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JP3485345B2 - Composting accelerator - Google Patents
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JP3485345B2 - Composting accelerator - Google Patents

Composting accelerator

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Publication number
JP3485345B2
JP3485345B2 JP06769694A JP6769694A JP3485345B2 JP 3485345 B2 JP3485345 B2 JP 3485345B2 JP 06769694 A JP06769694 A JP 06769694A JP 6769694 A JP6769694 A JP 6769694A JP 3485345 B2 JP3485345 B2 JP 3485345B2
Authority
JP
Japan
Prior art keywords
composting
accelerator
filamentous fungus
composting accelerator
experimental example
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
JP06769694A
Other languages
Japanese (ja)
Other versions
JPH07247192A (en
Inventor
武宏 野本
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.)
Tsurumi Soda Co Ltd
Original Assignee
Tsurumi Soda Co Ltd
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 Tsurumi Soda Co Ltd filed Critical Tsurumi Soda Co Ltd
Priority to JP06769694A priority Critical patent/JP3485345B2/en
Publication of JPH07247192A publication Critical patent/JPH07247192A/en
Application granted granted Critical
Publication of JP3485345B2 publication Critical patent/JP3485345B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

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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
    • Y02ATECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
    • Y02A40/00Adaptation technologies in agriculture, forestry, livestock or agroalimentary production
    • Y02A40/10Adaptation technologies in agriculture, forestry, livestock or agroalimentary production in agriculture
    • Y02A40/20Fertilizers of biological origin, e.g. guano or fertilizers made from animal corpses

Landscapes

  • Fertilizers (AREA)
  • Preparation Of Compounds By Using Micro-Organisms (AREA)
  • Micro-Organisms Or Cultivation Processes Thereof (AREA)

