JP4633222B2 - Organic waste treatment methods - Google Patents

Organic waste treatment methods Download PDF

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Publication number
JP4633222B2
JP4633222B2 JP2000088905A JP2000088905A JP4633222B2 JP 4633222 B2 JP4633222 B2 JP 4633222B2 JP 2000088905 A JP2000088905 A JP 2000088905A JP 2000088905 A JP2000088905 A JP 2000088905A JP 4633222 B2 JP4633222 B2 JP 4633222B2
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organic waste
treatment
tank
biodegradable plastic
treatment tank
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JP2001269652A (en
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康一 植村
文哉 北内
とみ子 堀井
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Unitika Ltd
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Unitika Ltd
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Description

【0001】
【発明の属する技術分野】
本発明は、プラスチック製品が混入している生ごみ、汚泥、糞尿等の有機性廃棄物を、発酵・乾燥させてコンポスト化する方法に関するものである。
【0002】
【従来の技術】
生ごみや、汚泥、糞尿等の有機性廃棄物は、微生物によって比較的容易に処理することが可能であり、微生物処理によって減容させることができるとともに、処理物をコンポスト、飼料、土壌改良剤等としてリサイクルすることが可能である。近年、廃棄物の埋立地の減少と、農業における有機栽培の見直しにより、有機性廃棄物の微生物処理が盛んに行われるようになっている。
【0003】
また、従来は微生物分解が不可能なプラスチックを用いて製造されていた種々の袋やシートあるいは用具等も、分別等の手間をさけ、微生物処理を容易にする目的で、生分解性のプラスチックを原料として製造されたものが用いられるようになってきている。
【0004】
生分解性プラスチックには様々な種類があるが、一般的には使用中には分解しにくく、処理過程において容易に分解するものが望まれている。一方コンポスト化処理においては、通常60℃以上の温度が数日間続き、非常に活発な微生物分解が行われる。そのため、生分解性プラスチック製品を含む有機性廃棄物をコンポスト化処理することは、非常に効果的な処理方法であるといえる。
【0005】
【発明が解決しようとする課題】
しかしながら、生分解性プラスチック製品のなかには、60℃程度の温度では非常に分解の遅いものもあり、コンポスト化の処理条件によっては高温を十分維持できない場合もある。また、生ごみ袋等の生分解性製品が最も混入する可能性が高い、家庭用あるいは業務用厨芥に関わる、いわゆる生ごみ処理機の場合、処理時の温度は60℃以下であることが多く、また処理時間も短いため、実際には生分解性プラスチック製品を十分処理できないという問題があった。このような処理装置によって生分解性プラスチック製品を含む有機性廃棄物を処理した場合、混入している生分解性プラスチックが処理できないのみならず、生分解性プラスチック製品が撹拌羽根にからみついて故障の原因となったり、生分解性プラスチックでできた生ごみ袋等を用いた場合には袋内の有機性廃棄物が好適に処理されずに嫌気分解して腐臭を発することも問題となっていた。
【0006】
本発明は、生分解性プラスチック製品が混入している有機性廃棄物を効率よくコンポスト化する方法を提供することを目的としている。
【0007】
【課題を解決するための手段】
本発明者らは、このような事情に鑑みて鋭意検討を重ねた結果、生分解性プラスチック製品を含む生ごみ等の有機性廃棄物を70℃以下の温度で微生物分解処理するにあたり、75℃以上90℃以下の高温、相対湿度100%の高湿条件で1〜48時間処理する工程を組み込むことによって、好適に処理が可能なことを見出し、本発明に到達した。
