JP3999713B2 - Garbage disposal method - Google Patents

Garbage disposal method Download PDF

Info

Publication number
JP3999713B2
JP3999713B2 JP2003280380A JP2003280380A JP3999713B2 JP 3999713 B2 JP3999713 B2 JP 3999713B2 JP 2003280380 A JP2003280380 A JP 2003280380A JP 2003280380 A JP2003280380 A JP 2003280380A JP 3999713 B2 JP3999713 B2 JP 3999713B2
Authority
JP
Japan
Prior art keywords
garbage
waste paper
fermented
fermentation
mixing
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.)
Expired - Fee Related
Application number
JP2003280380A
Other languages
Japanese (ja)
Other versions
JP2005040768A (en
Inventor
忠治 寺本
Original Assignee
忠治 寺本
Priority date (The priority date 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 date listed.)
Filing date
Publication date
Application filed by 忠治 寺本 filed Critical 忠治 寺本
Priority to JP2003280380A priority Critical patent/JP3999713B2/en
Publication of JP2005040768A publication Critical patent/JP2005040768A/en
Application granted granted Critical
Publication of JP3999713B2 publication Critical patent/JP3999713B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

Links

Description

本発明は、生ゴミの処理方法に関し、詳しくは生ゴミを細菌によって発酵させ分解処理する方法に関する。   The present invention relates to a method for treating garbage, and more particularly, to a method for fermenting and decomposing garbage with bacteria.

生ゴミの処理方法として、近年、生ゴミを細菌によって発酵させ分解処理する方法が開発されている。この方法によると、例えば生ゴミを焼却処理する方法に比べて石油燃料の使用量が少なくて済み、かつ、安価に処理をおこなうことができる。さらに、発酵による分解処理で得られた生成物は堆肥として使用可能であるため、生ゴミを資源として有効利用することのできる処理方法として注目されている(例えば、特許文献1、2)。   As a method for treating garbage, in recent years, a method for fermenting and decomposing garbage with bacteria has been developed. According to this method, for example, the amount of petroleum fuel used can be reduced as compared with a method of incinerating raw garbage, and the treatment can be performed at low cost. Furthermore, since the product obtained by the decomposition process by fermentation can be used as compost, it attracts attention as a treatment method that can effectively use raw garbage as a resource (for example, Patent Documents 1 and 2).

ここで、一般に生ゴミの発酵分解用の発酵菌としては種々の好気性細菌が用いられているが、家庭から出る生ゴミの中で大きな比重を占める残飯の中には多くの水分が含まれており、例えば残飯を多く含む生ゴミを発酵分解する場合には、生ゴミ中の水分量が過剰となって好気性細菌による発酵が良好におこなわれない場合があった。すなわち、生ゴミ中の水分量が多くなると、生ゴミに供給される酸素量が小さくなり、好気性細菌の生育が抑制されるとともに、種々の嫌気性細菌の生育が促進される。これら嫌気性細菌の生育が進行すると、生ゴミが発酵した発酵体に異臭が発生したり、異臭の発生により虫があつまって発酵体に虫が繁殖する等の問題が生じる。このため、一般に発酵により生ゴミを分解する場合、良好な発酵をおこなうためには生ゴミ中の水分量を低く保つ必要があるとされている。   Here, various aerobic bacteria are generally used as fermentative bacteria for fermentative decomposition of raw garbage, but a large amount of moisture is contained in the leftover food, which occupies a large specific gravity among raw garbage from homes. For example, when fermenting and decomposing raw garbage containing a large amount of leftover food, the amount of water in the raw garbage is excessive, and fermentation by aerobic bacteria may not be performed satisfactorily. That is, when the amount of water in the garbage increases, the amount of oxygen supplied to the garbage decreases, which suppresses the growth of aerobic bacteria and promotes the growth of various anaerobic bacteria. When the growth of these anaerobic bacteria progresses, problems such as the generation of off-flavors in the fermented material fermented with garbage and the occurrence of off-flavors that cause insects to accumulate and the fertilizers to propagate on the fermented materials occur. For this reason, when decomposing | disassembling raw garbage by fermentation generally, in order to perform favorable fermentation, it is supposed that the moisture content in raw garbage needs to be kept low.

生ゴミ中の水分を調整するために、おがくず等の繊維材を生ゴミ中に混合し、これら繊維材に生ゴミ中の水分を吸収させることも為されているが、繊維材の発酵分解には長時間を要するため、繊維材を含む生ゴミ全体の発酵分解に要する時間が長くなり、多量の生ゴミを同一の処理装置や処理空間で処理することが困難となる問題があった。
特開2002−361214号公報 特開2002−301449号公報
In order to adjust the moisture in the garbage, fiber materials such as sawdust are mixed in the garbage, and these fibers can absorb the moisture in the garbage. Since it takes a long time, the time required for the fermentation and decomposition of the whole raw garbage including the fiber material becomes long, and there is a problem that it is difficult to process a large amount of raw garbage in the same processing apparatus or processing space.
JP 2002-361214 A JP 2002-301449 A

本発明は、上記事情に鑑みてなされたものであり、生ゴミの発酵分解を、虫や異臭の発生を押さえつつ迅速に行うことのできる生ゴミ処理方法を提供することを目的とする。   The present invention has been made in view of the above circumstances, and an object of the present invention is to provide a garbage disposal method capable of quickly performing fermentation decomposition of garbage while suppressing generation of insects and off-flavors.

本発明の生ゴミの処理方法は、古紙を小片状にして小片状古紙を形成する工程と、小片状古紙と栄養源と発酵菌とを混合して発酵させる工程と、を含み、古紙の機械的強度を低下させてほぼ全体が発酵分解した発酵古紙を作る古紙発酵工程と、発酵古紙と生ゴミとを混合し生ゴミを発酵分解させて発酵古紙と一体化した粉末状の発酵体を得る本発酵工程と、備えることを特徴とする。 The method for treating garbage according to the present invention includes a step of making waste paper into small pieces to form small pieces of waste paper, and a step of mixing and fermenting the pieces of waste paper, nutrient sources, and fermentation bacteria, A waste paper fermentation process that reduces the mechanical strength of waste paper to produce a fermented waste paper that is almost entirely fermented and decomposed, and a fermented powder that combines fermented waste paper and raw waste to ferment and decompose raw waste and integrate it with fermented waste paper And a main fermentation process for obtaining a body.

