JP2003160390A - Method for composting woody material - Google Patents

Method for composting woody material

Info

Publication number
JP2003160390A
JP2003160390A JP2001357996A JP2001357996A JP2003160390A JP 2003160390 A JP2003160390 A JP 2003160390A JP 2001357996 A JP2001357996 A JP 2001357996A JP 2001357996 A JP2001357996 A JP 2001357996A JP 2003160390 A JP2003160390 A JP 2003160390A
Authority
JP
Japan
Prior art keywords
composting
ridge
bacterium
bacteria
wood
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.)
Pending
Application number
JP2001357996A
Other languages
Japanese (ja)
Inventor
Norishige Uemura
憲重 植村
Hiroshi Nishioka
浩 西岡
Hisashi Teranishi
永 寺西
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
HOKUHAI KK
Original Assignee
HOKUHAI KK
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 HOKUHAI KK filed Critical HOKUHAI KK
Priority to JP2001357996A priority Critical patent/JP2003160390A/en
Publication of JP2003160390A publication Critical patent/JP2003160390A/en
Pending legal-status Critical Current

Links

Classifications

    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W30/00Technologies for solid waste management
    • Y02W30/40Bio-organic fraction processing; Production of fertilisers from the organic fraction of waste or refuse
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W30/00Technologies for solid waste management
    • Y02W30/50Reuse, recycling or recovery technologies
    • Y02W30/78Recycling of wood or furniture waste

Landscapes

  • Micro-Organisms Or Cultivation Processes Thereof (AREA)
  • Processing Of Solid Wastes (AREA)
  • Fertilizers (AREA)

Abstract

<P>PROBLEM TO BE SOLVED: To provide a method for converting woody materials such as trimmed root chips into a fully ripened compost in a short period of time. <P>SOLUTION: This method for composting woody materials comprises adding high temperature bacteria and cellulose-decomposing bacteria and/or lignin- decomposing bacteria to a ridge with piled woody materials. <P>COPYRIGHT: (C)2003,JPO

Description

【発明の詳細な説明】Detailed Description of the Invention

【0001】[0001]

【発明の属する技術分野】本発明は、伐根物、樹皮、枝
葉などの木質材料の堆肥化方法に関し、さらに詳しくは
微生物を用いて伐根チップなどの木質材料を短期間で完
熟堆肥にする方法に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method for composting woody materials such as root cuts, bark and branches and leaves. More specifically, it uses microorganisms to make woody materials such as rooted chips into fully matured compost in a short period of time. Regarding the method.

【0002】[0002]

【従来の技術】従来、道路工事やダム工事などの大規模
工事に伴う伐開事業から、街路樹などの剪定作業にいた
るまで、いたるところで伐根物、樹皮、枝葉などの木質
系廃棄物が排出されている。これら木質系廃棄物は焼却
処分や埋立処分、あるいは破砕処理後、家畜の敷材料や
木質系堆肥の原材料として使用されている。これらの木
質材料の焼却処理には、二酸化炭素やダイオキシン類の
発生による環境問題があり、また、木質材料の埋立処理
は、最終処分場の切迫および処分場用地の確保が困難に
なりつつあるなどの問題を抱えている。
2. Description of the Related Art Conventionally, wood-based wastes such as debris, bark, and branches are everywhere, from the cutting business associated with large-scale construction such as road construction and dam construction to pruning work such as street trees. Has been discharged. These wood-based wastes are used as livestock materials or raw materials for wood-based compost after incineration, landfill, or crushing. The incineration of these wood materials has environmental problems due to the generation of carbon dioxide and dioxins, and the landfill disposal of wood materials makes it difficult to secure the final disposal site and the land for disposal sites. Have a problem.

【0003】近年、循環型社会の形成に伴い、木質材料
についても堆肥化などの再生利用が積極的に行われるよ
うになってきている。堆肥は、以前より農作物などの植
物の生育促進や病害抑制のために有効利用されており、
この堆肥の炭素源としてしばしば木質材料が使用されて
いる。
In recent years, with the formation of a recycling society, wood materials have also been actively recycled for composting. Compost has been used for a long time to promote the growth of plants such as agricultural crops and to control diseases.
Woody materials are often used as the carbon source for this compost.