【0008】
すなわち本発明は、生分解性プラスチック製品が混合された有機性廃棄物を収納する処理槽と、該処理槽内に空気を送り込むブロアーと、該処理槽内を加温することができる加温設備とを備えた有機性廃棄物処理装置を用いて、生分解性プラスチック製品が混合された有機性廃棄物を処理する方法において、主として有機性廃棄物の発酵分解を行う工程と、主として生分解性プラスチック製品の崩壊を行う工程とからなることを特徴とする有機性廃棄物の処理方法を要旨とするものである。
【0009】
以下、本発明を詳細に説明する。
本発明でいう生分解性プラスチック製品とは、生分解性のある樹脂で形成された製品であれば特に限定されるものではないが、具体的にはフィルム、シート、袋、紐、バンド、箱等の他、箸、フォーク、スプーン、皿等の各種食器類、服、帽子等の衣料品が挙げられる。
【0010】
生分解性プラスチック製品の原料としては、コラーゲン、ゼラチン、フィブリン、アルブミン、合成ポリペプチド、絹、羊毛等のポリペプチド、アミロース、デキストラン、アルギン酸、キチン、キトサン、木綿、麻、レーヨン、セルロース等の多糖類、ポリグリコール酸、ポリ乳酸、ポリグラクチン、ポリリンゴ酸、ポリ-ε-カプロラクトン、ポリ-3-ヒドロキシ酪酸、ポリ-3-ヒドロキシ吉草酸、ポリ-4-ヒドロキシ酪酸、ポリ-6-ヒドロキシヘキサン酸、ポリブチレンサクシネート、ポリエチレンサクシネート等のポリエステル等が挙げられるが、特にポリ乳酸を主原料とする製品に有効である。
【0011】
本発明でいう有機性廃棄物とは、有機性廃棄物で微生物分解できるものであれば特に限定しないが、家庭、レストラン等から排出される厨芥、食品加工場等から排出される加工残差、排水処理によって発生する有機性汚泥、畜糞等が挙げられる。
【0012】
本発明の処理方法で用いられる有機性廃棄物の処理装置としては、いわゆる生ごみ処理装置であればよいが、少なくとも有機性廃棄物を収納する処理槽と、該処理槽内に空気を送り込むブロアーと、該処理槽内を加温することができる加温設備とを備えたものでなければならず、該処理槽内を撹拌することができる撹拌手段を備えていることがさらに望ましい。
【0013】
このなかで、処理槽とは、有機性廃棄物を収容できればよく、容量や材質等特に限定されるものではないが、本発明においては、処理槽内を加温する必要があるため、容積としては、望ましくは10L以上5m3以下、さらに望ましくは20L以上1m3以下であり、材質としては高温に耐えることのでき、腐食に強い材質、例えばステンレスや耐熱・耐腐食性プラスチックを用いることが望ましい。
【0014】
ブロアーも特殊なものである必要はなく、内容物が嫌気的にならず乾燥に十分な容量があればよい。送気量としては、生分解性プラスチックの崩壊を主とする工程と、有機性廃棄物の発酵分解を主とする工程とで異なるが、1m3の処理槽あたり0.1〜10m3/minのものであればよい。
【0015】
加温設備としては槽自体を加熱あるいは加温するものでもよいし、送気する空気を加熱して槽内の温度を上昇させてもよい。
【0016】
撹拌手段とは、内容物が十分撹拌できるものであればよく、有機性廃棄物の処理装置に一般的に用いられているものでよい。具体的には、回転モーターの回転軸に撹拌翼が設けられた装置が挙げられる。この撹拌手段による撹拌により、内容物が撹拌され、好気的な発酵が起こると共に好適な乾燥が行われる。
【0017】
また、処理には特殊な分解菌を添加してもよいが、特に添加しなくても生ごみに付着している菌あるいは空気中の浮遊菌によって十分処理することが可能である。特に、処理槽中に前回処理した処理物が残った状態で次の投入を行う、いわゆる連続処理の場合は、分解菌の添加効果は薄い。
【0018】
また、水分調整剤、発酵基剤あるいは発酵助剤として、おがくず、バーク、籾殻、ゼオライト、木材チップ、米糠あるいはそれ以外の特殊な剤を用いても良いが、生ごみのみでの処理も可能である。
【0019】
本発明における、主として生分解性プラスチック製品の崩壊を行う工程とは、相対湿度を100%を維持しつつ槽内温度を75℃以上90℃以下とする工程である。この工程の主な目的は、混入している生分解性プラスチックを崩壊させ、主として有機性廃棄物の分解をおこなう工程において微生物分解しやすくするものである。通常の有機性廃棄物を処理する場合には、処理初期の槽内の相対湿度は90%以上となり、特に水分を加える必要はない。ただし、かなり乾燥したものを処理する場合、あるいは先に主として有機性廃棄物の分解をおこなう工程を行う場合には、水分を加えて、相対湿度を上昇させることが必要な場合がある。
【0020】