上記本発酵工程は、上記発酵古紙と上記生ゴミとを機械的に混合する混合工程と、混合工程により得られた混合物を空気の存在下で発酵させる後発酵工程と、からなる工程とすることができる。 The main fermentation process is a process comprising a mixing process for mechanically mixing the fermented waste paper and the raw garbage, and a post-fermentation process for fermenting the mixture obtained by the mixing process in the presence of air. Can do.

上記後発酵工程は、上記混合物の内部に強制的に空気を供与しつつおこなうことが好ましい。   The post-fermentation step is preferably performed while forcibly supplying air to the inside of the mixture.

上記本発酵工程は、50〜70℃でおこなうことが好ましい The present fermentation process is preferably carried out at 50-70 ° C..

上記栄養源は、米糠食用廃油、豆類の絞り滓、乾燥させた鳥獣糞、コーヒーかすから選ばれる少なくとも一種を含むことが好ましい。 It is preferable that the nutrient source includes at least one selected from rice bran , edible waste oil , squeezed bean paste, dried bird droppings, and coffee grounds .

上記混合工程は、混合された混合物を篩にかけ篩に残った物を再度混合工程に戻す処理を含むことが好ましい。   The mixing step preferably includes a process of sieving the mixed mixture and returning the material remaining on the sieve back to the mixing step.

上記生ゴミは、魚骨および/または鳥獣骨を含むものとすることができる。   The raw garbage may include fish bones and / or birds and bones.

上記混合工程は、さらに、土を加えておこなうことが好ましい。   The mixing step is preferably performed by adding soil.

本発明の生ゴミの処理方法によると、本発酵工程において、生ゴミに発酵古紙を混合して発酵分解をおこなうことで、生ゴミ中の水分が発酵古紙に吸収される。このため、発酵古紙の量を適宜調整することで、生ゴミの水分量を所望の水分量に調整することができる。その結果、発酵菌の生育を促進しつつ嫌気性細菌等の発酵菌以外の細菌の生育を抑制することができ、生ゴミの発酵分解を虫や異臭の発生を押さえつつ行うことが可能となる。 According to the method for treating garbage of the present invention, in the main fermentation process, the fermented waste paper is mixed with the fermented waste paper and fermented and decomposed, whereby the moisture in the raw garbage is absorbed by the fermented waste paper . For this reason, the water content of garbage can be adjusted to a desired water content by appropriately adjusting the amount of used fermented paper . As a result, it is possible to suppress the growth of bacteria other than fermenting bacteria such as anaerobic bacteria while promoting the growth of fermenting bacteria, and it is possible to perform fermentation decomposition of garbage while suppressing the generation of insects and off-flavors. .

また、古紙は発酵菌で予め発酵させて機械的強度を低下させているので、本発酵工程に供したときには既に分解された状態となっている。従って、古紙を用いるにも関わらず発酵工程は迅速におこなわれることとなる。 In addition, since the waste paper is previously fermented with a fermenting fungus to reduce the mechanical strength, it is already decomposed when subjected to the main fermentation process. Therefore, the fermentation process is performed quickly despite the use of waste paper .

本発明の生ゴミの処理方法は、古紙発酵工程と、本発酵工程とを有する。 The processing method of the garbage of this invention has a used paper fermentation process and a main fermentation process.

このうち、古紙発酵工程は、古紙を発酵菌で発酵させ機械的強度を低下させてほぼ全体が発酵分解した発酵古紙を作る工程である。この古紙発酵工程は、使用する古紙の含水量に応じて、水を添加しておこなうこともできる。 Among these, the waste paper fermentation process is a process of making fermented waste paper that is fermented and decomposed by fermenting the waste paper with fermenting bacteria to reduce the mechanical strength. This waste paper fermentation process can be performed by adding water according to the water content of the waste paper used.

古紙発酵工程で用いられる古紙として特に新聞紙等の古紙は、容易且つ安価に入手することができるとともに水分をよく吸収し、さらに、発酵菌によって比較的容易に分解されるため、特に好ましく用いられる。 As waste paper used in the waste paper fermentation process , especially waste paper such as newspaper is particularly preferred because it can be obtained easily and inexpensively, absorbs moisture well, and is relatively easily decomposed by fermentation bacteria. .

発酵菌としては、好気性の細菌であり、酵母菌、放線菌等、通常生ゴミの分解に用いられるものを1種又は複数種選択して使用することができる。なお、上述したようにこの発酵菌によって古紙を分解するため、古紙の機械的強度を低下できる菌が少なくとも1種含まれるものとする。 As a fermenting bacterium, it is an aerobic bacterium, and one or a plurality of those usually used for the decomposition of garbage such as yeast and actinomycete can be selected and used. As described above, since the used paper is decomposed by the fermenting bacteria, at least one kind of bacteria capable of reducing the mechanical strength of the used paper is included.

なお、この発酵菌は所望する菌又は複数種の菌からなる菌群を培養するなどして予め準備したものを用いることもできる。しかし、例えば一定の空間で上述した古紙発酵工程をおこなうことでその空間内に発酵菌が増加するため、同一空間で再度古紙発酵工程をおこなう場合には、別途発酵菌を準備しなくても古紙は空間内の発酵菌により発酵し発酵古紙となる。 In addition, what was prepared beforehand by culturing the fungal group which consists of desired microbe or several types of microbe can also be used for this fermenting microbe. However, for example, since the fermentation bacteria increases the space by performing the paper fermentation step described above with a constant space, when performing re-used paper fermentation step in the same space, without separately preparing a fermentation bacteria used paper Is fermented by fermenting bacteria in the space and becomes fermented waste paper .

この古紙発酵工程は、古紙を小片状にする工程と、得られた小片状古紙と栄養源と発酵菌とを混合して発酵させる工程と、を含む工程から構成される This waste paper fermentation process is composed of a process including a step of making waste paper into pieces, and a step of mixing and fermenting the obtained pieces of waste paper , nutrients, and fermentation bacteria .

古紙を小片状にして古紙の体積あたりの表面積を大きくすることで、古紙を発酵菌と接触し易くし、発酵菌による古紙の発酵をおこない易くすることができる。そして、小片状古紙と発酵菌とを混合して古紙と発酵菌とを均一に混ざり合った状態で発酵させることで、古紙と発酵菌とをより均一に接触させることができ、古紙の発酵分解をより促進することができる。 By the paper in the form of small pieces to increase the surface area per volume of waste paper, it is possible to easily contact the paper with the fermenters, to facilitate the fermentation of waste paper by the fermenting bacteria. And by mixing small pieces of waste paper and fermenting bacteria and fermenting the waste paper and the fermenting bacteria in a uniformly mixed state, the waste paper and the fermenting bacteria can be contacted more uniformly, and the fermentation of the waste paper Degradation can be further promoted.