Description

【発明の詳細な説明】 【0001】 【産業上の利用分野】本発明は、落葉、枯草、稲藁等の
植物遺体の堆肥化処理に用いる堆肥化促進剤に関するも
のである。 【0002】 【従来の技術】従来施肥法は通常化学肥料により行われ
ているが、この方法には、化学肥料の使用により土壌が
劣化し地力が低下するため、様々な植物の病害が発生す
ると共に、害虫に対する抵抗力も低下するという問題点
がある。そこで落葉、枯草、稲藁等の植物遺体を堆肥化
させて得られる有機物堆肥を畠土、水田、果樹園等へ施
肥することにより、土壌中の有用微生物を増殖させて地
力を回復させることが注目されている。このような有機
物堆肥は、従来、植物遺体に堆肥化を促進させる作用を
有する菌体を混入して放置し、植物を腐植させることに
より製造されている。 【0003】 【発明が解決しようとする課題】しかしながら上述の方
法では、堆肥化の進行は堆肥化促進菌体の性質に依存す
るため、菌体の生育に適する条件下においては堆肥化が
促進されるが、例えば低温下等の菌体の生育に不適切な
条件下においては堆肥化が促進されないという問題があ
った。従って、一般に菌体の生育に適する温度は10℃
以上望ましくは20℃以上であるので、気温がこの程度
となる季節には、比較的短期間で良質な有機物堆肥が製
造されるが、例えば気温が5℃以下となる冬期では、ほ
とんど堆肥化が進行しないことから有機物堆肥を製造す
ることは困難であった。 【0004】本発明は、このような事情のもとになされ
たものであり、その目的は、低温下においても、植物遺
体の堆肥化処理を行うことができる堆肥化促進剤を提供
することにある。 【0005】 【課題を解決するための手段】本発明の堆肥化促進剤
は、受託番号がFERM P−14027である糸状菌
NP−350を有効成分とすることを特徴とする。 【0006】 【作用】属、種が夫々Scedosporium,Ap
iospermumの好気性の細菌である糸状菌NP−
350を土壌中に含まれる菌群の中から選択培養し、こ
の糸状菌NP−350を有効成分とする堆肥化促進剤を
得る。糸状菌NP−350は植物の主成分であるセルロ
ースの分解能を有し、かつ好冷性を有するので、低温下
においても、植物遺体を分解して堆肥化を促進すること
ができる。 【0007】 【実施例】本発明の堆肥化促進剤は、受託番号 FER
M P−14027 糸状菌Scedosporium
Apiospermum(以下糸状菌NP−350と
いう。)を有効成分とするものであり、例えばこの糸状
菌NP−350を固体培養した後、細かく粉砕し、粉末
状としたものである。 【0008】本発明者らは、極寒地又は寒冷地において
例えば落葉、枯草、稲藁等の植物遺体の堆肥化処理を行
うことを目的としていたため、好冷性を有し、かつ植物
の主成分であるセルロースの分解能を有する微生物であ
れば、低温下においても植物遺体を分解して堆肥化を促
進することができるのではないかということに着目し
た。このため寒冷地の土壌にて低温領域でセルロースの
分解能を有する微生物の検索を行ったところ、糸状菌N
P−350を発見し、選択培養に成功することにより本
発明を完成するに至った。 【0009】この糸状菌NP−350は、本発明者らが
培養して得た、属、種が夫々Scedosporiu
m,Apiospermumである好気性の糸状菌であ
り、例えば表1に記載の組成を有するPotato D
extrose Agar培地やMalt Extra
ct Agar培地を用いて、培地のpHを4.6〜
4.8に調整した上、培養温度20℃の下で、長野県で
採取した土壌中に含まれる菌群の中から選択培養して得
たものである。また培養温度は25℃以下とすることが
望しい。 【0010】 【表1】そしてこのように固体培養して得られた糸状菌NP−3
50を例えば細かく粉砕して粉末状とし、植物遺体に散
布するかまたは混合することにより、植物の堆肥化処理
を行い有機物堆肥を製造する。 【0011】次に本発明の堆肥化促進剤の効果を確認す
るために行った実験例について説明する。 [実験例1]ヒマワリ種子残渣500kg、籾殻500
kgからなる植物遺体と、硫酸アンモニウム8kg、糸
状菌NP−350からなる堆肥化促進剤4kgとを混合
して試験区を設定した後、気温−3〜5℃の下で、4ヶ
月放置し、植物遺体の堆肥化処理を行い、有機物堆肥を
製造した。この後得られた有機物堆肥の腐植度、水分、
pH、全窒素濃度、全炭素濃度を夫々測定し、炭素率
(有機物堆肥の全炭素量/有機物堆肥の全窒素量)を計
算により求めた。また比較実験として堆肥化促進剤を添
加しない区(対照区)を設定し、同様の実験を行った。
この結果を表2に示す。 【0012】 【表2】[実験例2]ヒマワリ種子残渣500kg、籾殻500
kgからなる植物遺体に対して、糸状菌NP−350か
らなる堆肥化促進剤4kgとを混合して試験区を設定
し、比較実験として堆肥化促進剤を添加しない区を設定
して、気温−3〜5℃の下で実験例1と同様の実験を行
った。この結果を表3に示す。 【0013】 【表3】 [実験例3]バーク18000kg、バカスケーキ35
400kgからなる植物遺体と、乾燥鶏糞1000k
g、尿素300kg、油粕150kgと、糸状菌NP−
350からなる堆肥化促進剤50kgとを混合して試験
区を設定すると共に、比較実験として堆肥化促進剤を添
加しない区を設定し、気温2〜5℃の下で実験例1と同
様の実験を行った。この結果を表4に示す。 【0014】 【表4】[実験例4]バーク1000kgからなる植物遺体と、
硫酸アンモニウム55kgと、糸状菌NP−350から
なる堆肥化促進剤40kgとを混合して試験区を設定す
ると共に、比較実験として堆肥化促進剤を添加しない区
を設定し、気温2〜5℃の下で実験例1と同様の実験を
行った。この結果を表5に示す。 【0015】 【表5】 [実験例5]膨軟化籾殻4800kgからなる植物遺体
と、硫酸アンモニウム50kgと、糸状菌NP−350
からなる堆肥化促進剤5kgとを混合して試験区を設定
すると共に、比較実験として堆肥化促進剤を添加しない
区を設定し、気温2〜5℃の下で実験例1と同様の実験
を行った。この結果を表6に示す。 【0016】 【表6】[実験例6]膨軟化籾殻3000kgからなる植物遺体
と、硫酸アンモニウム27.5kgと、糸状菌NP−3
50からなる堆肥化促進剤3kgとを混合して試験区を
設定すると共に、比較実験として堆肥化促進剤を添加し
ない区を設定し、気温2〜5℃の下で実験例1と同様の
実験を行った。この結果を表7に示す。 【0017】 【表7】 [実験例7]稲藁500kgからなる植物遺体と、硫酸
アンモニウム10kgと、糸状菌NP−350からなる
堆肥化促進剤4kgとを混合して試験区を設定すると共
に、比較実験として堆肥化促進剤を添加しない区を設定
し、気温2〜5℃の下で放置期間を2ヶ月として実験例
1と同様の実験を行った。この結果を表8に示す。 【0018】 【表8】 [実験例8]バーク500kgからなる植物遺体と、鶏
糞10kgと、糸状菌NP−350からなる堆肥化促進
剤4kgとを混合して試験区を設定すると共に、比較実
験として堆肥化促進剤を添加しない区を設定し、気温2
〜8℃の下で実験例1と同様の実験を行った。この結果
を表9に示す。 【0019】 【表9】 [実験例9]稲藁250kg、オガクズ1250kgか
らなる植物遺体と、豚糞尿3000kg、オガクズ豚糞
尿500kgと、尿素20kgと、糸状菌NP−350
からなる堆肥化促進剤20kgとを混合して試験区を設
定すると共に、比較実験として堆肥化促進剤を添加しな
い区を設定し、気温2〜5℃の下で実験例1と同様の実
験を行った。この結果を表10に示す。 【0020】 【表10】 以上の実験結果により以下のことが確認された。即ち実
験例1〜9において、いずれの場合も糸状菌NP−35
0からなる堆肥化促進剤を添加して得られた有機物堆肥
の方が腐植度が高いことから、糸状菌NP−350を有
効成分とする堆肥化促進剤は、気温8℃以下さらには5
℃以下の低温下においても、植物遺体の分解能を有し、
堆肥化処理を進行させることができることが確認され
た。 【0021】また植物遺体としては、ヒマワリ種子残
渣、バーク、バカスケーキ、膨軟化籾殻、稲藁、オガク
ズ等を対象としたが、いずれの場合においても比較例に
比べて腐植度が高いことから、糸状菌NP−350を有
効成分とする堆肥化促進剤は、種々の植物に対して適用
できることが確認された。 【0022】さらに良質の有機物堆肥の水分含有率は約
60%、pHは約7.0であることが知られているが、
糸状菌NP−350からなる堆肥化促進剤を用いて製造
された有機物堆肥は、原料となる植物遺体や添加する材
料により多少の差異はあるが水分含有率は60%前後、
pHは7.0前後であることから、糸状菌NP−350
からなる堆肥化促進剤を用いて良質の有機物堆肥を製造
することができることが確認された。なお有機物堆肥の
水分含有量は水分調整剤の添加により調整される。 【0023】また夫々の実験例において、堆肥化促進剤
の他に、硫酸アンモニウム、乾燥鶏糞、尿素、油粕、豚
糞尿等を添加しているが、これらは従来から堆肥化を促
進させるために用いられているものであり、有機物堆肥