この工程での送気量は、相対湿度90%以上を維持することと、嫌気状態とならないことに留意することが望ましい。具体的には1m3の処理槽あたり0.1〜2m3/minが望ましく、0.2〜1m3/minがさらに望ましい。また、送気は槽内であればどこから行ってもよいが、全体に空気が行き渡るためには槽の底部あるいは撹拌羽根の裏側等から行うことが望ましい。このような高温高湿処理を行うことにより、生分解性プラスチックが効率よく崩壊する。
【0021】
この主として生分解性プラスチック製品の崩壊を行う工程の処理時間は1時間以上48時間以下が必要である。高温での長時間の処理は生分解性プラスチックの崩壊に関しては有効であるが、主として有機性廃棄物の分解を行う工程での微生物による有機性廃棄物ならびに崩壊した生分解性プラスチックの分解に支障をきたすためである。
【0022】
ここでいう、崩壊とは生分解性プラスチックが加水分解等により低分子化し強度が著しく低下し、形状を保てなくなることであり、モノマー自体の分解を意味するものではない。
【0023】
本発明でいう、主として有機性廃棄物の分解を行う工程とは、70℃以下の微生物反応に適した温度、具体的には30℃以上70℃以下が必要であり、望ましくは40℃以上65℃以下の温度で、有機性廃棄物並びに主として生分解性プラスチック製品の崩壊を行う工程にて崩壊した生分解性プラスチックを分解する工程である。主として生分解性プラスチック製品の崩壊を行う工程にて生分解性プラスチックは崩壊し低分子化しているため、本工程にて容易に分解される。また、有機性廃棄物も高温高湿条件下での処理によって微生物分解を受けやすくなっているため、処理が容易となる。
【0024】
この工程での送気量は、やや上昇させ、望ましくは1m3の処理槽当たり0.2〜10m3/min、さらに望ましくは0.5〜5m3/minとする。ただし、別に第三工程として乾燥工程を設ける場合には主として生分解性プラスチック製品の崩壊を行う工程と同様にして運転してもよい。また、処理物の含水率が十分高い場合や、送気量を高めても槽内の含水率が著しく低下しない場合にはさらに送気量を上げてもかまわない。
【0025】
本工程での微生物分解処理時間は、処理物の含水率が80%以下、望ましくは70%以下で30%を下回らない時間を6時間以上とすることが望ましく、8時間以上とすることがさらに望ましい。処理物の含水率が多いと良好な好気性処理が行えず、30%を下回ると、微生物活性が著しく低下するためである。
【0026】
本発明においては、主として生分解性プラスチック製品の崩壊を行う工程を行った後に、主として有機性廃棄物の分解を行う工程を行うことが必要である。連続的に生分解性プラスチック製品の混入した生ごみを処理する場合は前後逆に行ってもよい。
その場合は、生分解性プラスチック製品が初めの工程、すなわち主として有機性廃棄物の分解を行う工程では崩壊しないが、次に行う主として生分解性プラスチック製品の崩壊を行う工程によって崩壊し、連続的に行われる次のサイクルのなかの主として有機性廃棄物の分解を行う工程によって効果的に分解されるため、槽内に生分解性プラスチック製品が蓄積することはなく、良好な処理が可能となる。
【0027】
【実施例】
以下、本発明を具体的に説明する。
参考例1
生分解性プラスチックの崩壊挙動を調べるため以下の実験を行った。ポリ乳酸80量部と昭和高分子社製のビオノーレ20量部からなる高分子成分に可塑剤としてアセチルトリブチルクエン酸17量部と、酸化珪素(SiO2)5量部とからなるフィルム(特開平11-116788号公報の実施例1参照)を、相対湿度90%および100%の条件下、60℃、70℃、80℃の温度条件下に放置した。1、2、3、6、24、48時間後に室温に戻し、風乾した後、劣化・崩壊の程度を目視判定し、さらにモノマーの分子量を測定した。60℃及び70℃では相対湿度90%および100%両方において、すべての処理時間で、外観上全く変化がなかった。分子量は24時間までは60℃ではほとんど変化がなかったが、相対湿度100%、70℃、24時間の処理においてやや低下し、48時間後には60℃処理においてもやや低下した。処理温度を80℃としたものでは、相対湿度100%では2時間後には柔軟性がなくなり、6時間後には劣化が認められ、24時間後には袋の形態を保てず、ぼろぼろに崩壊した状態になった。相対湿度90%では相対湿度100%に比べて崩壊状態が悪く、24時間でも劣化は起こったが袋の形態を保っていた。図1に相対湿度100%、80℃処理における分子量変化を示す。処理時間と共に加水分解が起こり急速に低分子化することが明らかとなった。
【0028】
実施例1