【0004】[0004]

【発明が解決しようとする課題】しかしながら、上記の
如き木質材料の未完熟な堆肥を土壌に施肥すると、木質
材料の嫌気発酵によるアンモニアなどの有害物質の発生
や、土壌の窒素飢餓を引き起こし、逆に植物に害を及ぼ
すことになってしまう。
However, when fertilizing unsaturated compost of woody material as described above to soil, it causes toxic substances such as ammonia due to anaerobic fermentation of woody material and nitrogen starvation of soil, and It will endanger the plants.

【0005】従来、木質材料を堆肥にする場合、その木
材の構成成分上、数年程度の長期に及ぶ堆積が必要とな
り、特に樹皮や枝葉などに比べ伐根物の堆肥化は非常に
難しいとされている。木質材料の堆肥化は、木質材料の
主要構成成分のセルロース、ヘミセルロース、リグニン
などが細菌、放線菌、真菌などの微生物により分解され
ていく現象と考えられる。
Conventionally, when composting a woody material, it is necessary to deposit it for a long time of several years due to the constituent components of the wood, and it is very difficult to compost a felled tree compared with bark and branches. Has been done. It is considered that the composting of wood materials is a phenomenon in which the main constituent components of wood materials, such as cellulose, hemicellulose, and lignin, are decomposed by microorganisms such as bacteria, actinomycetes, and fungi.

【0006】通常、木質材料の堆肥化は、自然堆積によ
る自然発酵が普通で、微生物に関しても自然環境からの
混入に依存している。一般的に、木材の発酵過程は3段
階(糖分解期、セルロース分解期、リグニン分解期)に
分けて捉えることができ、律速段階はリグニン分解期と
されている。リグニンの分解は、主に真菌の一群に属す
る白色腐朽菌や褐色腐朽菌によって行われるが、発酵過
程の前期は発熱発酵によりかなり高温状態で推移するた
め、堆肥化初期に殆どの腐朽菌が死滅してしまい、結果
的にリグニンの分解に年単位の時間を要することにな
る。このように、木質材料を完熟堆肥にするにはかなり
の年月を必要とするため、迅速かつ効率的な堆肥化方法
が希求されている。
Normally, in the composting of wood materials, natural fermentation by natural deposition is common, and microorganisms also depend on contamination from the natural environment. Generally, the fermentation process of wood can be divided into three stages (sugar decomposition period, cellulose decomposition period, lignin decomposition period), and the rate-determining step is the lignin decomposition period. The decomposition of lignin is mainly performed by white rot fungi and brown rot fungi belonging to a group of fungi, but in the early stage of the fermentation process, most of the rotten fungi die off at the early stage of composting because it changes to a fairly high temperature due to exothermic fermentation. As a result, it takes years to decompose lignin. As described above, since it takes a considerable amount of time to make a wooden material into a fully-ripened compost, a rapid and efficient composting method has been demanded.

【0007】従って、本発明の目的は、伐根チップなど
の木質材料を短期間で完熟堆肥にする方法を提供するこ
とにある。
Therefore, it is an object of the present invention to provide a method for converting a woody material such as felled root chips into a fully-ripened compost in a short period of time.

【0008】[0008]

【課題を解決するための手段】上記目的は以下の本発明
によって達成される。すなわち、本発明は木質材料を堆
積した畝に高温菌および、セルロース分解菌および/ま
たはリグニン分解菌を添加してなる木質材料の堆肥化方
法を提供する。
The above object can be achieved by the present invention described below. That is, the present invention provides a method for composting a wood material, which comprises adding a thermophilic bacterium and a cellulose-decomposing bacterium and / or a lignin-decomposing bacterium to a ridge having a wood-based material deposited thereon.

【0009】[0009]

【発明の実施の形態】次に好ましい実施の形態を挙げて
本発明をさらに詳しく説明する。本発明では、木質材料
を堆肥化するに当たり、木質材料を畝に堆積して、該堆
積物に高温菌および、セルロース分解菌および/または
リグニン分解菌を添加し、堆肥化を短時間で行うことを
特徴としている。
BEST MODE FOR CARRYING OUT THE INVENTION The present invention will be described in more detail with reference to the following preferred embodiments. In the present invention, when composting a wood material, the wood material is deposited on a ridge, and a thermophilic bacterium and a cellulolytic bacterium and / or a lignin degrading bacterium are added to the deposit to perform composting in a short time. Is characterized by.