の炭素率を低くするために添加されるものである。即ち
炭素率は(有機物堆肥の炭素含有量)/(有機物堆肥の
窒素含有量)で計算されるものであり、炭素率が大きく
なる程微生物による分解がされにくくなることを示す
が、植物は炭素のみしか存在しないので、窒素の割合を
高めることが必要であり、このために添加されるもので
ある。 【0024】このように本発明の堆肥化促進剤は、植物
の主成分であるセルロースの分解能を有し、かつ好冷性
を有する糸状菌NP−350を有効成分としているの
で、例えば8℃以下の低温期においても植物遺体の分解
能を有する。従ってこの堆肥化促進剤を用いれば冬期や
寒冷地等の気温の低い季節や場所においても植物遺体の
堆肥化を促進し良質の有機物堆肥を製造することができ
る。 【0025】なお以上において、本発明の堆肥化促進剤
は、他の微生物を成分とする堆肥化促進剤に、糸状菌N
P−350を混合して構成するものであってもよい。 【0026】 【発明の効果】本発明によれば、植物の主成分であるセ
ルロースの分解能を有し、かつ、好冷性を有する糸状菌
を見出し、この糸状菌を有効成分とする堆肥化促進剤を
構成しているため、低温下においても植物の堆肥化処理
を行うことができる。
DETAILED DESCRIPTION OF THE INVENTION [0001] BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to defoliation, hay, rice straw and the like.
Composting accelerator used for composting of plant remains
It is. [0002] 2. Description of the Related Art Conventional fertilization methods are usually performed using chemical fertilizers.
However, this method involves the use of chemical fertilizers to remove soil.
Deterioration and deterioration of soil strength, causing various plant diseases
And the resistance to pests is reduced
There is. So composting plant remains such as leaf litter, hay, rice straw, etc.
The resulting organic compost is applied to the field, paddy fields, orchards, etc.
By fertilizing, useful microorganisms in the soil grow and
Attention has been focused on restoring strength. Such organic
Conventionally, compost has the effect of promoting composting of plant remains.
Humus plants
More manufactured. [0003] SUMMARY OF THE INVENTION
Method, the progress of composting depends on the nature of the composting-promoting cells
Therefore, composting under conditions suitable for cell growth
Promoted, but unsuitable for the growth of cells at low temperatures, for example
There is a problem that composting is not promoted under the conditions.
Was. Therefore, the temperature suitable for the growth of cells is generally 10 ° C.
More preferably, the temperature is about 20 ° C. or more.
High quality organic compost is produced in a relatively short period of time.
For example, in winter when the temperature falls below 5 ° C,
Organic compost is manufactured because composting hardly progresses
It was difficult to do. [0004] The present invention has been made under such circumstances.
The purpose is to keep the plant
Provides a composting accelerator that can perform body composting
Is to do. [0005] Means for Solving the Problems The present inventionComposting accelerator
IsAccession number is FERM P-14027Filamentous fungus
NP-350 is characterized as an active ingredient. [0006] [Action] The genus and species are Scedosporium and Ap, respectively.
Filamentous fungus NP-, an aerobic bacterium of iospermum
350 is selected and cultured from a group of bacteria contained in the soil.
Composting accelerator containing the filamentous fungus NP-350 as an active ingredient
obtain. The filamentous fungus NP-350 is a cellulos
It has the resolution of the source
Decompose plant remains to promote composting
Can be. [0007] EXAMPLES The composting promoter of the present invention has an accession number of FER
MP-14027 Filamentous fungus Scedosporium
  Apiospermum (hereinafter referred to as filamentous fungus NP-350)
Say. ) As the active ingredient.
After solid cultivation of the fungus NP-350, it is pulverized finely and powdered.
It is a shape. [0008] The present inventors have found that in extremely cold regions or cold regions.
For example, composting of plant remains such as leaf litter, hay, rice straw, etc.
Chilling properties and plants
Microorganisms that have the resolution of cellulose, the main component of
Decomposes plant remains and promotes composting even at low temperatures.
Focus on the possibility of progress
Was. For this reason, cellulose in low temperature region in cold climate soil
A search for microorganisms having a high resolution revealed that the filamentous fungi N
Discovered P-350 and succeeded in selective culture.
The invention has been completed. This filamentous fungus NP-350 has been developed by the present inventors.