上記の参考例と同じように作製したフィルムを熱圧着して作った生ごみ袋に厨芥1kgを入れたもの10袋を、撹拌羽根を持ち、処理槽下部より送気ができ、槽内を加温可能な生ごみ処理機(処理容量20L)に投入した。処理槽にはあらかじめ種コンポスト200gを加えておいた。厨芥投入後、撹拌羽根を停止したまま、10L/minで送気を行い、槽内が80℃となるまで加温を行った。このとき槽内の相対湿度は100%であった。5時間経過後、処理槽温度を60℃に下げ、送気量を20L/minに変更し、1rpmで撹拌を行いつつ、さらに24時間の処理を行った。生分解性プラスチックは80℃、5時間処理の間にかなり崩壊し、その後の60℃での撹拌によって、有機性廃棄物と崩壊した生分解性プラスチックは十分混ざり、良好な発酵が可能であった。試験終了後の処理物の含水率は40%でさらさらの発酵処理物となった。
【0029】
比較例1
実施例1と同様に、厨芥1kg入れた生分解性生ごみ袋10袋を、撹拌羽根を持ち、処理槽下部より送気ができ、槽内を加温可能な生ごみ処理機(処理容量20L)に投入した。処理槽にはあらかじめ種コンポスト200gを加えておいた。厨芥投入後、撹拌羽根を停止したまま、10L/minで送気を行い、槽内が60℃となるまで加温を行った。このとき槽内の相対湿度は100%であった。5時間経過後、送気量を20L/minに変更し、1rpmで撹拌を行いつつ、さらに24時間の処理を行った。試験終了後、槽内の生ごみ袋は原型をとどめており、一部が撹拌羽根にからみついた状態であった。また、一部の生ごみ袋は内容物が外部へ出ておらず、それらの中では生ごみが良好に処理されておらず、腐敗が起こっていた。
【0030】
【効果】
本発明によれば、生分解性プラスチックが混入した有機性廃棄物を効率的に充分発酵処理することができ、得られるコンポストも良好なものになる。
【図面の簡単な説明】
【図1】生分解性フィルムの崩壊工程(相対湿度100%、80℃処理)における分子量変化を示す図である。
[0001]
BACKGROUND OF THE INVENTION
The present invention relates to a method for composting organic waste such as food waste, sludge and manure mixed with plastic products by fermentation and drying.
[0002]
[Prior art]
Organic waste such as garbage, sludge, manure, etc. can be treated with microorganisms relatively easily and can be reduced by microbial treatment. It is possible to recycle as such. In recent years, microbial treatment of organic waste has been actively performed due to the reduction of waste landfill and the review of organic cultivation in agriculture.
[0003]
In addition, various bags, sheets, tools, etc. that were conventionally manufactured using plastics that cannot be decomposed by microorganisms can also be separated from biodegradable plastics for the purpose of facilitating microbial treatment. What was manufactured as a raw material has come to be used.
[0004]
There are various types of biodegradable plastics, but in general, it is desired that those that are difficult to decompose during use and easily decompose in the process. On the other hand, in the composting treatment, a temperature of 60 ° C. or higher usually lasts for several days, and very active microbial degradation is performed. Therefore, composting organic waste containing biodegradable plastic products can be said to be a very effective treatment method.
