JPH07247192A - Promoter for composting - Google Patents

Promoter for composting

Info

Publication number
JPH07247192A
JPH07247192A JP6067696A JP6769694A JPH07247192A JP H07247192 A JPH07247192 A JP H07247192A JP 6067696 A JP6067696 A JP 6067696A JP 6769694 A JP6769694 A JP 6769694A JP H07247192 A JPH07247192 A JP H07247192A
Authority
JP
Japan
Prior art keywords
composting
filamentous fungus
mold
promoter
plant
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Granted
Application number
JP6067696A
Other languages
Japanese (ja)
Other versions
JP3485345B2 (en
Inventor
Takehiro Nomoto
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

Abstract

PURPOSE:To obtain a promoter for composting capable of carrying out the composting treatment of the plant remains even at a low temperature. CONSTITUTION:This powdery promoter for composting is obtained by selecting a mold NP-350 which is an aerobic fungus of the species Apiospermum of the genus Scedosporium from a microorganism group contained in soil, culturing the selected mold in a potato dextrose agar culture medium, carrying out the solid culture of the mold NP-350 and then finely pulverize the culture. Since the mold NP-350 has the ability to decompose cellulose which is a main component of plants and further psychrophilic properties, the plant remains can be decomposed to promote the composting even at low temperatures.

Description

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

【0001】[0001]

【産業上の利用分野】本発明は、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。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a composting accelerator used for composting plant remains such as deciduous leaves, dead grass and rice straw.

【0002】[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。
2. Description of the Related Art Conventional fertilization methods are usually carried out using chemical fertilizers. However, the use of chemical fertilizers in this method deteriorates soil and reduces fertility, which causes various plant diseases and pests. There is a problem that the resistance to Therefore, by applying organic matter compost obtained by composting plant remains such as deciduous leaves, dead grass, and rice straw to soil, paddy fields, orchards, etc., useful microorganisms in the soil can be propagated to restore soil fertility. Attention has been paid. Such an organic matter compost has been conventionally produced by mixing a fungus body having an action of promoting composting with a plant body and leaving it to humus the plant.

【0003】[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。
However, in the above method, since the progress of composting depends on the properties of the composting-promoting cells, the composting is promoted under conditions suitable for the growth of the cells. For example, there is a problem that composting is not promoted under conditions unsuitable for the growth of bacterial cells, such as under low temperature. Therefore, the temperature suitable for the growth of bacterial cells is generally 10 ° C.
Since the temperature is preferably 20 ° C. or higher, high-quality organic compost is produced in a relatively short period in the season when the temperature is about this level. For example, in the winter when the temperature is 5 ° C. or lower, most of the compost is formed. It was difficult to produce organic compost because it did not progress.

【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。
The present invention has been made under such circumstances, and an object thereof is to provide a composting accelerator capable of performing composting treatment of plant remains even at low temperatures. is there.

【0005】[0005]

【課題を解決するための手段】本発明は、糸状菌NP−
350を有効成分とすることを特徴とする。
The present invention provides a filamentous fungus NP-
350 is an active ingredient.

【0006】[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。
[Function] The genus and species are Scedosporium and Ap, respectively.
Filamentous fungus NP- which is an aerobic bacterium of iospermum
350 is selectively cultivated from the bacteria group contained in the soil to obtain a composting promoter containing this filamentous fungus NP-350 as an active ingredient. Since the filamentous fungus NP-350 has the ability to decompose cellulose, which is the main component of plants, and has a psychrophilic property, it can decompose plant remains and promote composting even at low temperatures.

【0007】[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。
[Example] The composting promoting agent of the present invention has an accession number FER
MP-14027 Filamentous fungus Scedosporium
Apiospermum (hereinafter referred to as filamentous fungus NP-350) is used as an active ingredient. For example, the filamentous fungus NP-350 is solid-cultured and then finely pulverized into powder.

【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。
The present inventors have an object to perform composting treatment of plant remains such as deciduous leaves, dead grass and rice straw in extremely cold regions or cold regions. We paid attention to the fact that microorganisms capable of decomposing cellulose, which is a component, could decompose plant remains and promote composting even at low temperatures. Therefore, when a microorganism having a cellulose decomposing ability in a low temperature region was searched for in soil in a cold region, filamentous fungus N
The present invention was completed by discovering P-350 and succeeding in selective culture.