ここで、小片状古紙と発酵菌とにさらに栄養源を添加することで、発酵菌による古紙の発酵分解さらに促進される。すなわち、古紙は一般に澱粉やセルロース等の炭素成分を多く含み、発酵菌が生育する際には主に炭素源となる。その一方、一般にタンパク質等の窒素成分はあまり多く含まないため、古紙の種類によっては、発酵菌の生育に窒素源が不足する場合がある。また、発酵菌の種類によっては、古紙を発酵分解し難い菌もあり、この場合には、別途炭素源を添加することで古紙の発酵が促進される場合もある。したがって、栄養源としては炭素源や窒素源、或いは炭素窒素源となるものが好ましく使用される。特に、米糠は容易且つ安価に入手でき、炭素窒素源として好ましく使用される。そして、廃食用油もまた容易且つ安価に入手することができ、炭素源として好ましく使用することができる。その他、例えば、おから等の豆類の絞り滓や、乾燥させた鳥獣糞等を窒素源や炭素窒素源として用いることもできる。 Here, the fermentative decomposition of the waste paper by the fermenting bacteria is further promoted by further adding a nutrient source to the small pieces of waste paper and the fermenting bacteria. That is, waste paper generally contains a large amount of carbon components such as starch and cellulose, and is mainly a carbon source when fermenting bacteria grow. On the other hand, since nitrogen components such as proteins are generally not included so much, depending on the type of used paper , a nitrogen source may be insufficient for the growth of fermenting bacteria. In addition, depending on the type of fermenting bacteria, there are bacteria that are difficult to fermentatively decompose used paper . In this case, fermentation of used paper may be promoted by adding a carbon source separately. Therefore, as a nutrient source, a carbon source, a nitrogen source, or a carbon nitrogen source is preferably used. In particular, rice bran is easily and inexpensively available and is preferably used as a carbon nitrogen source. And waste edible oil can also be obtained easily and cheaply, and can be preferably used as a carbon source. In addition, for example, squeezed straw of beans such as okara, dried birds and animals feces, etc. can be used as a nitrogen source or a carbon nitrogen source.

なお、これらの工程により得られた発酵古紙は、そのまま後述する本発酵工程に供することもできるし、あるいは、乾燥させた水分量を調整した後に本発酵工程に供することもできる。 In addition, the fermented waste paper obtained by these processes can also be used for the main fermentation process mentioned later as it is, or can be used for the main fermentation process after adjusting the dried water content.

本発酵工程は、発酵古紙と生ゴミとを混合し生ゴミを発酵分解させて発酵古紙と一体化した粉末状の発酵体を得る工程である。 The main fermentation process is a process of obtaining a fermented powder that is integrated with fermented waste paper by mixing fermented waste paper and raw waste and fermenting and decomposing the raw waste.

生ゴミは、食品を調理する際に出る野菜や果物の皮や切れ端、魚骨や鳥獣骨、魚肉や鳥獣肉、調理され提供された食品の残飯等に代表される、植物や動物、微生物に由来する加熱物あるいは非加熱物を用いることができる。   Garbage can be used for plants, animals, and microorganisms, such as peels and slices of vegetables and fruits that appear when cooking food, fish bones and birds and animal bones, fish and birds and meat, and leftovers of cooked and provided foods. The derived heated or non-heated material can be used.

本発酵工程において、上述した発酵古紙と生ゴミとを混合することで、生ゴミに含まれる水分が発酵古紙に吸収されるとともに、発酵古紙に含まれる発酵菌が生ゴミ中に分散される。このとき、発酵菌が生ゴミ中に含まれる各種成分を栄養源として生育することで生ゴミが発酵分解され、発酵古紙と一体化した発酵体が生成する。またこのとき、生ゴミは発酵菌により発酵分解されて粉末状となり、上述した古紙発酵工程で機械的強度が低下し脆いものなっている発酵古紙もまた同様に粉末状となる。したがって、生ゴミが発酵分解されて生成した発酵体は発酵古紙と一体化されたものとなり、且つ、粉末状のものとなる。なお、ここでいう一体化とは、粉末化された発酵体と粉末化された発酵古紙とが全体として一体化されていることをいう。すなわち、粉末化され細片状となった個々の発酵体が同じく細片状となった個々の発酵古紙と一体化されているものだけでなく、例えば、粉末状の発酵体が粉末状の発酵古紙と混合され発酵体が発酵古紙と一体に混合された状態のものも発酵古紙と一体化された発酵体と呼ぶものとする。 In the fermentation process, by mixing the fermented waste paper and garbage as described above, with water contained in garbage is absorbed by the fermentation waste paper, fermentative bacteria contained in the fermentation waste paper is dispersed in the garbage. At this time, the fermented bacteria are grown using various components contained in the raw garbage as nutrient sources, whereby the raw garbage is fermented and decomposed, and a fermented body integrated with the fermented waste paper is generated. At this time, garbage is fermented decomposed by fermenting bacteria become powdery, fermentation waste paper mechanical strength in the above-described used paper fermentation process becomes brittle reduced versa becomes powdery. Therefore, the fermented material produced by fermenting and decomposing the garbage is integrated with the fermented waste paper and becomes powdery. In addition, integration here means that the powdered fermented material and the powdered fermented waste paper are integrated as a whole. That is, not only the individual fermented material that has been pulverized into pieces, but also integrated with each fermented waste paper that has also been in the form of fine pieces, for example, a powdered fermented material is a fermented powder. A state in which the fermented material is mixed with waste paper and mixed with fermented waste paper is also called a fermented material integrated with fermented waste paper .

発酵古紙と生ゴミとの混合は、既知の構造の混合装置を用いておこなうこともできるし、あるいは、例えば鍬や鋤等の器具を用いて手動でおこなうこともできる。 The mixing of the fermented waste paper and the garbage can be performed by using a mixing device having a known structure, or can be manually performed by using a device such as a straw or a straw.