[0005]
[Problems to be solved by the invention]
However, some biodegradable plastic products are very slow to decompose at a temperature of about 60 ° C., and depending on the processing conditions for composting, the high temperature may not be sufficiently maintained. Also, in the case of so-called garbage processing machines that are most likely to be mixed with biodegradable products such as garbage bags, and are related to household or commercial waste, the temperature during processing is often 60 ° C or less. In addition, since the processing time is short, there is a problem that the biodegradable plastic product cannot actually be processed sufficiently. When organic waste containing biodegradable plastic products is treated with such a treatment device, not only the biodegradable plastics that are mixed in cannot be treated, but also the biodegradable plastic products are When using garbage bags made of biodegradable plastics, the organic waste in the bags was not treated properly, causing anaerobic decomposition and causing odors. .
[0006]
The object of the present invention is to provide a method for efficiently composting organic waste mixed with biodegradable plastic products.
[0007]
[Means for Solving the Problems]
The present inventors have, when such circumstances result of intensive studies looking Kan, the microbial decomposition treatment at 70 ° C. below the temperature of organic waste garbage or the like including a biodegradable plastic product, 75 ° C. The present inventors have found that the treatment can be suitably performed by incorporating a process for 1 to 48 hours under a high temperature condition of 90 ° C. or less and a high humidity of 100% relative humidity .
[0008]
That is, the present invention relates to a treatment tank for storing organic waste mixed with a biodegradable plastic product, a blower for sending air into the treatment tank, and a heating facility capable of heating the inside of the treatment tank. In a method for treating organic waste mixed with biodegradable plastic products using an organic waste treatment apparatus comprising The gist of the present invention is a method for treating organic waste, characterized by comprising a step of disintegrating a plastic product.
[0009]
Hereinafter, the present invention will be described in detail.
The biodegradable plastic product referred to in the present invention is not particularly limited as long as it is a product formed of a biodegradable resin. Specifically, a film, a sheet, a bag, a string, a band, a box In addition to these, various tableware such as chopsticks, forks, spoons and dishes, and clothing such as clothes and hats.
[0010]
The raw materials for biodegradable plastic products include polypeptides such as collagen, gelatin, fibrin, albumin, synthetic polypeptide, silk and wool, amylose, dextran, alginic acid, chitin, chitosan, cotton, hemp, rayon and cellulose. Sugars, polyglycolic acid, polylactic acid, polyglactin, polymalic acid, poly-ε-caprolactone, poly-3-hydroxybutyric acid, poly-3-hydroxyvaleric acid, poly-4-hydroxybutyric acid, poly-6-hydroxyhexanoic acid, Examples thereof include polyesters such as polybutylene succinate and polyethylene succinate, and are particularly effective for products mainly made of polylactic acid.
[0011]
The organic waste as used in the present invention is not particularly limited as long as it can be microbially decomposed with organic waste, but waste generated from households, restaurants, etc., processing residuals discharged from food processing plants, Examples include organic sludge and livestock excrement generated by wastewater treatment.
[0012]
The organic waste processing apparatus used in the processing method of the present invention may be a so-called garbage processing apparatus. At least a processing tank for storing organic waste, and a blower for sending air into the processing tank And a heating facility capable of heating the inside of the treatment tank, and further preferably provided with a stirring means capable of stirring the inside of the treatment tank.
[0013]
Among these, the treatment tank is not particularly limited as long as it can accommodate organic waste, and the capacity and material are not particularly limited, but in the present invention, it is necessary to heat the inside of the treatment tank. is preferably 10L least 5 m 3 or less, more desirably at 20L than 1 m 3 or less, the material can that withstand high temperatures, it is desirable to use a strong material, such as stainless and heat-corrosion resistant plastic corrosion .
[0014]
The blower need not be special, as long as the contents are not anaerobic and have sufficient capacity for drying. The amount of air supply varies between the process that mainly focuses on the degradation of biodegradable plastics and the process that mainly fermentations and decomposes organic waste, but it is 0.1 to 10 m 3 / min per 1 m 3 treatment tank. If it is.