【0010】従来は、木質材料を完熟堆肥にするまでに
数年程度の期間を必要としているが、本発明の方法のよ
うに、高温菌および、セルロース分解菌および/または
リグニン分解菌を使用することにより、難分解性のセル
ロースやヘミセルロース、リグニンを効果的に分解でき
るため、堆肥化時間を大幅に、例えば、3〜6ケ月程度
に短縮することが可能になる。
Conventionally, a period of several years is required until the woody material is made into a fully-ripened compost, but as in the method of the present invention, thermophilic bacteria and cellulolytic and / or lignin degrading bacteria are used. As a result, the hardly decomposable cellulose, hemicellulose, and lignin can be effectively decomposed, so that the composting time can be greatly shortened, for example, to about 3 to 6 months.

【0011】また、堆肥過程の糖分解期やセルロース分
解前期は比較的畝の温度は高温で推移するが、この時期
の温度上昇は病原菌や雑草種子を死滅させるためには非
常に重要である。従って、高温菌を接種し畝の温度を安
定して高温(70〜80℃ぐらい)に維持することも、
後にセルロース分解菌やリグニン分解菌を接種すること
と同様に、高品質の堆肥を製造する上で非常に意義のあ
ることである。
Further, the temperature of the ridges is relatively high during the sugar-decomposing period and the cellulose-decomposing period of the composting process, and the temperature increase during this period is very important for killing the pathogenic bacteria and weed seeds. Therefore, it is also possible to inoculate the ridge with a thermophilic bacterium and maintain the ridge temperature at a high temperature (70-80 ° C)
It is of great significance in producing high-quality compost, as in the case of inoculating cellulose-decomposing bacteria or lignin-decomposing bacteria later.

【0012】本発明では、木質材料として、伐根物、樹
皮、幹、枝葉、建築廃材などを使用することができ、で
きれば破砕機などを用いてチップ化して使用することが
望ましい。破砕サイズは数inchサイズのものが使用
できるが、微生物の育成上好ましくは0.1〜5inc
h程度の破砕サイズのチップが良い。また、オガクズな
どの木屑も使用可能である。
In the present invention, as the woody material, felled wood, bark, trunks, branches and leaves, construction waste materials, etc. can be used, and if possible, it is desirable to use them by crushing them into chips. The crushed size may be several inches, but preferably 0.1 to 5 inc for the growth of microorganisms.
A crush size chip of about h is good. Wood chips such as sawdust can also be used.

【0013】本発明は、炭素源、窒素源のバランスを考
慮して、適量のキノコの廃菌床を用いることが特に好ま
しい。木質材料の破砕チップと適量のキノコ廃菌床とを
よく混合し、水分を50〜60重量%前後に調節して畝
建てを行う。
In the present invention, it is particularly preferable to use an appropriate amount of mushroom waste bed in consideration of the balance of carbon source and nitrogen source. The crushed chips of wood material and an appropriate amount of mushroom waste bacterial bed are mixed well, and the water content is adjusted to about 50 to 60% by weight, and ridge construction is performed.

【0014】次に各種有用菌の接種を行う。先ず、接種
する菌の培養方法については通常の菌の培養と同様に行
うことができ、液体培養および固体培養のどちらの培養
方法でもよい。使用する培地は、通常、細菌あるいは真
菌を増殖させるのに適した培地を使用することができ
る。
Next, various useful bacteria are inoculated. First, the method for culturing the bacterium to be inoculated can be the same as that for culturing a normal bacterium, and either a liquid culture method or a solid culture method may be used. As a medium to be used, usually, a medium suitable for growing bacteria or fungi can be used.

