごみ表面
に水分が少ないため処理助剤が溶解せず、ファンからの
風により、凝縮部等に吹き飛ばされてしまった。そこで
本実施例のように、投入手段で自動的に加熱乾燥過程で
生ごみに添加することで、塩基性電解質の処理助剤がご
みに溶解付着する加熱乾燥中期での添加が行えることに
なる。さらに、有機酸がある程度減少する加熱乾燥中期
に添加することで、生ごみの種類によらず塩基性電解質
の処理助剤の臭気低減効果を引き出すことができた。乾
燥中期では、生ごみより水分がしみでて処理助剤が溶解
しやすくなるため、ファンからの風により凝縮部等に吹
き飛ばされてしまうことも防止できた。又、処理助剤を
添加する手間もはぶくことができた。As shown in Example 1, in the latter stage of drying, a large amount of organic acid is generated from garbage. However, when the processing aid was added in the latter stage of drying, the basic electrolyte and the organic acid did not react effectively due to the low water content. In addition, a large amount of dressing containing a large amount of acetic acid may be mixed in the waste. When such waste is added before the drying treatment, it may be neutralized with the organic acid component in the garbage at the initial stage of drying, and the effect may be halved. Furthermore, if a powdered processing aid is sprinkled on top of the garbage before the drying process, the processing aid will not dissolve due to the low water content on the garbage surface, and it will be blown off by the wind from the fan to the condensation part, etc. Oops. Therefore, as in the present example, by automatically adding to the garbage in the heating and drying process by the charging means, the processing aid of the basic electrolyte can be added in the middle heating and drying stage in which the processing aid dissolves and adheres to the garbage. . Furthermore, by adding it in the middle of heating and drying when the organic acid decreases to some extent, it was possible to bring out the odor reducing effect of the processing aid of the basic electrolyte regardless of the type of food waste. In the mid-drying period, the processing aid is more likely to dissolve due to water stains than kitchen waste, so that it is possible to prevent the processing aid from being blown off by the wind from the fan. In addition, the trouble of adding the processing aid could be saved.
【0056】なお、本実施例では、処理助剤として炭酸
カリウム水溶液を用いたが、処理助剤の1成分が水溶し
塩基性を示す化合物の水溶液あるいはその粉末ならば、
どのようなもので良い。例えば、アルカリ金属又はアル
カリ土類金属の水酸化物塩、アルカリ金属又はアルカリ
土類金属の無機弱酸塩、アルカリ金属の炭酸塩、等、要
するにアルカリ金属の化合物やアルカリ土類金属の化合
物、あるいは、アルカリ土類金属でも良く、本実施例と
同様の効果がえられる。In this example, an aqueous solution of potassium carbonate was used as the processing aid, but if one component of the processing aid is an aqueous solution of a compound showing basicity or its powder,
Anything is fine. For example, a hydroxide salt of an alkali metal or an alkaline earth metal, an inorganic weak acid salt of an alkali metal or an alkaline earth metal, a carbonate of an alkali metal, etc., that is, a compound of an alkali metal or a compound of an alkaline earth metal, or, Alkaline earth metal may be used, and the same effect as this embodiment can be obtained.
【0057】さらに、これらの塩基性電解質を2成分以
上に混合して添加しても良い。Further, these basic electrolytes may be added as a mixture of two or more components.
【0058】又、処理助剤の投入手段として、圧力差を
利用して処理助剤を生ごみに吹き付ける構成としたが、
重力を利用し生ごみ収納部上部に設けた処理助剤の貯め
部から処理助剤を落下させ、ごみ中に添加する構成とし
てももちろん良い。 (実施例3)次に、更に他の本発明の実施例を図1を用
いて説明する。Further, as the means for introducing the processing aid, the processing aid is sprayed on the garbage by utilizing the pressure difference.
It is of course also possible that the processing aid is dropped from the storage part of the processing aid provided at the upper part of the garbage storage part by using gravity and is added into the waste. (Embodiment 3) Next, still another embodiment of the present invention will be described with reference to FIG.
【0059】実施例1と同一構成部の装置を用いたの
で、その部分の詳細な説明は省略する。Since a device having the same structure as that of the first embodiment is used, detailed description of that part is omitted.
【0060】実施例3では、実施例1とほぼ同様に生ご
みを処理した。異なる主な点は、生ごみより加熱分離し
た水蒸気の凝縮水に、塩基性電解質を1成分とする処理
助剤を添加したことである。In Example 3, raw garbage was treated in substantially the same manner as in Example 1. The main difference is that a processing aid having a basic electrolyte as one component is added to condensed water of steam separated by heating from food waste.
【0061】実施例1で示すように、生ごみ乾燥過程で
は、悪臭有機酸多量に発生する。生ごみより加熱分離し
た水蒸気を凝縮する時、これら有機酸は凝縮水に溶解す
る。そのため、凝縮水は悪臭を発生する。そこで本実施
例では、凝縮水に炭酸カリウムを処理助剤として、凝縮
水20gに対して0.5g添加した。その結果、凝縮水
中の有機酸と添加した塩基成分が反応する。そして有機
酸が不揮発性となり、処理助剤添加前と比較して、凝縮
水から発生する臭気を大幅に低減することができた。
又、処理助剤添加前は凝縮水のPHが4付近であった
が、処理助剤添加後はPHが9となることから、有機酸
が揮発しにくい条件になっているといえる。As shown in Example 1, a large amount of malodorous organic acid is generated in the process of drying food waste. These organic acids dissolve in the condensed water when the steam separated by heating from the garbage is condensed. Therefore, the condensed water produces a bad odor. Therefore, in this example, 0.5 g of condensed carbonate was added to 20 g of condensed water as a processing aid. As a result, the organic acid in the condensed water reacts with the added base component. Then, the organic acid became non-volatile, and the odor generated from the condensed water could be significantly reduced as compared with that before the addition of the processing aid.