[0015]
As the heating equipment, the tank itself may be heated or heated, or the air in the tank may be heated to raise the temperature in the tank.
[0016]
The stirring means is not particularly limited as long as the contents can be sufficiently stirred, and may be those generally used in organic waste treatment apparatuses. Specifically, an apparatus in which a stirring blade is provided on the rotary shaft of the rotary motor can be mentioned. By stirring by this stirring means, the contents are stirred, aerobic fermentation occurs, and suitable drying is performed.
[0017]
In addition, a special degrading bacterium may be added to the treatment, but even if it is not particularly added, the treatment can be sufficiently performed by the bacteria attached to the garbage or the floating bacteria in the air. In particular, in the case of so-called continuous processing in which the next treatment is performed in a state where the processed material left in the processing tank remains in the processing tank, the effect of adding degrading bacteria is small.
[0018]
In addition, sawdust, bark, rice husk, zeolite, wood chips, rice bran, or other special agents may be used as a water conditioner, fermentation base, or fermentation aid, but it is also possible to treat with only garbage. is there.
[0019]
In the present invention, the step of mainly disintegrating the biodegradable plastic product is a step of setting the internal temperature of the tank to 75 ° C. or higher and 90 ° C. or lower while maintaining the relative humidity at 100% . The main purpose of this process is to break down the biodegradable plastics that are mixed in, and to facilitate microbial degradation in the process of mainly decomposing organic waste. When processing ordinary organic waste, the relative humidity in the tank at the initial stage of processing is 90% or more, and it is not necessary to add water. However, when processing a fairly dry one or when performing a process of mainly decomposing organic waste first, it may be necessary to add moisture to increase the relative humidity.
[0020]
It is desirable to keep in mind that the amount of air supplied in this process maintains a relative humidity of 90% or more and does not become anaerobic. Preferably the processing tank per 0.1~2m 3 / min of 1 m 3 in particular, 0.2~1m 3 / min is more preferable. In addition, air can be supplied from anywhere as long as it is in the tank, but it is desirable to perform air supply from the bottom of the tank or the back side of the stirring blade in order to spread the air throughout. By performing such high-temperature and high-humidity treatment, the biodegradable plastic is efficiently disintegrated.
[0021]
The processing time of the step of mainly disintegrating the biodegradable plastic product requires 1 to 48 hours . Long-term treatment at high temperatures is effective for the degradation of biodegradable plastics, but it hinders the degradation of organic waste by microorganisms and the degradation of biodegradable plastics mainly in the process of decomposing organic waste. It is for bringing about.
[0022]
The term “collapse” as used herein means that the biodegradable plastic has a low molecular weight due to hydrolysis or the like, the strength is remarkably lowered, and the shape cannot be maintained, and does not mean degradation of the monomer itself.
[0023]
In the present invention, the step of mainly decomposing organic waste requires a temperature suitable for a microbial reaction of 70 ° C. or lower, specifically 30 ° C. or higher and 70 ° C. or lower , preferably 40 ° C. or higher and 65 ° C. or lower. This is a step of degrading the biodegradable plastic that has collapsed in the step of collapsing organic waste and mainly biodegradable plastic products at a temperature of ℃ or lower. Since the biodegradable plastic collapses and has a low molecular weight mainly in the process of disintegrating the biodegradable plastic product, it is easily decomposed in this process. Moreover, since organic waste is also susceptible to microbial degradation by treatment under high-temperature and high-humidity conditions, the treatment becomes easy.
[0024]
Air amount in this step is slightly raised, preferably 0.2 to 10 m 3 / min per treatment tank 1 m 3, more preferably to 0.5 to 5 m 3 / min. However, when a drying step is provided as a third step, the operation may be performed in the same manner as the step of mainly disintegrating the biodegradable plastic product. In addition, when the moisture content of the processed product is sufficiently high, or when the moisture content in the tank is not significantly reduced even if the air supply amount is increased, the air supply amount may be further increased.
[0025]
The microbial decomposition treatment time in this step is preferably 6 hours or more, and more preferably 8 hours or more when the moisture content of the treated product is 80% or less, desirably 70% or less and not less than 30%. desirable. This is because if the water content of the treated product is high, good aerobic treatment cannot be performed, and if it is less than 30%, the microbial activity is significantly reduced.