本発明の生ゴミの処理方法は、古紙発酵工程と本発酵工程とを実施することによって、生ゴミの水分量を所望の水分量に調整するように生ゴミ中の水分を発酵古紙に吸収させつつ発酵分解をおこなうことができ、嫌気性細菌等の発酵菌以外の細菌の生育を抑制しつつ発酵菌による生ゴミの発酵分解をおこなうことができる。したがって、生ゴミの発酵分解を異臭や虫の発生を抑止しつつおこなうことが可能となる。さらに、古紙古紙発酵工程で発酵菌により予め発酵しているため、その機械的強度は低下した状態で本発酵工程に供される。したがって、本発酵工程においてさらに古紙を分解する必要はなく、古紙を用いて水分の吸収をおこなうにも関わらず発酵工程は迅速におこなわれることとなる。 The processing method of the garbage of this invention makes the fermented waste paper absorb the water | moisture content in garbage so that the moisture content of a garbage may be adjusted to a desired moisture content by implementing a used paper fermentation process and a main fermentation process. While being able to perform fermentation decomposition, it is possible to perform fermentation decomposition of garbage with fermentation bacteria while suppressing the growth of bacteria other than fermentation bacteria such as anaerobic bacteria. Therefore, it becomes possible to perform the fermentation decomposition of garbage while suppressing the generation of off-flavors and insects. Furthermore, since the used paper is previously fermented with the fermenting bacteria in the used paper fermentation process, the mechanical strength of the used paper is reduced and provided to the main fermentation process. Therefore, it is not necessary to further decompose the used paper in the main fermentation process, and the fermentation process is performed quickly despite the moisture absorption using the used paper .

この本発酵工程は、混合工程と後発酵工程とから構成することができる。混合工程は、発酵古紙と生ゴミとを機械的に混合する工程であり、後発酵工程は混合工程により得られた混合物を空気の存在下で発酵させる工程である。 This main fermentation process can be composed of a mixing process and a post-fermentation process. The mixing step is a step of mechanically mixing fermented waste paper and garbage, and the post-fermentation step is a step of fermenting the mixture obtained in the mixing step in the presence of air.

このうち、混合工程においては、生ゴミの発酵分解は混合されつつ進行するため、生ゴミと発酵菌を含む発酵古紙とは均一に接触する。したがって、発酵を混合しつつおこなわない場合よりも、より迅速に生ゴミの発酵分解をおこなうことが可能となる。 Among these, in the mixing step, since the fermentation decomposition of the garbage proceeds while being mixed, the garbage and the fermented waste paper containing the fermenting bacteria are in uniform contact. Therefore, it becomes possible to perform the fermentation decomposition of garbage more rapidly than in the case where the fermentation is not performed while mixing.

ここで、従来の生ゴミ処理方法では、魚骨や鳥獣骨等の発酵分解には非常に長い時間を要するため、魚骨や鳥獣骨等を含む生ゴミの処理は非常に困難なものとされていた。しかし、本発明の生ゴミの処理方法によると、上述したように混合工程によって発酵菌と生ゴミとが均一に接触するため、従来発酵分解し難いとされていた魚骨や鳥獣骨等を含む生ゴミであっても迅速に発酵分解することが可能となる。そしてさらに、混合工程を長く設けることで魚骨や鳥獣骨等を多く含む生ゴミであっても迅速に発酵分解することが可能となる。なお、魚骨や鳥獣骨より発酵され易い材料、例えば野菜や果物の皮や切れ端等がさらに生ゴミ中に含まれる場合には、これら発酵され易い材料によって発酵菌が生育し菌数が増加するため、発酵菌による魚骨や鳥獣骨等の発酵分解され難い材料の発酵分解は進行する。したがって、本発酵工程に供する生ゴミには、魚骨や鳥獣骨とともに魚骨や鳥獣骨より発酵されやすい材料を含むことが好ましい。   Here, in the conventional garbage disposal method, since it takes a very long time for the fermentation and decomposition of fish bones, animal bones, etc., it is considered extremely difficult to treat garbage containing fish bones, animal bones, etc. It was. However, according to the garbage processing method of the present invention, since the fermentation bacteria and the garbage are uniformly contacted by the mixing step as described above, it includes fish bones and birds and bones that have been conventionally difficult to be decomposed by fermentation. Even raw garbage can be rapidly fermented and decomposed. Furthermore, by providing a long mixing step, it is possible to rapidly ferment and decompose even garbage that contains a large amount of fish bones, animal bones, and the like. In addition, in the case where materials that are more easily fermented than fish bones or birds and bones, for example, peels or pieces of vegetables or fruits, are further contained in the garbage, fermented bacteria grow and the number of bacteria increases due to these easily fermented materials. Therefore, fermentative decomposition of materials that are difficult to be fermented and decomposed, such as fish bones and animal bones, caused by fermenting bacteria proceeds. Therefore, it is preferable that the raw garbage to be subjected to the main fermentation step includes a material that can be more easily fermented than fish bones and wildlife bones together with fish bones and wildlife bones.

また、この混合工程における混合頻度や混合工程の長さ等は、生ゴミの種類によって適宜設定することができる。混合頻度を高くする程より迅速に発酵分解が行われ、混合工程を長く行う程より発酵分解しにくいものを発酵分解することができる。   Moreover, the mixing frequency in this mixing process, the length of a mixing process, etc. can be suitably set with the kind of garbage. The higher the mixing frequency, the faster the fermentation decomposition, and the longer the mixing process, the more difficult the fermentation decomposition can be.

さらに、混合工程は、混合された混合物を篩にかけ篩に残った物を再度混合工程に戻す処理を含む工程とすることが好ましい。上述したように、混合工程が良好に進行すると生ゴミは発酵菌により発酵分解されて粉末状に近づき、上述した古紙発酵工程で機械的強度が低下し脆いものなっている発酵古紙もまた同様に粉末状に近づく。したがって、混合工程で混合された混合物を篩にかけた時に篩を通過したものは発酵が進行している部分とみなし、篩に残ったものは発酵が充分でない部分とみなすことができる。このため、混合物を篩にかけ、篩に残ったものを再度混合工程に戻すことで、発酵が良好に進行していないもののみを再度混合工程に供することとなるため、効率よく発酵分解をおこなうことが可能となる。 Furthermore, the mixing step is preferably a step including a process of sieving the mixed mixture and returning the material remaining on the sieve to the mixing step again. As described above, the mixing process proceeds satisfactorily garbage approached fermented decomposed by fermenting bacteria in powdered, fermentation waste paper mechanical strength in the above-described used paper fermentation process it becomes brittle reduced versa It approaches powder. Therefore, what passed through the sieve when the mixture mixed in the mixing step is sieved can be regarded as a portion where fermentation is progressing, and what remains on the sieve can be regarded as a portion where fermentation is not sufficient. For this reason, by passing the mixture through a sieve and returning the material remaining on the sieve to the mixing step again, only those that have not undergone favorable fermentation will be subjected to the mixing step again, so that the fermentation decomposition can be performed efficiently. Is possible.