The genus and species obtained by cultivation are Scedosporiu, respectively.
m, an aerobic filamentous fungus that is Apiospermum
For example, Potato D having the composition shown in Table 1
extrose Agar medium or Malt Extra
Using ct Agar medium, the pH of the medium was adjusted to 4.6-
After adjusting to 4.8, in Nagano Prefecture at a culture temperature of 20 ° C.
Selective cultivation from a group of bacteria contained in the collected soil
It is something. The culture temperature should be 25 ° C or less.
Hopeful. [0010] [Table 1]And the filamentous fungus NP-3 obtained by the solid culture in this manner.
50, for example, finely pulverized to a powder form,
Composting of plants by clothing or mixing
To produce organic compost. Next, the effect of the composting accelerator of the present invention will be confirmed.
An experimental example performed for this will be described. [Experimental example 1] Sunflower seed residue 500 kg, rice husk 500
kg of plant remains, ammonium sulfate 8 kg, thread
Mixed with 4 kg of composting accelerator consisting of fungi NP-350
After setting the test area, four months at a temperature of -3 to 5 ° C
Leave it for a month and compost the plant remains to remove organic compost.
Manufactured. Humidity, moisture,
Measure pH, total nitrogen concentration and total carbon concentration respectively, and
(Total carbon content of organic compost / Total nitrogen content of organic compost)
It was obtained by calculation. As a comparative experiment, a composting accelerator was added.
The same experiment was performed by setting a section (control section) where no addition was made.
Table 2 shows the results. [0012] [Table 2][Experimental example 2] 500 kg of sunflower seed residue, 500 husks
NP-350 for a plant body consisting of
4kg of composting promoter
As a comparative experiment, set a section where no composting accelerator was added
Then, the same experiment as in Experimental Example 1 was performed at a temperature of −3 to 5 ° C.
Was. Table 3 shows the results. [0013] [Table 3] [Experimental example 3] Bark 18000 kg, Bacas cake 35
400kg plant remains and 1000k dried chicken droppings
g, urea 300 kg, oil cake 150 kg, and filamentous fungus NP-
Tested by mixing with 350kg of composting accelerator consisting of 350
Set a plot and add a composting accelerator as a comparative experiment.
Set a ward not to add, and set the same as in Experimental Example 1 at a temperature of 2 to 5 ° C.
The same experiment was performed. Table 4 shows the results. [0014] [Table 4][Experimental example 4] A plant body consisting of 1000 kg of bark,
From 55 kg of ammonium sulfate and filamentous fungus NP-350
Mix with 40kg of composting accelerator to set up a test plot
As a comparative experiment,
And perform the same experiment as in Experimental Example 1 at a temperature of 2 to 5 ° C.
went. Table 5 shows the results. [0015] [Table 5] [Experimental example 5] Plant body consisting of 4800 kg of softened rice husk
And 50 kg of ammonium sulfate and the filamentous fungus NP-350
Test zone by mixing with 5 kg of composting accelerator consisting of
And do not add composting accelerator as a comparative experiment
Set the ward and conduct the same experiment as Experiment 1 under the temperature of 2-5 ° C
Was done. Table 6 shows the results. [0016] [Table 6][Experimental example 6] Plant body consisting of 3000 kg of softened rice husk
And 27.5 kg of ammonium sulfate, and the filamentous fungus NP-3
50kg composting accelerator and 3kg
Set and add a composting accelerator as a comparative experiment.
Set no ward, and use the same method as in Experimental Example 1 at a temperature of 2 to 5 ° C.
An experiment was performed. Table 7 shows the results. [0017] [Table 7] [Experimental example 7] A plant body consisting of 500 kg of rice straw and sulfuric acid
Consists of 10 kg of ammonium and filamentous fungus NP-350
Combine with 4 kg of composting accelerator to establish a test plot.
In the comparison, a section was set without adding a composting promoter as a comparative experiment