Further, the pH of the condensed water was around 4 before the addition of the processing aid, but after the addition of the processing aid, the pH was 9, so it can be said that the conditions are such that the organic acid is less likely to volatilize.
【0062】なお、添加する塩基性電解質の量は、凝縮
水の量に応じ凝縮水のPHが7以上となるように添加す
れば本実施例の効果が得られる。The effect of the present embodiment can be obtained by adding the basic electrolyte so that the pH of the condensed water becomes 7 or more according to the amount of the condensed water.
【0063】又実施例1同様、処理助剤の1成分が水溶
し塩基性を示すものならば、どのような処理助剤でも良
い。As in Example 1, any processing aid may be used as long as one component of the processing aid is water-soluble and basic.
【0064】さらに、ごみと凝縮水両方に塩基性電解質
を1成分とする処理助剤の添加を併用することも可能で
ある。 (実施例4)次に、更に他の本発明の実施例を図3を用
いて説明する。Further, it is possible to use a processing aid containing a basic electrolyte as one component in both the waste and the condensed water. (Embodiment 4) Still another embodiment of the present invention will be described with reference to FIG.
【0065】図3は、本発明にかかる一実施例の生ごみ
乾燥処理装置の要部縦断面図である。FIG. 3 is a longitudinal sectional view of the essential parts of a food waste drying apparatus according to an embodiment of the present invention.
【0066】実施例1とほぼ同一構成部の装置を用いた
ので、その部分の詳細な説明は省略する。異なる主な点
は、凝縮部4下部(本発明の通路部)に塩基性電解質を
1成分とする処理助剤の設置部14を設けたことであ
る。なお、処理助剤15として、不織布内に納めた水酸
化カルシウムを設置部14に設置した。Since a device having substantially the same structure as that of the first embodiment is used, detailed description of that part is omitted. The main difference is that a processing aid installation section 14 containing a basic electrolyte as one component is provided below the condensation section 4 (the passage section of the present invention). As the processing aid 15, calcium hydroxide contained in the non-woven fabric was set in the setting section 14.
【0067】実施例4では、実施例1とほぼ同様に生ご
みを処理した。異なる点は、生ごみを加熱して乾燥処理
する過程において、生ごみより加熱分離した水蒸気の凝
縮水が凝縮部4下部に設けた処理助剤の設置部14の水
酸化カルシウムを通過することで、凝縮水中に水酸化カ
ルシウムが溶解する。その結果、処理助剤を凝縮水中に
添加する手間が省かれて、実施例3に示す凝縮水の臭気
を低減することができた。In Example 4, raw garbage was treated in substantially the same manner as in Example 1. The difference is that in the process of heating and drying raw garbage, the condensed water of the steam heated and separated from the raw garbage passes through calcium hydroxide in the treatment aid installation portion 14 provided at the lower portion of the condensation portion 4. , Calcium hydroxide dissolves in condensed water. As a result, the trouble of adding the processing aid to the condensed water was saved, and the odor of the condensed water shown in Example 3 could be reduced.
【0068】なお、凝縮水の通路(本発明の通路部)で
ある排水口、あるいは貯水部のいずれかの場所に、塩基
性電解質を1成分とする処理助剤を設けるか、あるいは
投入することで、本実施例の効果を得ることができる。It should be noted that a treatment aid containing a basic electrolyte as a component is provided or added at any of the drainage port which is the passage of the condensed water (the passage portion of the present invention) or the water storage portion. Thus, the effect of this embodiment can be obtained.
【0069】又、処理助剤は、錠剤状、顆粒状、粉末状
等のものをそのまま用いても同様の効果が得られる。 (実施例5)次に、更に他の本発明の実施例を図4を用
いて説明する。The same effect can be obtained even if the processing aid is used in the form of tablet, granule, powder or the like as it is. (Embodiment 5) Next, still another embodiment of the present invention will be described with reference to FIG.
【0070】図4は、本発明にかかる一実施例の生ごみ
乾燥処理装置の要部縦断面図である。FIG. 4 is a longitudinal sectional view of the essential parts of a food waste drying apparatus according to an embodiment of the present invention.
【0071】実施例1とほぼ同一構成部の装置を用いた
ので、その部分の詳細な説明は省略する。異なる主な点
は、凝縮部4側面上部一面(本発明の通路部)に塩基性
電解質を1成分とする処理助剤の設置部14を設けた点
である。なお、本実施例では、処理助剤15として不織
布内に納めた水酸化カルシウムを凝縮部4の上部の内面
周囲に沿って設置した点である。Since a device having substantially the same structure as that of the first embodiment is used, detailed description of that part is omitted. The main difference is that a processing aid installation portion 14 containing a basic electrolyte as one component is provided on the entire upper surface of the side surface of the condenser portion 4 (the passage portion of the present invention). In this embodiment, calcium hydroxide contained in the nonwoven fabric as the processing aid 15 is installed along the periphery of the inner surface of the upper part of the condensation part 4.
【0072】本実施例の構成で生ごみの乾燥を行った場
合、上記構成を有しない場合と比較して、凝縮水臭が低
減するとともに、乾燥ごみ臭も大幅に低減することが確
認できた。これは、次のような理由によるものである。It was confirmed that when the raw garbage was dried with the constitution of this embodiment, the odor of condensed water was reduced and the odor of dried dust was significantly reduced as compared with the case where the above constitution was not provided. . This is due to the following reasons.