また、混合工程は、さらに、土を加えておこなうことが好ましい。混合工程を土を加えておこなう場合には、土が生ゴミおよび発酵古紙に対してバインダのように作用し、混合工程で粉末状になりつつある生ゴミおよび発酵古紙の小片の表面が土によってコートされる。このため、これらが互いに凝着し合うことが防止されて、粉末状の混合物、あるいは、粉末状の発酵体を容易に得ることができる。 Moreover, it is preferable that the mixing process is further performed by adding soil. When performing the mixing step by adding soil by the soil acts as a binder with respect to garbage and fermentation waste paper, small pieces of the surface of the garbage and fermentation waste paper is becoming powdery mixing process soil Coated. For this reason, they are prevented from adhering to each other, and a powdery mixture or a powdered fermented material can be easily obtained.

ここで用いる土は、発酵菌を含むものであっても良いし、或いは発酵菌を含まないものであっても良い。例えば、発酵菌を含まない土を加える場合には、上述したように土によりバインダ様の作用が得られ、発酵菌を含む土を加える場合には、発酵紙由来の発酵菌だけでなく土由来の発酵菌によっても生ゴミの発酵をおこなうことができるため、生ゴミの発酵をより迅速且つ良好におこなうことができる。   The soil used here may contain fermenting bacteria or may not contain fermenting bacteria. For example, when soil containing no fermenting bacteria is added, a binder-like action is obtained by the soil as described above, and when soil containing fermenting bacteria is added, not only fermented paper-derived fermenting bacteria but also soil-derived Since the fermented garbage can also be fermented with the fermentative bacterium, the fermentation of the garbage can be performed more quickly and satisfactorily.

本発明の生ゴミの処理方法において、本発酵工程を混合工程のみから構成することもできる。この場合には、本発酵工程の全部が混合されつつおこなわれることとなり、発酵分解がより迅速におこなわれる。しかし一方、混合工程において混合に要する労力や装置の運転コストが高くなる問題もある。したがって、混合工程によってある程度にまで発酵分解が進行した後に、混合物を後分解工程に供することで、比較的安いコストで生ゴミの発酵分解をおこなうことができる。さらに、例えば混合工程を混合装置内でおこなう場合には、生ゴミと発酵古紙との混合物の発酵がある程度進行した状態で混合装置から他の発酵槽等に移し後発酵工程をおこなうことで、混合装置によって新たな生ゴミおよび発酵古紙を混合することができ、発酵分解工程を効率よくおこなうことが可能となる。 In the method for treating garbage according to the present invention, the main fermentation process can be composed of only the mixing process. In this case, the entire main fermentation process is performed while being mixed, and the fermentation decomposition is performed more rapidly. On the other hand, however, there is a problem that labor required for mixing and operation cost of the apparatus are increased in the mixing step. Therefore, after fermentation decomposition progresses to some extent by the mixing step, the mixture is subjected to a post-decomposition step, whereby the raw garbage can be decomposed at a relatively low cost. Furthermore, for example, when the mixing step is performed in the mixing device, the mixture is transferred from the mixing device to another fermenter or the like in a state where fermentation of the mixture of raw garbage and fermented waste paper has progressed to some extent, and then the mixing step is performed. New garbage and fermented waste paper can be mixed by the apparatus, and the fermentation decomposition process can be performed efficiently.

後発酵工程は、混合工程で充分に混合されて得られた混合物を空気の存在下で発酵させる工程である。この後発酵工程においては、混合工程で得られた混合物をさらに発酵させ、混合物のほぼ全部を発酵体とする。この後発酵工程は、前記混合物の内部に強制的に空気を供与しつつおこなうことが好ましい。上述したように、本発酵工程に使用する発酵菌は好気性の細菌であるため、混合物の内部に強制的に空気を供給することで発酵菌の生育がよりおこなわれ易くなり、発酵がより進行するからである。   The post-fermentation step is a step of fermenting the mixture obtained by being sufficiently mixed in the mixing step in the presence of air. In the post-fermentation step, the mixture obtained in the mixing step is further fermented, and almost all of the mixture is used as a fermented product. The post-fermentation step is preferably performed while forcibly supplying air into the mixture. As described above, since the fermentation bacteria used in the main fermentation process are aerobic bacteria, the fermentation bacteria are more easily grown by forcibly supplying air into the mixture, and the fermentation proceeds more. Because it does.

また、上述した混合工程と同様に、後発酵工程においても混合物を篩にかける工程を実施することもできる。この場合、篩を通過した混合物のみを発酵体とし、篩に残った混合物を再度後発酵工程に戻すこともできる。さらに、篩を通過した混合物のみを集め、さらに発酵させて発酵体とすることもできる。この場合には、発酵体は発酵の進行度がほぼ同程度のもののみで構成されることとなり、例えば発酵体を堆肥として使用する場合等に品質を均一化することができる。   Moreover, the process which sifts a mixture can also be implemented also in a post-fermentation process similarly to the mixing process mentioned above. In this case, only the mixture that has passed through the sieve can be used as a fermenter, and the mixture remaining on the sieve can be returned to the post-fermentation step again. Furthermore, only the mixture that has passed through the sieve can be collected and further fermented to obtain a fermented product. In this case, the fermented material is composed only of the fermented material having substantially the same degree of fermentation. For example, when the fermented material is used as compost, the quality can be made uniform.

本発明の生ゴミの処理方法において、本発酵工程は50〜70℃でおこなうことが好ましい。発酵菌が順調に生育し、生ゴミの発酵が進行している場合、発酵している生ゴミは50〜70℃程度に発熱する。この温度範囲は発酵菌の生育に適する温度であるため、生ゴミの発熱により発酵菌の生育はさらに促進され、発酵菌による生ゴミの発酵分解はさらに促進される。また、生ゴミが発熱することで、生ゴミ中の水分の蒸発が進行するため、発酵菌による生ゴミの発酵分解はよりおこなわれ易くなるとともに発酵分解により得られた発酵体は水分の含有量が低くなり粉体化されたものとなる。   In the method for treating garbage according to the present invention, the main fermentation step is preferably performed at 50 to 70 ° C. When fermenting bacteria grows smoothly and fermentation of raw garbage proceeds, the fermented raw garbage generates heat at about 50 to 70 ° C. Since this temperature range is a temperature suitable for the growth of the fermenting bacteria, the growth of the fermenting bacteria is further promoted by the heat generation of the garbage, and the fermentation decomposition of the garbage by the fermentation bacteria is further promoted. Moreover, since the evaporation of water in the garbage progresses due to the heat generation of the garbage, the fermentation decomposition of the garbage by the fermenting bacteria becomes easier and the fermented material obtained by the fermentation decomposition has a water content. Becomes lower and powdered.