[0026]
In the present invention, it is necessary to mainly perform a step of decomposing organic waste after performing a step of disintegrating the biodegradable plastic product. When processing garbage containing biodegradable plastic products continuously, it may be performed in reverse.
In that case, the biodegradable plastic product does not collapse in the first step, that is, mainly the step of decomposing organic waste, but it is collapsed by the next step of mainly degrading the biodegradable plastic product and is continuously In the next cycle, the biodegradable plastic product does not accumulate in the tank, and it can be processed well because it is effectively decomposed mainly by the process of decomposing organic waste. .
[0027]
【Example】
Hereinafter, the present invention will be specifically described.
Reference example 1
The following experiment was conducted to investigate the collapse behavior of biodegradable plastics. A film composed of 80 parts by weight of polylactic acid and 20 parts by weight of Bionole manufactured by Showa Polymer Co., Ltd., 17 parts by weight of acetyltributyl citrate as a plasticizer, and 5 parts by weight of silicon oxide (SiO 2 ) No. 11-116788 (see Example 1) was allowed to stand at 60 ° C., 70 ° C., and 80 ° C. under conditions of relative humidity of 90% and 100%. After returning to room temperature after 1, 2, 3, 6, 24, and 48 hours and air-drying, the degree of deterioration / disintegration was visually determined, and the molecular weight of the monomer was measured. At 60 ° C. and 70 ° C., there was no change in appearance at all treatment times at both 90% and 100% relative humidity. The molecular weight was almost unchanged at 60 ° C. until 24 hours, but decreased slightly in the treatment at 100% relative humidity, 70 ° C. and 24 hours, and after 48 hours, it decreased slightly in the 60 ° C. treatment. When the treatment temperature is 80 ° C, the flexibility is lost after 2 hours at 100% relative humidity, the deterioration is observed after 6 hours, and the shape of the bag cannot be maintained after 24 hours, and it is broken into pieces. Became. When the relative humidity was 90%, the collapsed state was worse than that of the relative humidity of 100%, and although the deterioration occurred even after 24 hours, the bag shape was maintained. Figure 1 shows the change in molecular weight when treated at 80 ° C with 100% relative humidity. It became clear that hydrolysis occurred with the treatment time and the molecular weight decreased rapidly.
[0028]
Example 1
10 bags containing 1kg of cocoon in a garbage bag made by thermocompression bonding of the film produced in the same way as in the above reference example, have a stirring blade, can be fed from the bottom of the treatment tank, and the inside of the tank is added It was put into a heatable garbage processing machine (processing capacity 20L). 200g of seed compost was added to the treatment tank in advance. After throwing in the soot, air was supplied at 10 L / min with the stirring blade stopped, and the inside of the tank was heated to 80 ° C. At this time, the relative humidity in the tank was 100%. After 5 hours, the treatment tank temperature was lowered to 60 ° C., the air supply amount was changed to 20 L / min, and the treatment was further performed for 24 hours while stirring at 1 rpm. The biodegradable plastics collapsed significantly during the treatment at 80 ° C for 5 hours, and the subsequent agitation at 60 ° C allowed the organic waste and the collapsed biodegradable plastics to mix well, allowing good fermentation. . The water content of the processed product after the test was 40%, which was a smooth fermented processed product.
[0029]
Comparative Example 1
As in Example 1, 10 biodegradable garbage bags containing 1 kg of straw have a stirring blade, can feed air from the bottom of the treatment tank, and can heat the inside of the garbage treatment machine (processing capacity 20L) ). 200g of seed compost was added to the treatment tank in advance. After charging, the air was fed at 10 L / min while the stirring blade was stopped, and the inside of the tank was heated to 60 ° C. At this time, the relative humidity in the tank was 100%. After 5 hours, the air supply rate was changed to 20 L / min, and a further 24 hours of treatment was performed while stirring at 1 rpm. After the test was completed, the garbage bags in the tank remained the original shape, and a part of them was entangled with the stirring blades. In addition, some garbage bags had no contents outside, and the garbage was not treated well among them, causing corruption.