【0073】すなわち、生ごみから加熱分離された水蒸
気は、凝縮部上部より凝縮していく。凝縮部上部に塩基
性電解質がある場合、凝縮と同時に凝縮水中の有機酸成
分は塩基と反応するため不揮発性になる。その結果、凝
縮水の臭気は低減する。又、乾燥処理後に凝縮部に凝縮
水が残存する場合、従来であれば、凝縮水中に溶解した
有機酸が揮発し乾燥ごみに再付着することもある。しか
し、凝縮部に存在する凝縮水中の有機酸がほとんど不揮
発性となる本実施例では、乾燥ごみに再付着することを
防止したからである。That is, the water vapor heated and separated from the garbage is condensed from the upper part of the condenser. When the basic electrolyte is present in the upper part of the condensation part, the organic acid component in the condensed water reacts with the base simultaneously with the condensation, so that it becomes non-volatile. As a result, the odor of condensed water is reduced. Further, when the condensed water remains in the condensing part after the drying treatment, conventionally, the organic acid dissolved in the condensed water may be volatilized and redeposit on the dry dust. However, in the present embodiment in which the organic acid in the condensed water existing in the condensation section is almost non-volatile, redeposition on the dry dust was prevented.
【0074】なお、本実施例では、処理助剤として水酸
化カルシウムを用いたが、他の塩基性電解質でも同様な
効果を得る。又、処理助剤を不織布内に納めたる構成を
とったが、これに限らず、例えば、凝縮部側面上部形状
に一致するように処理助剤自体を加圧成型したもの、処
理助剤を不織布内に納めコルゲ−ト状に成型したもの、
処理助剤を紙に納めたもの、処理助剤を溶出口を設けた
樹脂成型品に納めたもの等のように、凝縮水中に処理助
剤が溶解するならばどのような構成でも良く、又、本実
施例と同様の効果が得られる。又、処理助剤の設置場所
は、側面上部に限らず、例えば、凝縮部全面あるいは凝
縮部側面に層状設置し、より処理助剤が溶解するような
構成でももちろん良い。 (実施例6)次に、更に他の本発明の実施例を図1を用
いて説明する。In this example, calcium hydroxide was used as the processing aid, but other basic electrolytes can also produce similar effects. Further, although the processing aid is contained in the nonwoven fabric, the present invention is not limited to this. For example, the processing aid itself is pressure-molded so as to match the shape of the upper side surface of the condensation part, or the processing aid is a nonwoven fabric. It is housed inside and molded into a corrugated shape,
Any configuration may be used as long as the processing aid is dissolved in the condensed water, such as the one in which the processing aid is stored in paper, the one in which the processing aid is stored in a resin molded product having an elution port, or the like. The same effect as the present embodiment can be obtained. The location of the processing aid is not limited to the upper part of the side surface, but may be, for example, layered on the entire surface of the condensation part or on the side surface of the condensation part so that the processing aid is more dissolved. (Embodiment 6) Next, still another embodiment of the present invention will be described with reference to FIG.
【0075】実施例1と同一構成部の装置を用いたの
で、その部分の詳細な説明は省略する。Since a device having the same structure as that of the first embodiment is used, detailed description of that part is omitted.
【0076】実施例6では、実施例1とほぼ同様に生ご
みを処理した。異なる主な点は、生ごみを加熱して乾燥
処理する過程において、生ごみより加熱分離した水蒸気
の凝縮水に水溶性過酸化物の処理助剤を添加したことで
ある。In Example 6, raw garbage was treated in substantially the same manner as in Example 1. The main difference is that in the process of heating and drying food waste, a water-soluble peroxide processing aid is added to the condensed water of steam separated from the food waste by heating.
【0077】生ごみ乾燥過程では、有機酸のほかにも多
量に臭気が発生する。凝縮水の溶解有機成分を定性分析
した結果、水溶性のあるアルデヒド類等の臭気も、有機
酸とともに凝縮水に溶解していることが分かった。本実
施例では、生ごみより加熱分離した凝縮水に凝縮水10
0gに対して、ペルオキソ炭酸ナトリウムを処理助剤と
して1g添加した。凝縮水臭気を処理助剤添加前後で官
能評価したところ、処理助剤添加後臭気は穏やかになる
ことがわかった。又、ガスクロマトグラフィ−で凝縮水
の溶解成分を定量分析したところ、添加前にあったアセ
トアルデヒドを示すピ−クが、添加後認められなかっ
た。すなわち、ペルオキソ炭酸ナトリウムは、凝縮水に
溶解すると水中に活性酸素を発生させ、アルデヒドとい
った酸化しやすい臭気成分を酸化し臭気強度の低い物質
に反応させる。又、本実施例で用いたペルオキソ炭酸ナ
トリウムは水溶すると塩基性を示すことから、塩基性電
解質を溶解せた場合と同様に有機酸も不揮発性とする効
果もある。水溶性過酸化物の処理助剤を添加した結果、
凝縮水中の臭気成分が低減でき、発生臭気も抑えること
ができた。In the garbage drying process, a large amount of odor is generated in addition to the organic acid. As a result of qualitative analysis of dissolved organic components of condensed water, it was found that odors such as water-soluble aldehydes were also dissolved in condensed water together with organic acid. In the present embodiment, the condensed water that is heated and separated from the garbage is condensed water 10
To 0 g, 1 g of sodium peroxocarbonate was added as a processing aid. A sensory evaluation of the odor of condensed water before and after the addition of the processing aid revealed that the odor became mild after the addition of the processing aid. Further, when the dissolved component of the condensed water was quantitatively analyzed by gas chromatography, no peak showing acetaldehyde before the addition was found after the addition. That is, when sodium peroxocarbonate is dissolved in condensed water, active oxygen is generated in water, and oxidizable odorous components such as aldehydes are oxidized to react with substances having low odor intensity. Further, since sodium peroxocarbonate used in this example shows basicity when dissolved in water, it also has the effect of making the organic acid non-volatile as in the case of dissolving the basic electrolyte. As a result of adding a processing aid for water-soluble peroxide,
The odor component in the condensed water could be reduced, and the generated odor could be suppressed.