【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。
This filamentous fungus NP-350 has Scedosporiu of genus and species obtained by culturing by the present inventors.
m, Apiospermum, an aerobic filamentous fungus, for example, Potato D having the composition shown in Table 1.
extrose Agar medium and Malt Extra
Using ct Agar medium, adjust the pH of the medium to 4.6-
After being adjusted to 4.8, it was obtained by selective culturing from a group of bacteria contained in the soil collected in Nagano Prefecture at a culturing temperature of 20 ° C. Further, it is desirable that the culture temperature is 25 ° C or lower.

【0010】[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。
[Table 1] And the filamentous fungus NP-3 obtained by the solid culture in this way
For example, 50 is finely pulverized into a powder form, which is sprayed on or mixed with a plant body to produce a compost of a plant to produce an organic compost.

【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。
Next, an example of an experiment conducted to confirm the effect of the composting accelerator of the present invention will be described. Experimental Example 1 Sunflower seed residue 500 kg, rice husk 500
After the plant body consisting of kg, 8 kg of ammonium sulfate and 4 kg of a composting accelerator consisting of filamentous fungus NP-350 were mixed to set a test section, the plant was allowed to stand at a temperature of -3 to 5 ° C for 4 months, and the plant The body was composted to produce organic compost. The humus degree, water content, and
The pH, total nitrogen concentration, and total carbon concentration were measured, and the carbon rate (total carbon amount of organic compost / total nitrogen amount of organic compost) was calculated. As a comparative experiment, the same experiment was conducted by setting a section (control section) to which the composting accelerator was not added.
The results are shown in Table 2.

【0012】[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。
[Table 2] Experimental Example 2 Sunflower seed residue 500 kg, rice husk 500
A plant body consisting of kg was mixed with 4 kg of a composting promoter composed of filamentous fungus NP-350 to set a test section, and a group to which the composting promoter was not added was set as a comparative experiment, and the temperature- The same experiment as in Experimental Example 1 was performed under 3 to 5 ° C. The results are shown in Table 3.

【0013】[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。
[Table 3] [Experimental example 3] 18000 kg of bark, 35 bacas cake
400kg of plant body and 1000k of dried chicken manure
g, 300 kg urea, 150 kg oil cake, and filamentous fungus NP-
A test section was set by mixing with 50 kg of a composting accelerator composed of 350, and a section in which the composting accelerator was not added was set as a comparative experiment, and an experiment similar to that of Experimental Example 1 was performed under the temperature of 2 to 5 ° C. I went. The results are shown in Table 4.

【0014】[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。
[Table 4] [Experimental Example 4] A plant body consisting of 1000 kg of bark,
55 kg of ammonium sulfate and 40 kg of a composting accelerator composed of filamentous fungus NP-350 were mixed to set a test section, and as a comparative experiment, a section to which the composting accelerator was not added was set, and the temperature was 2 to 5 ° C. Then, the same experiment as in Experimental Example 1 was performed. The results are shown in Table 5.

【0015】[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。
[Table 5] [Experimental Example 5] Plant remains consisting of 4800 kg of softened and hulled rice husks, 50 kg of ammonium sulfate, and filamentous fungus NP-350.
5 kg of the composting accelerator consisting of is set as a test section, and a section where no composting accelerator is added is set as a comparative experiment, and the same experiment as in Experimental Example 1 is performed under the temperature of 2 to 5 ° C. went. The results are shown in Table 6.

【0016】[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。
[Table 6] [Experimental Example 6] A plant body composed of 3000 kg of softened and husks, 27.5 kg of ammonium sulfate, and filamentous fungus NP-3
An experiment similar to that of Experimental Example 1 was performed under a temperature of 2 to 5 ° C. by setting a test section by mixing with 3 kg of a composting accelerator consisting of 50 and setting a section in which a composting accelerator was not added as a comparative experiment. I went. The results are shown in Table 7.

【0017】[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。
[Table 7] [Experimental Example 7] A plant body composed of 500 kg of rice straw, 10 kg of ammonium sulfate, and 4 kg of a composting accelerator composed of filamentous fungus NP-350 were mixed to set a test section, and a composting accelerator was used as a comparative experiment. The same experiment as in Experimental Example 1 was performed under the condition that the temperature was kept at 2 to 5 ° C. and the period was left for 2 months. The results are shown in Table 8.