Example of an experiment where the temperature is 2 to 5 ° C and the storage period is 2 months
The same experiment as in Example 1 was performed. Table 8 shows the results. [0018] [Table 8] [Experimental example 8] Plant body consisting of 500 kg of bark and chicken
Composting promotion consisting of 10 kg of feces and filamentous fungus NP-350
4 kg, and set a test plot.
As a test, set a zone where no composting accelerator was added,
The same experiment as in Experimental Example 1 was performed at 88 ° C. As a result
Are shown in Table 9. [0019] [Table 9] [Experimental example 9] 250 kg of rice straw, 1250 kg of sawdust
Plant remains consisting of 3,000 kg of pig manure, sawdust pig manure
500 kg of urine, 20 kg of urea, and the filamentous fungus NP-350
With a composting accelerator consisting of 20 kg
And do not add a composting accelerator as a comparative experiment.
And set the same conditions as in Experimental Example 1 at a temperature of 2-5 ° C.
Test was carried out. Table 10 shows the results. [0020] [Table 10] The following was confirmed from the above experimental results. That is,
In Experimental Examples 1 to 9, in each case, the filamentous fungus NP-35 was used.
Organic compost obtained by adding a composting accelerator consisting of 0
Has a higher humus degree, and therefore has a filamentous fungus NP-350.
The composting accelerator used as an active ingredient has a temperature of 8 ° C.
Even at low temperatures below ℃, it has the resolution of plant remains,
It was confirmed that the composting process could proceed
Was. The plant remains include sunflower seed residues.
Residue, bark, bacas cake, softened rice hulls, rice straw, sawdust
, Etc., but in any case,
Compared to the high humus degree, it contains the filamentous fungus NP-350.
Composting accelerator as an active ingredient can be applied to various plants
It was confirmed that it was possible. Further, the water content of high quality organic compost is about
60%, pH is known to be about 7.0,
Manufactured using composting accelerator consisting of filamentous fungus NP-350
Organic compost is used as raw materials for plant remains and materials to be added.
There are some differences depending on the ingredients, but the water content is around 60%,
Since the pH is around 7.0, the filamentous fungus NP-350
High-quality organic compost using a composting accelerator consisting of
It was confirmed that it could be done. Organic compost
The water content is adjusted by adding a water regulator. In each of the experimental examples, a composting accelerator was used.
Besides, ammonium sulfate, dried chicken dung, urea, oil cake, pig
Manure is added, but these have conventionally promoted composting.
Organic compost
Is added in order to lower the carbon ratio. That is
The carbon ratio is (carbon content of organic compost) / (organic compost
Nitrogen content).
Indicates that it is difficult to be decomposed by microorganisms
However, because plants only contain carbon,
It is necessary to increase
is there. As described above, the composting promoter of the present invention can be used
It has the resolution of cellulose, the main component of
NP-350 having the active ingredient as an active ingredient
Decomposition of plant remains, for example, even at low temperatures of 8 ° C or less
Has ability. Therefore, if this composting accelerator is used,
Even in cold places such as cold seasons and places,
Promote composting and produce high quality organic compost
You. In the above, the composting accelerator of the present invention
Is a composting accelerator containing other microorganisms as a component;
P-350 may be mixed and constituted. [0026] According to the present invention, the cell which is a main component of a plant is
Filamentous fungi having reulose resolution and psychrophilic
And a composting accelerator containing this filamentous fungus as an active ingredient.
Composting of plants even at low temperatures
It can be performed.