【0078】なお、本実施例では凝縮水100gに対し
て、ペルオキソ炭酸ナトリウムを処理助剤として1g添
加したが、凝縮水のPHが6.5以上になる量ならばど
のような割合で添加してもよい。又、ペルオキソ酸塩と
してペルオキソ炭酸ナトリウムを用いたが、ペルオキソ
ほう酸ナトリウムといった他のペルオキソ酸塩でも同様
の効果を得る。In the present example, 1 g of sodium peroxocarbonate was added as a processing aid to 100 g of condensed water, but at any ratio as long as the pH of condensed water is 6.5 or more. May be. Although sodium peroxocarbonate was used as the peroxoacid salt, similar effects can be obtained with other peroxoacid salts such as sodium peroxoborate.
【0079】又、過酸化水素水のような水溶性過酸化物
で、酸化性を有する化合物であっても同様な効果があ
る。Further, even a compound having an oxidizing property such as a water-soluble peroxide such as hydrogen peroxide water has the same effect.
【0080】又、本実施例では、人が水溶性過酸化物を
1成分とする処理助剤を添加する場合について説明した
が、これに限らず、例えば、図3あるいは図4で説明し
たように、不織布内に上記処理助剤を納めて所定の設置
部14等に配設するようにしてももちろん良く、同様の
効果を得る。 (実施例7)次に、更に他の本発明の実施例を図1を用
いて説明する。Further, in the present embodiment, the case where a person adds a processing aid having a water-soluble peroxide as one component has been described, but the present invention is not limited to this, and for example, as described in FIG. 3 or FIG. Of course, the processing aid may be contained in the non-woven fabric and disposed in the predetermined installation portion 14 or the like, and the same effect is obtained. (Embodiment 7) Next, still another embodiment of the present invention will be described with reference to FIG.
【0081】実施例1と同一構成部の装置を用いたの
で、その部分の詳細な説明は省略する。Since a device having the same structure as that of the first embodiment is used, detailed description of that part will be omitted.
【0082】実施例7では、実施例3とほぼ同様に生ご
みを処理した。異なる主な点は、生ごみより加熱分離し
た水蒸気の凝縮水に、水溶性過酸化物の処理助剤を添加
した後、酸性物質を付加し凝縮水を中和したことであ
る。In Example 7, raw garbage was treated in substantially the same manner as in Example 3. The main difference is that after adding a treatment aid for the water-soluble peroxide to the condensed water of steam separated by heating from food waste, an acidic substance is added to neutralize the condensed water.
【0083】本実施例では、生ごみを加熱して乾燥処理
する過程において、生ごみより加熱分離した凝縮水10
0gに対して、ペルオキソ酸ナトリウムを処理助剤とし
て1g添加した後、塩酸を適量加えて中和しPH7付近
になるように調整した。凝縮水にペルオキソ酸ナトリウ
ムを1成分とする処理助剤を添加しした場合、凝縮水中
のアルデヒドは酸化され減少する。又、凝縮水が塩基性
となるため有機酸の発生も抑えられる。しかしながら、
アミン、アンモニアといった塩基性臭気成分が揮発しや
すくなる。すなわち、処理した生ごみの種類によって
は、臭気が低減できない場合があった。又、鰯、鯖等の
魚類の生ごみを処理て得られた凝縮水に、ペルオキソ酸
ナトリウムを1成分とする処理助剤を添加した場合、凝
縮水は有機酸系の臭気からアミン系の臭気へと変化する
ことが確認できた。しかしながら、その凝縮水に塩酸を
加え中和させた場合、アミン系の臭気も不揮発性となり
臭気強度は低減した。すなわち、有機酸等の酸性、アミ
ン等の塩基性臭気、アルデヒド等の中性臭気の発生を抑
え、凝縮水中からの発生臭気を大幅に低減することがで
きた。生ごみを加熱して乾燥処理する過程において、生
ごみより加熱分離した凝縮水に水溶性過酸化物を凝縮水
に添加することで、凝縮水中の臭気成分を低減できる。
しかし、水溶性過酸化物を溶解させた凝縮水が酸性にな
った場合、有機酸系の臭気成分は凝縮水より揮発する。
又、凝縮水が塩基性になった場合、アンモニア、アミン
類といった塩基性臭気成分が揮発してきた。そこで過酸
化物で中性臭気を低減した後に、凝縮水を中性にするこ
とで塩基性、酸性臭気の揮発を抑える。その結果、凝縮
水中からの発生臭気を大幅に抑えることができた。In this embodiment, in the process of heating and drying raw garbage, the condensed water 10 heated and separated from the raw garbage is used.