【0015】また、液体培養あるいは固体培養された培
養物を、堆肥化する発酵畝に直接接種することも可能で
あるが、堆肥化する畝の1〜10重量%程度の少量の破
砕チップに菌を接種して前培養を行うことも可能であ
る。各有用菌の接種時期であるが、高温菌は畝建てを行
う時、あるいは畝建て直後の発酵初期に接種する。セル
ロース分解菌は、発熱発酵の中期以降、具体的には畝の
最高温度のピークを過ぎた時点で接種するのが好まし
い。
It is also possible to directly inoculate the fermented ridges to be composted with the culture that has been liquid-cultured or solid-cultured. However, a small amount of crushed chips of about 1 to 10% by weight of the ridges to be composted is used as a fungus. It is also possible to inoculate and preculture. Although it is the time of inoculation of each useful bacterium, the thermophilic bacterium is inoculated at the time of ridge building or at the early stage of fermentation immediately after ridge building. It is preferable to inoculate the cellulolytic bacterium after the middle stage of the exothermic fermentation, specifically, when the peak of the maximum temperature of the ridges has passed.

【0016】リグニン分解菌は、畝の温度が50〜60
℃に下降した時点で接種する。また、セルロース分解菌
およびリグニン分解菌を同時に添加することも可能であ
る。さらに、高温菌、セルロース分解菌およびリグニン
分解菌を常に全て使用する必然性はなく、堆肥化の進行
状況に応じて適宜選択して使用することもできる。使用
可能な高温菌には、バチルス属、ゲオバチルス属などが
あり、セルロース分解菌には、ペニシリウム属、グリオ
クラディウム属などがある。リグニン分解活性を示す微
生物には、ケトミウム属などに含まれる真菌がある。
The lignin-degrading bacterium has a ridge temperature of 50 to 60.
Inoculate when the temperature drops to ℃. It is also possible to simultaneously add the cellulolytic bacterium and the lignin degrading bacterium. Furthermore, it is not always necessary to use all thermophilic bacteria, cellulose-decomposing bacteria and lignin-decomposing bacteria, and they can be appropriately selected and used according to the progress of composting. Thermophilic bacteria that can be used include Bacillus and Geobacillus, and cellulolytic bacteria include Penicillium and Gliocladium. Microorganisms exhibiting lignin degrading activity include fungi contained in the genus Ketomium.

【0017】本発明方法の実施に際しては、畝の酸素量
や水分量を調節するために切り返しを行う必要がある。
切り返しは手動あるいはコンポストターナーなどの攪拌
機を使用して通常行われている方法で行うことができ、
その頻度は発酵畝の温度変化によるが、通常、月1〜2
回程度が望ましい。また、切り返し時に、畝の水分を5
0〜60重量%になるように調節することが好ましい。
In carrying out the method of the present invention, it is necessary to cut back in order to adjust the oxygen content and water content of the ridge.
The turning back can be performed manually or by using a stirrer such as a compost turner, which is a commonly used method.
The frequency depends on the temperature change of the fermentation ridge, but usually 1-2 months a month.
About once is desirable. Also, when turning back, remove water from the ridges by 5
It is preferable to adjust the content to be 0 to 60% by weight.

【0018】[0018]

【実施例】次に実施例および比較例を挙げて本発明をさ
らに具体的に説明する。伐根物をタブグラインダーと呼
ばれる破砕機で破砕し、0.1〜3inchサイズのチ
ップを約100m3作製した。この伐根物チップを1畝
25m3の割合で4畝に分割し、第1の畝には米糠(1
0kg/m3)のみ、第2の畝には米糠(10kg/
3)および石灰窒素(4.8kg/m3)を添加し、第
3の畝にはフスマ(10kg/m3)を添加し、第4の
畝には米糠(10kg/m3)に加え、さらに高温菌で
あるゲオバチルス属の菌を接種し、各畝を60重量%に
水分調整してから畝建てを行った。
EXAMPLES Next, the present invention will be described more specifically with reference to Examples and Comparative Examples. The root cuts were crushed by a crusher called a tab grinder to produce 0.1 to 3 inch size chips of about 100 m 3 . This root cut chip is divided into 4 ridges at a rate of 25 m 3 per ridge, and the first ridge is rice bran (1
0 kg / m 3 ) only, rice bran (10 kg / m 2) in the second ridge
m 3) and added lime nitrogen (4.8kg / m 3), the third ridges added bran (10kg / m 3), the fourth ridges added to rice bran (10 kg / m 3) Further, a bacterium of the genus Geobacillus, which is a thermophilic bacterium, was inoculated, and the water content of each ridge was adjusted to 60% by weight before ridge construction.