───────────────────────────────────────────────────── フロントページの続き (56)参考文献 特開 平5−32658(JP,A) 特開 平7−149647(JP,A) 特開 平5−310707(JP,A) 特開 昭55−51789(JP,A) 特開 昭52−93569(JP,A) 特公 昭34−8875(JP,B1) 特表 平2−501733(JP,A) (58)調査した分野(Int.Cl.7,DB名) C05B 1/00 - C05G 5/00 C02F 11/00 - 11/20 B09B 1/00 - 5/00 C12N 1/00 - 1/38 C12P 1/00 - 1/06 BIOSIS(DIALOG)────────────────────────────────────────────────── ─── Continuation of the front page (56) References JP-A-5-32658 (JP, A) JP-A-7-149647 (JP, A) JP-A-5-310707 (JP, A) JP-A 55- 51789 (JP, A) JP-A-52-93569 (JP, A) JP-B-34-8875 (JP, B1) JP-T2-501733 (JP, A) (58) Fields investigated (Int. 7 , DB name) C05B 1/00-C05G 5/00 C02F 11/00-11/20 B09B 1/00-5/00 C12N 1/00-1/38 C12P 1/00-1/06 BIOSIS (DIALOG)

Claims (1)

(57)【特許請求の範囲】 【請求項1】 受託番号がFERM P−14027で
ある糸状菌NP−350を有効成分とする堆肥化促進
剤。
(57) [Claims] [Claim 1] The deposit number is FERM P-14027.
A composting accelerator comprising a certain filamentous fungus NP-350 as an active ingredient.
JP06769694A 1994-03-11 1994-03-11 Composting accelerator Expired - Fee Related JP3485345B2 (en)

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Application Number Priority Date Filing Date Title
JP06769694A JP3485345B2 (en) 1994-03-11 1994-03-11 Composting accelerator

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JP3485345B2 true JP3485345B2 (en) 2004-01-13

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JP (1) JP3485345B2 (en)

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JP2010161997A (en) * 2009-01-19 2010-07-29 Tech Corporation:Kk Method for producing saccharified liquid by using seed of assai palm and method for producing ethanol by using the saccharified liquid
JP5719067B1 (en) * 2014-08-27 2015-05-13 信雅 園井 Method for producing weed germination growth inhibiting material, weed germination growth inhibiting material obtained by the production method and cultivation method of paddy rice

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