To 0 g, 1 g of sodium peroxoate was added as a processing aid, and then an appropriate amount of hydrochloric acid was added to neutralize and adjust the pH to be around pH 7. When a processing aid containing sodium peroxoate as one component is added to the condensed water, the aldehyde in the condensed water is oxidized and reduced. Further, since the condensed water becomes basic, generation of organic acid can be suppressed. However,
Basic odor components such as amine and ammonia are likely to volatilize. That is, the odor may not be reduced depending on the type of processed garbage. In addition, when a processing aid containing sodium peroxoate as one component is added to the condensed water obtained by treating the raw garbage of fish such as sardines and mackerel, the condensed water changes from an organic acid odor to an amine odor. It was confirmed that it changed to. However, when hydrochloric acid was added to the condensed water to neutralize it, the amine odor was also non-volatile, and the odor intensity was reduced. That is, it was possible to suppress the generation of acidic odors such as organic acids, basic odors such as amines, and neutral odors such as aldehydes, and to significantly reduce the odor generated from condensed water. In the process of heating and drying raw garbage, by adding a water-soluble peroxide to the condensed water heated and separated from the raw garbage, the odorous component in the condensed water can be reduced.
However, when the condensed water in which the water-soluble peroxide is dissolved becomes acidic, the organic acid odor component volatilizes from the condensed water.
When the condensed water becomes basic, basic odor components such as ammonia and amines are volatilized. Therefore, after reducing the neutral odor with peroxide, the condensed water is neutralized to suppress the volatilization of basic and acidic odors. As a result, it was possible to significantly reduce the odor generated from the condensed water.
【0084】なお、本実施例では、水溶性酸化物として
ペルオキソ酸塩としてペルオキソ炭酸ナトリウムを用い
たが、ペルオキソほう酸ナトリウムといった他のペルオ
キソ酸塩、過酸化水素水のような水溶性過酸化物で酸化
性を有する化合物であってもかまわない。In this example, sodium peroxocarbonate was used as the peroxoacid salt as the water-soluble oxide, but other peroxoacid salts such as sodium peroxoborate and water-soluble peroxides such as hydrogen peroxide solution were used. It may be a compound having an oxidizing property.
【0085】又、本実施例では、初めに添加する処理助
剤として、水溶性過酸化物を1成分とする処理助剤を用
いる場合について、説明したが、これに限らず、例え
ば、塩基性電解質を1成分とする処理助剤を初めに用い
てももちろん良い。Further, in the present embodiment, the case where a processing aid having a water-soluble peroxide as one component is used as the processing aid to be added first has been described, but the present invention is not limited to this, and for example, a basic Of course, a processing aid having an electrolyte as one component may be used first.
【0086】又、中和剤として塩酸を用いたが、これに
限らず、例えば、水溶性過酸化物を添加したの地の凝縮
水のPHに応じ、酸性ならば水酸化ナトリウム、炭酸カ
リウムといった無機系の塩基性化合物、塩基性ならばほ
う酸、シュウ酸といったそれ自体臭気の少ない酸ならば
どのようなものでも良く、実施例と同様の効果がえられ
る。Although hydrochloric acid was used as the neutralizing agent, the present invention is not limited to this. For example, if acidic, sodium hydroxide, potassium carbonate, etc. can be used depending on the pH of the condensed water in the ground water. Inorganic basic compounds, and basic acids such as boric acid and oxalic acid may be used as long as they have little odor, and the same effects as those of the examples can be obtained.
【0087】上記のように本実施例によれば、生ごみを
加熱して乾燥処理する過程において、生ごみに塩基性電
解質を1成分とする処理助剤を添加することにより、生
ごみの酸化により発生した有機酸と塩基成分が反応する
ため有機酸が不揮発性となり、乾燥後の生ごみから発生
する臭気を低減する。As described above, according to this example, in the process of heating and drying food waste, the addition of a processing aid containing one component of the basic electrolyte to the food waste makes it possible to oxidize the food waste. The organic acid generated by the reaction with the basic component makes the organic acid non-volatile, and reduces the odor generated from the dried food waste.
【0088】又、生ごみの収納部と、生ごみを加熱する
加熱手段と、水蒸気の凝縮部と、塩基性電解質を1成分
とする処理助剤の貯め部と、処理助剤の投入手段を有す
る生ごみ乾燥処理装置では、生ごみに処理中に処理助剤
を投入手段で最適条件で添加する。その結果、生ごみの
酸化により発生した有機酸と塩基成分が反応するため有
機酸が不揮発性となり、乾燥後の生ごみから発生する臭
気を低減する。さらに、処理助剤を添加する手間が省け
る。Further, there are provided a storage portion for food waste, a heating means for heating the food waste, a water vapor condensing portion, a storage portion for a processing aid containing one component of the basic electrolyte, and a means for introducing the processing aid. In the apparatus for drying food waste, the processing aid is added to the food waste during processing by the charging means under the optimum conditions. As a result, the organic acid generated by the oxidation of the food waste reacts with the basic component, so that the organic acid becomes non-volatile and the odor generated from the dried food waste is reduced. Furthermore, the labor of adding a processing aid can be saved.
【0089】又、生ごみを加熱して乾燥処理する過程に
おいて、生ごみを加熱した時に発生した水蒸気の凝縮水
に塩基性電解質を1成分とする処理助剤を添加すること
により、凝縮水に溶解した有機酸と塩基成分が反応す
る。その結果、有機酸が不揮発性となり、凝縮水から発
生する臭気を低減する。In the process of heating and drying raw garbage, by adding a processing aid having a basic electrolyte as one component to the condensed water of steam generated when the raw garbage is heated, the condensed water is added to the condensed water. The dissolved organic acid reacts with the basic component. As a result, the organic acid becomes non-volatile, and the odor generated from condensed water is reduced.