発酵している生ゴミの温度がこの範囲に満たない場合には、50〜70℃程度に加熱しつつ本発酵工程をおこなうことで、発酵菌の生育が促進されて生ゴミの発酵分解が促進される。   If the temperature of the fermented garbage is less than this range, the main fermentation process is performed while heating to about 50 to 70 ° C., thereby promoting the growth of fermenting bacteria and promoting the fermentative decomposition of the garbage. Is done.

以下、本発明の生ゴミの処理方法を具体的に説明する。 Hereinafter, the garbage disposal method of the present invention will be described in detail.

(実施例1)
本発明の実施例1の生ゴミの処理方法を以下に示す。
(1)古紙発酵工程
(1−A)裁断工程
古紙10kgを裁断機にて裁断し、小片状古紙を形成した。
Example 1
A method for treating garbage in Example 1 of the present invention will be described below.
(1) Waste paper fermentation process (1-A) Cutting process 10 kg of waste paper was cut with a cutting machine to form small pieces of waste paper .

(1−B)前発酵工程
裁断工程で形成された小片状古紙全量に、水約6kgと栄養源としての米糠約1kgを添加し混合して、古紙、水および米糠からなる混合繊維材を得た。なお、このとき廃食用油やコーヒーかす等を栄養源として加えることもできる。
(1-B) About 6 kg of water and about 1 kg of rice bran as a nutrient source are added to and mixed with the entire amount of small pieces of waste paper formed in the pre-fermentation process cutting step, and a mixed fiber material composed of waste paper , water and rice bran is mixed. Obtained. At this time, waste cooking oil or coffee grounds can be added as a nutrient source.

この混合繊維材をコンクリート製の繊維発酵槽内に載置し、常温で1週間放置した。このとき、繊維発酵槽が設置された空間中の発酵菌が繊維発酵槽中の混合繊維材に付着して生育し、古紙の発酵が進行した。1週間の経過後に、混合繊維材を再度混合して全体を空気に曝すとともに混合繊維材中の水分量に応じてさらに水を加え、常温で7週間放置した。7週間の経過後に古紙のほぼ全体が発酵した発酵古紙が得られた。得られた発酵古紙を陰干しし乾燥さて水分量を調整した。
(2)本発酵工程
(2−A)混合工程
前発酵工程で得られた乾燥した発酵古紙10kgに対して生ゴミ約30kgと山土約4kgを加えて混合装置で約7時間混合した。生ゴミとしては、主に野菜や果物米飯、食肉等からなる残飯を含み、魚骨や鳥獣骨を含まないものを用いた。生ゴミ中には、野菜10重量部、果物2重量部、米飯15重量部、その他のもの(例えば、畜肉等)3重量部が含まれていた。また、山土としては粘土を多く含むものを用いた。なお、本混合工程において、混合は1.5分に1回の割合でおこなった。7時間後、得られた混合物は数ミリオーダーの小片となった。
The mixed fiber material was placed in a concrete fiber fermenter and allowed to stand at room temperature for 1 week. At this time, the fermenting bacteria in the space where the fiber fermenter was installed adhered to the mixed fiber material in the fiber fermenter and grew, and the fermentation of the used paper progressed. After 1 week, the mixed fiber material was mixed again and the whole was exposed to air, and water was further added according to the amount of water in the mixed fiber material, and the mixture was left at room temperature for 7 weeks. After 7 weeks, fermented waste paper in which almost the entire waste paper was fermented was obtained. The obtained fermented waste paper was shade-dried and dried to adjust the water content.
(2) Main fermentation step (2-A) About 30 kg of raw garbage and about 4 kg of mountain soil were added to 10 kg of dried fermented waste paper obtained in the fermentation step before the mixing step, and the mixture was mixed for about 7 hours with a mixing device. As raw garbage, the thing which contains the leftovers which consist mainly of vegetables, fruit rice, meat, etc., and does not contain a fish bone or a wild animal bone was used. The raw garbage contained 10 parts by weight of vegetables, 2 parts by weight of fruits, 15 parts by weight of cooked rice, and 3 parts by weight of other things (eg, livestock meat). The mountain soil used was one containing a lot of clay. In this mixing step, mixing was performed once every 1.5 minutes. After 7 hours, the resulting mixture became small pieces on the order of several millimeters.

(2−B)後発酵工程
混合工程で得られた混合物を後発酵槽に移し、混合物内部に空気を供給しつつ1週間発酵させた。このとき、空気の供給量は発酵の進行に応じて適宜調整した。1週間の経過後に、細かい細片状の前発酵体が得られた。得られた前発酵体を篩にかけ、篩を通過した粉末状の前発酵体のみを別の発酵槽に載置して、さらに1ヶ月発酵させた。1ヶ月の経過後に、発酵古紙と一体化した微粉末状の発酵体が得られた。この発酵体は無臭の微粉末であった。
(2-B) Post-fermentation step The mixture obtained in the mixing step was transferred to a post-fermentor and fermented for one week while supplying air to the inside of the mixture. At this time, the supply amount of air was appropriately adjusted according to the progress of fermentation. After 1 week, a fine strip-shaped pre-fermented product was obtained. The obtained pre-fermented material was passed through a sieve, and only the powdered pre-fermented material that passed through the sieve was placed in another fermenter and further fermented for 1 month. After 1 month, a fine powdery fermented body integrated with fermented waste paper was obtained. This fermented product was an odorless fine powder.