【0018】[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。
[Table 8] [Experimental Example 8] A plant body composed of 500 kg of bark, 10 kg of chicken feces, and 4 kg of a composting promoter composed of filamentous fungus NP-350 were mixed to set a test section, and a composting promoter was added as a comparative experiment. Set a ward that does not, temperature 2
An experiment similar to that of Experimental Example 1 was performed at -8 ° C. The results are shown in Table 9.

【0019】[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。
[Table 9] [Experimental Example 9] A plant body consisting of 250 kg of rice straw and 1250 kg of sawdust, 3000 kg of pig manure, 500 kg of sawdust pig, 20 kg of urea, and filamentous fungus NP-350.
20 kg of a composting accelerator consisting of is set as a test section, and a section where no composting accelerator is added is set as a comparative experiment, and the same experiment as in Experimental Example 1 is performed under an air temperature of 2 to 5 ° C. went. The results are shown in Table 10.

【0020】[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。
[Table 10] From the above experimental results, the following was confirmed. That is, in Experimental Examples 1 to 9, filamentous fungus NP-35 was used in all cases.
Since the organic matter compost obtained by adding the composting accelerator consisting of 0 has a higher degree of humus, the composting accelerator containing the filamentous fungus NP-350 as an active ingredient is not more than 5 ° C in temperature.
Even at low temperatures below ℃, it has the resolution of plant remains,
It was confirmed that the composting process could proceed.

【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。
As the plant remains, sunflower seed residues, bark, bacas cake, puffed rice hulls, rice straw, sawdust, etc. were used. In each case, the degree of humus was higher than that of the comparative example. It was confirmed that the composting promoter containing fungus NP-350 as an active ingredient can be applied to various plants.

【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。
It is known that the moisture content of high quality organic compost is about 60% and the pH is about 7.0.
The organic matter compost produced using the composting accelerator composed of the filamentous fungus NP-350 has a water content of about 60%, although there are some differences depending on the plant remains as raw materials and the added material.
Since the pH is around 7.0, the filamentous fungus NP-350
It was confirmed that a good quality organic matter compost can be produced by using the composting accelerator consisting of. The water content of the organic compost is adjusted by adding a water adjusting agent.

【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。
In addition, in each of the experimental examples, ammonium sulfate, dried chicken manure, urea, oil dregs, pig manure, etc. are added in addition to the composting accelerator, but these have been conventionally used to promote composting. It is added to reduce the carbon content of organic matter compost. That is, the carbon rate is calculated by (carbon content of organic matter compost) / (nitrogen content of organic matter compost), and it means that the higher the carbon rate, the more difficult it is to decompose by microorganisms. Since only there is present, it is necessary to increase the proportion of nitrogen, which is why it is added.

【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。
As described above, the composting accelerator of the present invention has the ability to decompose cellulose, which is the main component of plants, and the filamentous fungus NP-350, which has a psychrophilicity, as an active ingredient. It has the ability to decompose plant remains even in the low temperature period. Therefore, by using this composting accelerator, it is possible to promote composting of plant remains and produce a high-quality organic matter compost even in low temperatures and seasons such as winter and cold regions.

【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。
In the above, the composting promoter of the present invention is a fungal composting promoter containing other microorganisms as a component.
It may be configured by mixing P-350.

【0026】[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。
INDUSTRIAL APPLICABILITY According to the present invention, a filamentous fungus having the ability to decompose cellulose, which is a main component of plants, and having a psychrophilicity, was found, and a composting accelerator containing the filamentous fungus as an active ingredient was constructed. Therefore, the composting process of the plant can be performed even at a low temperature.

Claims (1)

【特許請求の範囲】[Claims] 【請求項1】 糸状菌NP−350を有効成分とする堆
肥化促進剤。
1. A composting accelerator containing filamentous fungus NP-350 as an active ingredient.
JP06769694A 1994-03-11 1994-03-11 Composting accelerator Expired - Fee Related JP3485345B2 (en)

Priority Applications (1)

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

Applications Claiming Priority (1)

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

Publications (2)

Publication Number Publication Date
JPH07247192A true JPH07247192A (en) 1995-09-26
JP3485345B2 JP3485345B2 (en) 2004-01-13

Family

ID=13352386

Family Applications (1)

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

Country Status (1)

Country Link
JP (1) JP3485345B2 (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
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

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
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
JP2016047778A (en) * 2014-08-27 2016-04-07 信雅 園井 Manufacturing method of weed germination/growth suppression material, weed germination/growth suppression material obtained by the manufacturing method, and cultivation method of paddy rice

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