【0090】又、生ごみの収納部と、生ごみを加熱する
加熱手段と、水蒸気の凝縮部と、凝縮水の貯水部を有
し、凝縮水の排水口、貯水部のいずれかの場所に塩基性
電解質を1成分とする処理助剤を設けた生ごみ乾燥処理
装置では、凝縮水が処理助剤を通過することにより、処
理助剤が凝縮水中に溶解する。その結果、処理助剤凝縮
水中に添加する手間を省き、凝縮水の臭気を低減する。
又、凝縮部全面、側面上部あるいは側面の1部に塩基性
電解質を1成分とする処理助剤を設けた構成では、凝縮
水に塩基性電解質が溶解し、前記のように凝縮水の臭気
を低減する。さらに、凝縮部に存在する凝縮水中の有機
酸がほとんど不揮発性にするため、乾燥ごみに再付着す
ることを防止し、乾燥後のごみの臭気も大幅に低減す
る。Further, it has a storage section for food waste, a heating means for heating the food waste, a condensation section for water vapor, and a water storage section for condensed water. In a food waste drying treatment apparatus provided with a treatment aid containing a basic electrolyte as one component, the treatment aid dissolves in the condensed water when the condensed water passes through the treatment aid. As a result, the labor of adding the processing aid to the condensed water is saved, and the odor of the condensed water is reduced.
In addition, in the structure in which the processing aid containing the basic electrolyte as one component is provided on the entire surface of the condensing part, the upper part of the side surface, or a part of the side surface, the basic electrolyte is dissolved in the condensed water to remove the odor of the condensed water as described above. Reduce. Furthermore, since the organic acid in the condensed water existing in the condensation part is made almost non-volatile, it is prevented from redepositing on the dry dust and the odor of the dry dust is significantly reduced.
【0091】又、生ごみを加熱して乾燥処理する過程に
おいて、生ごみより加熱分離した凝縮水に水溶性過酸化
物を1成分とする処理助剤を添加することで、凝縮水中
に活性酸素を発生させ、アルデヒドといった酸化しやす
い臭気成分を酸化させ、臭気強度の低い物質に反応させ
る。その結果、凝縮水中の臭気成分が低減でき、発生臭
気も抑える。In addition, in the process of heating and drying food waste, by adding a processing aid containing water-soluble peroxide as one component to the condensed water heated and separated from the food waste, active oxygen is added to the condensed water. Is generated, oxidizable odorous components such as aldehydes are oxidized and reacted with a substance having low odor intensity. As a result, the odorous components in the condensed water can be reduced and the generated odor can be suppressed.
【0092】又、生ごみを加熱して乾燥処理する過程に
おいて、生ごみより加熱分離した凝縮水に水溶性過酸化
物を1成分とする処理助剤を添加した後、処理助剤添加
後の凝縮水が塩基性ならば酸性物質、酸性又は中性なら
ば塩基性物質を付加し凝縮水を中和する。この処理方法
では、過酸化物で中性臭気を低減した後に、凝縮水を中
性にすることで塩基性、酸性臭気の揮発を抑える。その
結果、凝縮水中からの発生臭気を大幅に抑える。以上の
ように処理することで、生ごみ乾燥処理装置で処理した
ごみ、あるいはその処理過程で生成される凝縮水からの
臭気を低減する乾燥処理を達成することができる。In addition, in the process of heating and drying the food waste, after adding a processing aid having a water-soluble peroxide as one component to the condensed water heated and separated from the food waste, after adding the processing aid. If the condensed water is basic, an acidic substance is added, and if it is acidic or neutral, a basic substance is added to neutralize the condensed water. In this treatment method, after neutral odor is reduced by peroxide, condensed water is neutralized to suppress volatilization of basic and acidic odors. As a result, the odor generated from the condensed water is significantly suppressed. By performing the treatment as described above, it is possible to achieve the drying treatment for reducing the odor from the dust treated by the food waste drying treatment apparatus or the condensed water generated in the treatment process.
【0093】尚、上記実施例では、処理助剤の配設場所
を凝縮部の一部とした場合について説明したが、これに
限らず、例えば、収納部を断熱している断熱容器1と凝
縮部4との間に形成された通路空間あるいは断熱容器1
の壁面部等、要するに、生ごみから分離された気体及び
/又はその気体が凝縮されて生成された液体が通過する
部分でさえあれば、その場所を問わない。In the above embodiment, the case where the processing aid is disposed in a part of the condensing part has been described. However, the present invention is not limited to this. A passage space formed between the portion 4 and the heat insulating container 1
The location is not limited as long as it is a wall portion or the like, that is, a portion through which the gas separated from the garbage and / or the liquid generated by condensing the gas passes.
【0094】[0094]
【発明の効果】以上述べたことから明らかなように、本
発明は、生ごみの乾燥処理後のごみ、あるいは生ごみか
ら分離された凝縮水の臭気を従来に比べてより一層低減
出来るといった長所を有する。EFFECTS OF THE INVENTION As is clear from the above, the present invention has the advantage that the odor of dried garbage or the condensed water separated from the garbage can be further reduced as compared with the conventional one. Have.
【図1】本発明の第1、第3,第6および第7の実施例
における生ごみ乾燥処理装置の要部縦断面図FIG. 1 is a longitudinal sectional view of essential parts of a food waste drying apparatus according to first, third, sixth and seventh embodiments of the present invention.
【図2】本発明の第2の実施例における生ごみ乾燥処理
装置の要部縦断面図FIG. 2 is a longitudinal sectional view of essential parts of a food waste drying apparatus according to a second embodiment of the present invention.
【図3】本発明の第4の実施例における生ごみ乾燥処理
装置の要部縦断面図FIG. 3 is a longitudinal sectional view of essential parts of a food waste drying apparatus according to a fourth embodiment of the present invention.
【図4】本発明の第5の実施例における生ごみ乾燥処理
装置の要部縦断面図FIG. 4 is a longitudinal sectional view of essential parts of a food waste drying apparatus according to a fifth embodiment of the present invention.