[0030]
【effect】
According to the present invention, organic waste mixed with biodegradable plastics can be efficiently and sufficiently fermented, and the resulting compost is also good.
[Brief description of the drawings]
FIG. 1 is a graph showing changes in molecular weight in a biodegradable film disintegration process (100% relative humidity, 80 ° C. treatment).

Claims (1)

生分解性プラスチック製品が混合された有機性廃棄物を収納する処理槽と、該処理槽内に空気を送り込むブロアーと、該処理槽内を加温することができる加温設備とを備えた有機性廃棄物処理装置を用いて、生分解性プラスチック製品が混合された有機性廃棄物を処理する方法において、処理槽内の相対湿度が100%、温度が75℃〜90℃の状態を1時間〜48時間維持する、主として生分解性プラスチック製品の崩壊を行う工程を行った後に、処理槽内の温度が30℃以上70℃以下である、主として有機性廃棄物の発酵分解を行う工程を行うことを特徴とする有機性廃棄物の処理方法。Organic having a treatment tank for storing organic waste mixed with biodegradable plastic products, a blower for sending air into the treatment tank, and a heating facility capable of heating the treatment tank In a method for treating organic waste mixed with biodegradable plastic products using a toxic waste treatment apparatus, the relative humidity in the treatment tank is 100%, and the temperature is between 75 ° C. and 90 ° C. for 1 hour. After performing the step of mainly disintegrating the biodegradable plastic product that is maintained for ˜48 hours, the step of performing the fermentative decomposition of organic waste mainly having a temperature in the treatment tank of 30 ° C. or higher and 70 ° C. or lower is performed. An organic waste processing method characterized by the above.
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JP3681724B2 (en) * 2002-12-26 2005-08-10 キヨモトバイオ株式会社 Recycling method of organic waste
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Citations (8)

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Publication number Priority date Publication date Assignee Title
JPH04362080A (en) * 1991-06-05 1992-12-15 Akira Ito Treatment of organic waste
JPH05155680A (en) * 1991-12-05 1993-06-22 Toho Gas Co Ltd Treatment of organic waste
JPH0884981A (en) * 1994-09-16 1996-04-02 Toshiba Corp Garbage throwing-away draining bag and garbage disposal device using same
JPH08192130A (en) * 1995-01-18 1996-07-30 Hitachi Ltd Waste treatment method and apparatus for house
JPH0942642A (en) * 1995-07-24 1997-02-14 Osaka Gas Eng Kk Disposal equipment and use thereof
JPH09201579A (en) * 1996-01-26 1997-08-05 Japan Steel Works Ltd:The Method for separating and recovering paper from biodegradable plastic-coated paper
JPH09249474A (en) * 1996-03-15 1997-09-22 Japan Steel Works Ltd:The Composting treatment of organic waste containing biodegradable plastic
JPH09249475A (en) * 1996-03-15 1997-09-22 Japan Steel Works Ltd:The Composting treatment of biodegradable plastic and apparatus therefor

Patent Citations (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH04362080A (en) * 1991-06-05 1992-12-15 Akira Ito Treatment of organic waste
JPH05155680A (en) * 1991-12-05 1993-06-22 Toho Gas Co Ltd Treatment of organic waste
JPH0884981A (en) * 1994-09-16 1996-04-02 Toshiba Corp Garbage throwing-away draining bag and garbage disposal device using same
JPH08192130A (en) * 1995-01-18 1996-07-30 Hitachi Ltd Waste treatment method and apparatus for house
JPH0942642A (en) * 1995-07-24 1997-02-14 Osaka Gas Eng Kk Disposal equipment and use thereof
JPH09201579A (en) * 1996-01-26 1997-08-05 Japan Steel Works Ltd:The Method for separating and recovering paper from biodegradable plastic-coated paper
JPH09249474A (en) * 1996-03-15 1997-09-22 Japan Steel Works Ltd:The Composting treatment of organic waste containing biodegradable plastic
JPH09249475A (en) * 1996-03-15 1997-09-22 Japan Steel Works Ltd:The Composting treatment of biodegradable plastic and apparatus therefor

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