【0019】酸素供給および水分調整の目的で月1回の
割合で切り返しを行った。切り返し時に必要に応じて水
分補給も行った。第4の畝については、畝建て後3カ月
目にセルロース分解菌、5カ月目にリグニン分解菌の接
種を行った。このような状況で、6カ月間、4畝を堆積
させた。同時に畝の状態を大まかに把握する目的で、週
1〜2回、畝の温度(畝の上部から約50cmの畝内部
の温度)を測定した。
For the purpose of oxygen supply and water content adjustment, cutting was performed once a month. Hydration was also performed when necessary when turning back. The fourth ridge was inoculated with a cellulolytic bacterium 3 months after the ridge construction and a lignin degrading bacterium 5 months after the ridge. In such a situation, 4 ridges were deposited for 6 months. At the same time, the temperature of the ridges (the temperature inside the ridges about 50 cm from the top of the ridges) was measured once or twice a week for the purpose of roughly understanding the condition of the ridges.

【0020】4畝の比較を、先ず、畝温度について行う
と、図1に示したように、高温菌を接種していない第1
から第3までの畝は、最高温度が60℃台にとどまった
が、高温菌を接種した第4の畝のみが最高温度が81.
5℃まで上昇した。病原菌や雑草種子を死滅させるため
にも高温状態(70〜80℃)を再現性よく安定して維
持することが高品質の堆肥を製造する上で必須であるた
め、高温菌の接種は有効な手法と考えられる。また、堆
肥分析の結果(表1に示す)から、一般的にバーク堆肥
基準は、pHが中性付近で、炭素量が多く、C/N比が
35以下とされていることから、第4畝は、他の畝に比
べて堆肥化の完熟度が著しく高いことがわかる。よっ
て、セルロース分解菌およびリグニン分解菌の接種も堆
肥作製には有用な手法であることが示された。また、図
示してないが、ブナシメジ廃菌床を第4畝にさらに添加
したものも良好な結果が得られた。
The comparison of the four ridges was first carried out with respect to the ridge temperature. As shown in FIG. 1, the first ridge not inoculated with the thermophilic bacterium was used.
The maximum temperature of the ridges from No. 3 to No. 3 remained in the range of 60 ° C, but only the maximum temperature of the fourth ridge inoculated with the thermophilic bacterium was 81.
It rose to 5 ° C. In order to kill pathogenic bacteria and weed seeds, maintaining a high temperature condition (70-80 ° C) with good reproducibility and stability is essential for producing high-quality compost, so inoculation of thermophilic bacteria is effective. Considered a technique. In addition, from the results of compost analysis (shown in Table 1), it is generally said that the bark compost standard is that the pH is around neutral, the carbon content is large, and the C / N ratio is 35 or less. It can be seen that the ridge has a significantly higher degree of maturity in composting than the other ridges. Therefore, it was shown that inoculation of cellulose-decomposing bacteria and lignin-decomposing bacteria is also a useful method for compost production. Further, although not shown, good results were also obtained when the waste beech spore bed was further added to the fourth ridge.

【0021】さらに表2に示されるようにコマツナ種子
の発芽試験を行ったところ、堆肥として品質上問題のな
いことが確認された。発芽試験方法については以下に説
明する。上記第1〜4の畝の堆肥のそれぞれの生試料1
0gを、それぞれ200ml容三角フラスコにとり、沸
騰水100mlを加えアルミホイルで蓋をした。1時間
放置後、ガーゼ2枚を重ねて濾過し、この濾液10ml
を予め濾紙2枚を敷いてあるシャーレに分注した。一
方、対照(コントロール)として一旦沸騰させた水10
mlを用いて上記と同様にしてシャーレに分注した。こ
れらの5枚のシャーレ内にそれぞれコマツナ種子30粒
を播き、各シャーレに蓋をして室温に保持し、3日後に
発芽率と根の状態を観察した。
Further, as shown in Table 2, a germination test of Komatsuna seeds was carried out, and it was confirmed that the compost had no quality problem. The germination test method will be described below. Raw sample 1 of each of the above-mentioned first to fourth ridge composts
0 g of each was placed in a 200 ml Erlenmeyer flask, 100 ml of boiling water was added, and the flask was covered with an aluminum foil. After standing for 1 hour, 2 pieces of gauze were stacked and filtered, and 10 ml of this filtrate
Was dispensed into a petri dish on which two pieces of filter paper had been laid in advance. On the other hand, as a control, water 10 once boiled
Dispense into a petri dish in the same manner as above using ml. 30 seeds of komatsuna seeds were sown in each of these 5 petri dishes, each petri dish was covered with the lid and kept at room temperature, and after 3 days, the germination rate and the state of the roots were observed.