2 収納部 4 凝縮部 6a 加熱部ヒ−タ− 6b 加熱部ファン 7 排水口 10 貯水部 12a ボンベ 12b 制御部 13 ノズル 15 処理助剤 2 Storage part 4 Condensing part 6a Heating part heater 6b Heating part fan 7 Drainage port 10 Water storage part 12a Cylinder 12b Control part 13 Nozzle 15 Processing aid
───────────────────────────────────────────────────── フロントページの続き (51)Int.Cl.6 識別記号 庁内整理番号 FI 技術表示箇所 F26B 9/06 Q 25/00 Z (72)発明者 鈴木 次郎 大阪府門真市大字門真1006番地 松下電器 産業株式会社内─────────────────────────────────────────────────── ─── Continuation of the front page (51) Int.Cl. 6 Identification number Reference number within the agency FI Technical indication location F26B 9/06 Q 25/00 Z (72) Inventor Jiro Suzuki, 1006 Kadoma, Kadoma, Osaka Prefecture Matsushita Denki Sangyo Co., Ltd.
Claims (25)
に収納された前記生ごみを加熱乾燥するための加熱手段
とを備えた生ごみ乾燥処理装置を用いて、前記生ごみを
前記収納部に収納し加熱乾燥をする際に、前記生ごみの
前記収納と同時期及び/又は異なる時期に前記収納部へ
脱臭のための処理助剤を投入することを特徴とする生ご
み処理方法。1. A food waste drying treatment apparatus comprising: a storage unit for storing food waste; and a heating means for heating and drying the food waste stored in the storage unit. A method for treating food waste, characterized in that, when the food waste is stored in a storage unit and heated and dried, a processing aid for deodorization is added to the storage unit at the same time and / or at a different time from the storage of the food waste. .
に収納された前記生ごみを加熱乾燥するための加熱手段
と、前記収納部の外側に設けられ、前記加熱手段により
前記生ごみから分離された気体及び/又は前記気体が凝
縮されて生成された液体が通過する通路部と、前記液体
を貯留する貯留部とを備えた生ごみ乾燥処理装置を用い
て、前記生ごみを前記収納部に収納し加熱乾燥をする際
に、前記生ごみの前記収納と同時期及び/又は異なる時
期に前記通路部及び/又は前記貯留部へ脱臭のための処
理助剤を投入することを特徴とする生ごみ処理方法。2. A storage unit for storing food waste, a heating means for heating and drying the food waste stored in the storage unit, and a heating unit provided outside the storage unit for the food waste. Using a food waste drying treatment apparatus provided with a passage part through which a liquid separated from the gas and / or a liquid produced by condensing the gas and a storage part for storing the liquid are used, When stored in a storage unit and heated and dried, a processing aid for deodorization is added to the passage unit and / or the storage unit at the same time and / or at a different time from the storage of the food waste. How to dispose of garbage.
基性を示す場合は、他の処理助剤として酸性物質を投入
し、又前記生ごみが酸性又は中性を示す場合は、他の処
理助剤として塩基性物質を投入することにより、前記生
ごみを中和させることを特徴とする請求項1、又は2記
載の生ごみ処理方法。3. After the processing aid is added, if the food waste is basic, an acidic substance is added as another processing aid, and if the food waste is acidic or neutral, The method for treating food waste according to claim 1 or 2, wherein the food waste is neutralized by adding a basic substance as another processing aid.
る処理助剤であることを特徴とする請求項1、2、又は
3記載の生ごみ処理方法。4. The method according to claim 1, 2 or 3, wherein the processing aid is a processing aid containing a basic electrolyte as one component.
する処理助剤であることを特徴とする請求項1、2、又
は3記載の生ごみ処理方法。5. The method for treating food waste according to claim 1, 2 or 3, wherein the treatment aid is a treatment aid containing a water-soluble peroxide as one component.
るとこを特徴とする請求項5記載の生ごみ処理方法。6. The method for treating food waste according to claim 5, wherein the water-soluble peroxide is a peroxo acid salt.
ペルオキソほう酸塩、または他の無機弱酸塩の過酸化水
素付加物の中から選ばれた1種あるいは2種以上の成分
の混合物を1成分とすることを特徴とする請求項6記載
の生ごみ処理方法。7. The peroxo acid salt is a peroxo carbonate,
The raw garbage treatment according to claim 6, wherein one component or a mixture of two or more components selected from hydrogen peroxide adducts of peroxoborate or other inorganic weak acid salt is used as one component. Method.
とこを特徴とする請求項5記載の生ごみ処理方法。8. The method for treating food waste according to claim 5, wherein the water-soluble peroxide is a hydrogen peroxide solution.
物塩又はアルカリ土類金属の水酸化物塩であることを特
徴とする請求項4記載の生ごみ処理方法。9. The method for treating food waste according to claim 4, wherein the basic electrolyte is an alkali metal hydroxide salt or an alkaline earth metal hydroxide salt.
ることを特徴とする請求項9記載の生ごみ処理方法。10. The method for treating food waste according to claim 9, wherein the hydroxide salt is calcium hydroxide.
弱酸塩またはアルカリ土類金属の無機弱酸塩であること
を特徴とする請求項4記載の生ごみ処理方法。11. The method for treating food waste according to claim 4, wherein the basic electrolyte is an inorganic weak acid salt of an alkali metal or an inorganic weak acid salt of an alkaline earth metal.
徴とする請求項11記載の生ごみ処理方法。12. The method of treating food waste according to claim 11, wherein the weak inorganic acid salt is a carbonate.
特徴とする請求項12記載の生ごみ処理方法。13. The method of treating food waste according to claim 12, wherein the carbonate is potassium carbonate.