(実施例2)
本実施例2の生ゴミの処理方法は、本発酵工程で用いた生ゴミの種類以外は実施例1と同じ方法である。本実施例2において、生ゴミとしては実施例1と同じ生ゴミ100重量部に150重量部の魚アラを混合したものを用いた。なお、この魚アラは魚骨および魚肉を含むものであり、魚アラ100重量部中に20重量部の魚骨が含まれるものである。本実施例2の生ゴミの処理方法によると、通常発酵分解し難いとされている魚骨を含む生ゴミであるにも関わらず、実施例1の方法と同様に後発酵工程終了後には無臭の微粉体状の発酵体が得られた。
(Example 2)
The method for treating garbage in Example 2 is the same as that in Example 1 except for the type of garbage used in the main fermentation process. In the second embodiment, as the raw garbage, a mixture of 100 parts by weight of the same raw garbage as in Example 1 and 150 parts by weight of fish ara was used. This fish ara contains fish bone and fish meat, and 20 parts by weight of fish skeleton is contained in 100 parts by weight of fish ara. According to the method for treating garbage in this Example 2, although it is garbage containing fish bones that are usually difficult to be fermented and decomposed, it is odorless after the end of the post-fermentation step, as in the method of Example 1. A finely powdered fermented product was obtained.

(成分評価試験)
実施例1の処理方法で生成した発酵体および実施例2の方法で生成した発酵体の成分を分析した。その結果を表1に示す。
(Component evaluation test)
The components of the fermented material produced by the treatment method of Example 1 and the fermented material produced by the method of Example 2 were analyzed. The results are shown in Table 1.

Figure 0003999713
Figure 0003999713

表1に示される結果から、実施例1および実施例2の処理方法により生ゴミを発酵分解して得られた発酵体は堆肥に適した性質を持つことがわかる。   From the results shown in Table 1, it can be seen that the fermented material obtained by fermenting and decomposing garbage by the treatment methods of Example 1 and Example 2 has properties suitable for compost.

また、本実施例1および実施例2の生ゴミの処理方法により得られた発酵体は無臭の微粉末状のものであり、生ゴミの水分が発酵古紙に吸収されつつ発酵が進行したために虫や異臭の発生もなかった。また、一般に魚骨を含む魚のアラは発酵分解が困難とされ、魚のアラを混入した生ゴミを発酵分解させる為には予め魚のアラを細片状に切断する処理が必要とされている。しかし、本発明の実施例2の生ゴミの処理方法によると、魚のアラを切断することなく直接本発酵工程に供しても、後発酵工程の終了後には微粉体状の発酵体を得ることができた。 Moreover, the fermented material obtained by the processing method of the garbage of Example 1 and Example 2 is in the form of odorless fine powder, and the fermentation progressed while the moisture of the garbage was absorbed by the fermented waste paper. There was also no off-flavor. In general, fish arabic fish including fish bones is difficult to be fermented and decomposed, and in order to fermentate and decompose raw garbage mixed with fish ara, it is necessary to previously cut the fish arabic into strips. However, according to the processing method of the garbage of Example 2 of the present invention, even if it is directly subjected to the main fermentation step without cutting the fish ara, it is possible to obtain a fermented material in the form of a fine powder after the end of the post-fermentation step. did it.

また、得られた発酵体は堆肥として使用することができ、資源として有効利用することができる。   Moreover, the obtained fermented material can be used as compost and can be effectively used as a resource.

さらに、通常生ゴミの焼却処理には、水分の多い生ゴミを乾燥させるために多大な電力を要するが、本発明の生ゴミの処理方法によると、生ゴミの水分は発酵古紙に吸収されるとともに、発酵により生じた熱で蒸発する。したがって、本発明の生ゴミの処理方法に要する電力は少量で済み、生ゴミの処理を非常に安価に行うことが可能となる。参考までに、本発明の生ゴミの処理方法で、生ゴミ約4100kg(内訳は、米飯、野菜屑および果物屑約1800kg、魚アラ約2000kg、鳥骨約300kg)を処理するのに要する電気代は約8500円である。 Further, incineration of normal garbage requires a large amount of power to dry the garbage with a lot of moisture, but according to the method for treating garbage of the present invention, the moisture of the garbage is absorbed by the fermented waste paper. At the same time, it evaporates with the heat generated by fermentation. Therefore, a small amount of electric power is required for the garbage disposal method of the present invention, and the garbage disposal can be performed at a very low cost. For reference, the electricity bill required to process about 4100 kg of raw garbage (breakdown is about 1800 kg of cooked rice, vegetable and fruit waste, about 2000 kg of fish ara, about 300 kg of bird bones) with the method of processing garbage of the present invention. Is about 8500 yen.

さらに、通常魚骨や鳥獣骨を含む生ゴミの発酵分解には長期間を要するが、本実施例1および実施例2の生ゴミの処理方法によると、生ゴミの発酵分解には5週間程度を要するのみであり、生ゴミの発酵分解は迅速におこなわれた。   Furthermore, fermentation decomposition of raw garbage containing normal fish bones and animal bones requires a long period of time, but according to the method of treating garbage in Examples 1 and 2, the fermentation decomposition of garbage is about 5 weeks. The fermentation decomposition of raw garbage was carried out quickly.

Claims (8)

古紙を小片状にして小片状古紙を形成する工程と、該小片状古紙と栄養源と発酵菌とを混合して発酵させる工程と、を含み、該古紙の機械的強度を低下させてほぼ全体が発酵分解した発酵古紙を作る古紙発酵工程と、
該発酵古紙と生ゴミとを混合し該生ゴミを発酵分解させて該発酵古紙と一体化した粉末状の発酵体を得る本発酵工程と、備えることを特徴とする生ゴミの処理方法。
Reducing the mechanical strength of the waste paper, comprising a step of forming the waste paper into small pieces to form a small piece of waste paper, and a step of mixing and fermenting the small pieces of waste paper with nutrients and fermenting bacteria. Waste paper fermentation process to make fermented waste paper almost entirely fermented and decomposed ,
A method of treating garbage, comprising: a main fermentation step of mixing the fermented waste paper and raw garbage, fermenting and decomposing the raw garbage to obtain a powdered fermented body integrated with the fermented waste paper, and a fermentation process.
前記本発酵工程は、前記発酵古紙と前記生ゴミとを機械的に混合する混合工程と、該混合工程により得られた混合物を空気の存在下で発酵させる後発酵工程と、からなる請求項1に記載の生ゴミの処理方法。   The main fermentation step comprises a mixing step of mechanically mixing the fermented waste paper and the garbage, and a post-fermentation step of fermenting the mixture obtained by the mixing step in the presence of air. The processing method of the garbage described in 2. 前記後発酵工程は、前記混合物の内部に強制的に空気を供与しつつおこなう請求項2に記載の生ゴミの処理方法。   The method for treating garbage according to claim 2, wherein the post-fermentation step is performed while forcibly supplying air to the inside of the mixture. 前記本発酵工程は、50〜70℃でおこなう請求項1に記載の生ゴミの処理方法。   The said main fermentation process is a processing method of the garbage of Claim 1 performed at 50-70 degreeC. 前記栄養源は、米糠、食用廃油、豆類の絞り滓、乾燥させた鳥獣糞、コーヒーかすから選ばれる少なくとも一種を含む請求項1に記載の生ゴミの処理方法。   The method for treating garbage according to claim 1, wherein the nutrient source includes at least one selected from rice bran, edible waste oil, bean squeezed rice, dried bird and animal droppings, and coffee grounds. 前記混合工程は、混合された前記混合物を篩にかけ篩に残った物を再度前記混合工程に戻す処理を含む請求項2に記載の生ゴミの処理方法。   The said mixing process is a processing method of the garbage of Claim 2 including the process which sifts through the said mixed mixture and returns the thing which remained on the sieve to the said mixing process again. 前記生ゴミは、魚骨および/または鳥獣骨を含む請求項1に記載の生ゴミの処理方法。   The said garbage is a processing method of the garbage of Claim 1 containing a fish bone and / or a wild animal bone. 前記混合工程は、さらに、土を加えておこなう請求項2に記載の生ゴミの処理方法。   The garbage disposal method according to claim 2, wherein the mixing step is further performed by adding soil.
JP2003280380A 2003-07-25 2003-07-25 Garbage disposal method Expired - Fee Related JP3999713B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP2003280380A JP3999713B2 (en) 2003-07-25 2003-07-25 Garbage disposal method