【0022】 [0022]

【0023】 [0023]

【0024】[0024]

【発明の効果】以上の如き本発明によれば、木質材料の
堆肥化を短期間で行うことができる。
As described above, according to the present invention, the composting of the woody material can be performed in a short period of time.

【図面の簡単な説明】[Brief description of drawings]

【図1】 堆肥過程における温度変化を示す図。FIG. 1 is a diagram showing a temperature change in a composting process.

───────────────────────────────────────────────────── フロントページの続き (72)発明者 寺西 永 北海道苫小牧市新開町4丁目2番7号 株 式会社ホクハイ内 Fターム(参考) 4B065 AA57X AC02 AC15 AC20 BB26 BC32 BC33 BC34 BC35 BC42 BC50 CA55 4D004 AA12 BA04 CA04 CA18 CB13 CC03 CC07 CC15 DA02 DA09 4H061 AA02 CC47 CC60 EE66 GG48   ─────────────────────────────────────────────────── ─── Continued front page    (72) Inventor Ei Teranishi             4-2-7 Shinkaimachi, Tomakomai City, Hokkaido             In ceremony company Hokuhai F-term (reference) 4B065 AA57X AC02 AC15 AC20                       BB26 BC32 BC33 BC34 BC35                       BC42 BC50 CA55                 4D004 AA12 BA04 CA04 CA18 CB13                       CC03 CC07 CC15 DA02 DA09                 4H061 AA02 CC47 CC60 EE66 GG48

Claims (2)

【特許請求の範囲】[Claims] 【請求項1】 木質材料を堆積した畝に高温菌および、
セルロース分解菌および/またはリグニン分解菌を添加
してなることを特徴とする木質材料の堆肥化方法。
1. A ridge in which a wood-based material is deposited, and a thermophilic bacterium,
A method for composting a wood material, comprising adding a cellulolytic bacterium and / or a lignin degrading bacterium.
【請求項2】 さらにキノコ廃菌床を添加してなる請求
項1に記載の木質材料の堆肥化方法。
2. The method for composting a wood material according to claim 1, further comprising a mushroom fungus bed.
JP2001357996A 2001-11-22 2001-11-22 Method for composting woody material Pending JP2003160390A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP2001357996A JP2003160390A (en) 2001-11-22 2001-11-22 Method for composting woody material

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP2001357996A JP2003160390A (en) 2001-11-22 2001-11-22 Method for composting woody material

Publications (1)

Publication Number Publication Date
JP2003160390A true JP2003160390A (en) 2003-06-03

Family

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Family Applications (1)

Application Number Title Priority Date Filing Date
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Country Status (1)

Country Link
JP (1) JP2003160390A (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2005306694A (en) * 2004-04-26 2005-11-04 Ueto:Kk Method for composting ginkgo leaf and ginkgo leaf compost
WO2007114324A1 (en) * 2006-03-31 2007-10-11 Menicon Co., Ltd. Method of treating biomass, compost, mulching material for livestock and agent for treating biomass

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2005306694A (en) * 2004-04-26 2005-11-04 Ueto:Kk Method for composting ginkgo leaf and ginkgo leaf compost
JP4500580B2 (en) * 2004-04-26 2010-07-14 株式会社植藤 Ginkgo leaf compost production method
WO2007114324A1 (en) * 2006-03-31 2007-10-11 Menicon Co., Ltd. Method of treating biomass, compost, mulching material for livestock and agent for treating biomass
US8268608B2 (en) 2006-03-31 2012-09-18 Menicon Co., Ltd. Method of treating biomass, compost, mulching material for livestock and agent for treating biomass

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