あることを特徴とする請求項4記載の生ごみ処理方法。14. The method of treating food waste according to claim 4, wherein the basic electrolyte is an alkaline earth metal.
て加えたことを特徴とする請求項9〜14の何れか1つ
に記載の生ごみ処理方法。15. The method of treating food waste according to claim 9, wherein a fragrance is added as another component of the treatment aid.
部に収納された前記生ごみを加熱乾燥するための加熱手
段と、前記生ごみに対して前記加熱乾燥をする際に、塩
基性電解質を1成分とする処理助剤を前記収納部に所定
の時期に投入するための投入手段と、その投入手段に供
給される前記処理助剤を貯めておく貯め部と、前記投入
手段の動作を制御するための制御部とを備えたことを特
徴とする生ごみ乾燥処理装置。16. A storage unit for storing food waste, a heating means for heating and drying the food waste stored in the storage unit, and a basic material for heating and drying the food waste. Operation means of charging means for charging a processing aid containing one component of an electrolyte into the storage part at a predetermined time, a storage part for storing the processing aid supplied to the charging means, and operation of the charging means. And a control unit for controlling the food waste.
部に収納された前記生ごみを加熱乾燥するための加熱手
段と、前記収納部の外側に設けられ、前記加熱手段によ
り前記生ごみから分離された気体及び/又は前記気体が
凝縮されて生成された液体が通過する通路部と、前記液
体を貯留する貯留部とを備え、前記通路部の全部又は一
部、及び/又は前記貯留部に脱臭のための処理助剤を配
設可能としたことを特徴とする生ごみ乾燥処理装置。17. A storage unit for storing food waste, a heating means for heating and drying the food waste stored in the storage unit, and a heating unit provided outside the storage unit for the food waste. Gas and / or a passage part through which a liquid produced by condensing the gas passes, and a storage part for storing the liquid, and all or part of the passage part, and / or the storage An apparatus for drying food waste, characterized in that a processing aid for deodorization can be disposed in the portion.
する処理助剤であることを特徴とする請求項17記載の
生ごみ乾燥処理装置。18. The food waste drying treatment apparatus according to claim 17, wherein the treatment aid is a treatment aid containing a basic electrolyte as one component.
とする処理助剤であることを特徴とする請求項17記載
の生ごみ乾燥処理装置。19. The food waste drying treatment apparatus according to claim 17, wherein the treatment aid is a treatment aid containing a water-soluble peroxide as one component.
れた排水口であり、前記処理助剤を前記液体中に溶解さ
せるようにしたことを特徴とする請求項18、又は19
記載の生ごみ乾燥処理装置。20. The part of the passage is a drain port provided at the bottom of the passage, and the processing aid is dissolved in the liquid.
The described equipment for drying food waste.
であり、前記通路部の一部とは、その内壁側面上部又
は、内壁側面部の少なくとも一部であり、前記処理助剤
を前記液体中に溶解させるようにしたことを特徴とする
請求項18、又は19記載の生ごみ乾燥処理装置。21. The entire passage portion is the entire inner wall portion thereof, and the portion of the passage portion is an upper portion of the inner wall side surface or at least a portion of the inner wall side surface portion, and the processing aid is The food waste drying apparatus according to claim 18 or 19, wherein the food waste drying apparatus is adapted to be dissolved in the liquid.
状に一致するように加圧成型されていることを特徴とす
る請求項20、又は21記載の生ごみ乾燥処理装置。22. The apparatus for drying food waste according to claim 20, wherein the processing aid is pressure-molded so as to match the shape of the inner wall portion of the passage portion.
材料内に納られていることを特徴とする請求項20、又
は21記載の生ごみ乾燥処理装置。23. The food waste drying treatment apparatus according to claim 20 or 21, wherein the treatment aid is contained in a water-permeable material such as paper or nonwoven fabric.
不織布内に納められていることを特徴とする請求項2
0、又は21記載の生ごみ乾燥処理装置。24. The processing aid is contained in a corrugated non-woven fabric.
The apparatus for drying food waste according to 0 or 21.
処理助剤収納部材に納められていることを特徴とする請
求項20、又は21記載の生ごみ乾燥処理装置。25. The food waste drying treatment apparatus according to claim 20, wherein the processing aid is contained in a resin-made processing aid storage member having an elution port.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP07217894A JP3408313B2 (en) | 1994-04-11 | 1994-04-11 | Garbage drying equipment |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP07217894A JP3408313B2 (en) | 1994-04-11 | 1994-04-11 | Garbage drying equipment |
Publications (2)
Publication Number | Publication Date |
---|---|
JPH07275836A true JPH07275836A (en) | 1995-10-24 |
JP3408313B2 JP3408313B2 (en) | 2003-05-19 |
Family
ID=13481722
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
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JP07217894A Expired - Fee Related JP3408313B2 (en) | 1994-04-11 | 1994-04-11 | Garbage drying equipment |
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Cited By (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN100445676C (en) * | 2007-03-21 | 2008-12-24 | 同济大学 | A biological drying method for domestic waste |
CN114602928A (en) * | 2022-03-15 | 2022-06-10 | 电子科技大学中山学院 | Garbage recycling treatment process |
-
1994
- 1994-04-11 JP JP07217894A patent/JP3408313B2/en not_active Expired - Fee Related
Cited By (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN100445676C (en) * | 2007-03-21 | 2008-12-24 | 同济大学 | A biological drying method for domestic waste |
CN114602928A (en) * | 2022-03-15 | 2022-06-10 | 电子科技大学中山学院 | Garbage recycling treatment process |
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Publication number | Publication date |
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JP3408313B2 (en) | 2003-05-19 |
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