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP2003280380A JP3999713B2 (en) 2003-07-25 2003-07-25 Garbage disposal method

Publications (2)

Publication Number Publication Date
JP2005040768A JP2005040768A (en) 2005-02-17
JP3999713B2 true JP3999713B2 (en) 2007-10-31

Family

ID=34266222

Family Applications (1)

Application Number Title Priority Date Filing Date
JP2003280380A Expired - Fee Related JP3999713B2 (en) 2003-07-25 2003-07-25 Garbage disposal method

Country Status (1)

Country Link
JP (1) JP3999713B2 (en)

Families Citing this family (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN100404473C (en) * 2006-11-09 2008-07-23 武汉理工大学 Innocuity method for treating disused stuffing material
CN100404474C (en) * 2006-11-09 2008-07-23 武汉理工大学 Method for preparing organic fertilizer from activated sludge of disused stuffing material

Also Published As

Publication number Publication date
JP2005040768A (en) 2005-02-17

Similar Documents

Publication Publication Date Title
CN110201972A (en) A method of it is handled using black soldier flies and utilizes kitchen garbage and stalk
CN103467143B (en) Airtight aerobic production process of bio-organic fertilizer by municipal sludge or kitchen biogas residues
CN105798050B (en) Kitchen castoff cooperates with treatment process with domestic garbage burning electricity generation
JP4698705B2 (en) Fermented fertilizer containing an active ingredient of bamboo and method for producing the same
Suthar Potential of domestic biogas digester slurry in vermitechnology
CN1680218B (en) Fermented fertilizer and its production
CN208787178U (en) Kitchen castoff resource utilization and nuisanceless disposal system
CN110014017A (en) Kitchen castoff bioconversion systems integrate and kitchen castoff bioconversion method
CN101913962A (en) Process for producing biological organic fertilizer by using garbage
CN103340139A (en) Method for utilizing cedar barks to produce soilless culture substrates
CN104230401A (en) Treatment method of kitchen garbage
Tratsch et al. Composition and mineralization of organic compost derived from composting of fruit and vegetable waste
CN108849757A (en) The method that changing food waste into resources utilizes
KR101553073B1 (en) Decoposing method for organic sludge
CN112474723B (en) Efficient microbial degradation method for kitchen garbage
JP3999713B2 (en) Garbage disposal method
CN104145879A (en) Method for simultaneously obtaining organic fertilizer and biological protein by means of utilizing hermetia illucens larvae to biologically treat inapplicable fresh tobacco leaves
JP2003235465A (en) Method for producing malt feed using oil and fat
KR101494327B1 (en) Method of pulverizing fermented food garbage and method of manufacturing environment-friendly biomass solid fuel using the food garbage
CN108142375A (en) The method of organic refuse fermentation residue Ecological Disposal and trans-utilization
Bajra et al. Determination of black soldier fly larvae performance for oil palm based waste reduction and biomass conversion
CN112552088A (en) Kitchen waste treatment method
JP3753627B2 (en) Organic waste treatment methods
Herlina et al. The effect of maggots lentera flies (hermetia illucens) growing media as the solution of using organic waste
KR102046797B1 (en) Manufacuring method of compost containing stevia powder and compost manufactured the same method

Legal Events

Date Code Title Description
A977 Report on retrieval

Free format text: JAPANESE INTERMEDIATE CODE: A971007

Effective date: 20050825

A131 Notification of reasons for refusal

Free format text: JAPANESE INTERMEDIATE CODE: A131

Effective date: 20051108

A521 Request for written amendment filed

Free format text: JAPANESE INTERMEDIATE CODE: A523

Effective date: 20051228

A131 Notification of reasons for refusal

Free format text: JAPANESE INTERMEDIATE CODE: A131

Effective date: 20061107

A02 Decision of refusal

Free format text: JAPANESE INTERMEDIATE CODE: A02

Effective date: 20070309

A521 Request for written amendment filed

Free format text: JAPANESE INTERMEDIATE CODE: A523

Effective date: 20070508

A521 Request for written amendment filed

Free format text: JAPANESE INTERMEDIATE CODE: A821

Effective date: 20070409

A911 Transfer to examiner for re-examination before appeal (zenchi)

Free format text: JAPANESE INTERMEDIATE CODE: A911

Effective date: 20070521

TRDD Decision of grant or rejection written
A01 Written decision to grant a patent or to grant a registration (utility model)

Free format text: JAPANESE INTERMEDIATE CODE: A01

Effective date: 20070726

A61 First payment of annual fees (during grant procedure)

Free format text: JAPANESE INTERMEDIATE CODE: A61

Effective date: 20070809

R150 Certificate of patent or registration of utility model

Free format text: JAPANESE INTERMEDIATE CODE: R150

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20100817

Year of fee payment: 3

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20110817

Year of fee payment: 4

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20120817

Year of fee payment: 5

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20130817

Year of fee payment: 6

R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250

R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250

R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250

LAPS Cancellation because of no payment of annual fees