JPH11225747A - Microorganism degrading organic material, culturing material composition thereof, and prevention of fairy ring disease by using the culturing material composition - Google Patents

Microorganism degrading organic material, culturing material composition thereof, and prevention of fairy ring disease by using the culturing material composition

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Publication number
JPH11225747A
JPH11225747A JP10029537A JP2953798A JPH11225747A JP H11225747 A JPH11225747 A JP H11225747A JP 10029537 A JP10029537 A JP 10029537A JP 2953798 A JP2953798 A JP 2953798A JP H11225747 A JPH11225747 A JP H11225747A
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JP
Japan
Prior art keywords
meal
oil residue
material composition
bone meal
ammonium
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
JP10029537A
Other languages
Japanese (ja)
Other versions
JP3283228B2 (en
Inventor
Katsunori Noguchi
勝憲 野口
Yuzo Kinooka
雄三 紀岡
Hiroaki Masumura
弘明 増村
Takanori Akazawa
貴徳 赤澤
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.)
Katakura Chikkarin Co Ltd
Original Assignee
Katakura Chikkarin Co Ltd
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Publication date
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Priority to JP02953798A priority Critical patent/JP3283228B2/en
Publication of JPH11225747A publication Critical patent/JPH11225747A/en
Application granted granted Critical
Publication of JP3283228B2 publication Critical patent/JP3283228B2/en
Anticipated expiration legal-status Critical
Expired - Lifetime legal-status Critical Current

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

Abstract

PROBLEM TO BE SOLVED: To obtain a new microorganism useful for degradation of organic materials such as composting of organic materials such as straw, bark and waste of stock raising, and degradation promotion of garbage. SOLUTION: This new microorganism is selected from Penicillium sp. CF-1 (FERM P-16479), Penicillium sp. FS-26 (FERM P-16480) and Penicillium sp. FS-29 (FERM P-16481), having cellulose-degrading activities, and Bacillus sp. LB-5 (FERM P-16485), Debaryomyces sp. LB-31 (FERM P-16484), Aspergillus sp. LF-3 (FERM P-16482) and Aspergillus sp. FS-35 (FERM P-16483), having lignin-degrading activities. The cultivating material composition is preferably prepared by including one or more kinds of the new microorganisms and a cultivating material such as vermiculite.

Description

【発明の詳細な説明】DETAILED DESCRIPTION OF THE INVENTION

【0001】[0001]

【産業上の利用分野】本発明は新規微生物および新規微
生物を添加した培養資材組成物であり、イナワラ、バー
ク、畜産廃棄物などの有機物の堆肥化や生ゴミの分解促
進などの有機物分解に有用なものである。さらに当該培
養資材組成物を用いた芝のフェアリーリング病の防除方
法に関するものである。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a novel microorganism and a culture material composition to which the novel microorganism is added, and is useful for composting organic matter such as rice straw, bark, livestock waste, and decomposing organic matter such as accelerating the decomposition of garbage. It is something. Further, the present invention relates to a method for controlling turf fairy ring disease using the culture material composition.

【0002】[0002]

【従来の技術】従来有機物の腐熟促進を目的とする資材
としては、石灰窒素、苦土石灰等の石灰質資材が一般的
に使われている。また、近年では微生物や酵素を使った
資材も数多く流通している。しかし、石灰窒素や苦土石
灰を加えた場合、有機物の分解に伴うpHの上昇により
アルカリ過剰となる。一方、微生物や酵素を使った資材
では添加している微生物の種類を明らかにしているもの
はわずかしかなく、その作用機作も明らかとなっていな
い。かかる現状のもとで微生物を用いたより効果の高い
ものが求められている。
2. Description of the Related Art Conventionally, calcareous materials such as lime nitrogen and magnesite lime are generally used as materials for promoting the maturation of organic substances. In recent years, many materials using microorganisms and enzymes have been distributed. However, when lime nitrogen or formic lime is added, the alkali is excessive due to the increase in pH accompanying the decomposition of organic matter. On the other hand, very few materials using microorganisms or enzymes clarify the type of microorganism added, and the mechanism of action is not clear. Under these circumstances, there is a need for more effective ones using microorganisms.

【0003】また、ゴルフ場では刈り芝等の有機物が土
壌に蓄積することにより、フェアリーリング病が発生
し、この防除には化学農薬に頼っているが、シロを形成
した担子菌類は容易に死滅させることができず、芝草の
外観を大きく損なう。最終的には芝の更新が必要とな
り、経済的損失は大きい。そこで、化学農薬に頼らない
フェアリーリング病の防除方法が望まれている。
[0003] In a golf course, fairy grass disease occurs due to the accumulation of cut grass and other organic matter in the soil, and chemical pesticides are used to control this. However, basidiomycetes that have formed white soil easily die. And the appearance of turfgrass is greatly impaired. Ultimately, the turf needs to be renewed, and the economic loss is large. Therefore, a method for controlling fairy ring disease that does not rely on chemical pesticides is desired.

【0004】なお、フェアリーリング病とは芝草が円形
または弧状に枯れあがる病害であり、サッチおよび土壌
に多量の担子菌類が生息すると発生するものである。こ
の病原菌は主としてハラタケ科の担子菌類である。この
フェアリーリング病は水分および肥料の少ないフェアウ
ェー、サッチ層の発達したターフやサンドグリーンで被
害を生じやすいものである。
[0004] Fairy ring disease is a disease in which turfgrass wilts in a circular or arc shape, and occurs when a large amount of basidiomycetes inhabits thatch and soil. This pathogen is mainly a Basidiomycete fungus. This fairy ring disease is susceptible to damage on fairways with low moisture and fertilizer, turfs and sand greens with a developed thatch layer.

【0005】[0005]

【発明が解決しようとする課題】本発明が解決しようと
する課題は、分解が困難なセルロースおよびリグニンを
分解する新規微生物、これらの微生物を使ったオガク
ズ、バークなどの木質物、イナワラ、ムギワラなどのワ
ラ類、モミガラ、フスマなどの穀物残さ、茶・果樹等の
剪定枝、野菜等収穫残さ、ゴルフ場などよりでる刈り
芝、家庭から排泄される生ゴミ、家畜排泄物、食品産業
廃棄物等の分解を促進する培養資材組成物、および前記
微生物を含む芝のフェアリーリング病の防除剤を提供す
ることにある。
The problems to be solved by the present invention are novel microorganisms which degrade cellulose and lignin which are difficult to decompose, woody materials such as sawdust and bark using these microorganisms, rice straw and wheat straw. Grass residues such as straws, peaches, bran, etc., pruned branches such as tea and fruit trees, crop residues such as vegetables, cut grass from golf courses, garbage excreted from homes, livestock excrement, food industry waste, etc. It is an object of the present invention to provide a culture material composition for accelerating the decomposition of turf, and an agent for controlling turf fairy ring disease containing the microorganism.

【0006】[0006]

【課題を解決させるための手段】即ち、本発明はセルロ
ース分解能を有するPenicillium sp.CF−1、Penicil
lium sp.FS−26又はPenicillium sp.FS−29か
ら選ぶ微生物である。
That is, the present invention relates to Penicillium sp.
lium sp. FS-26 or Penicillium sp. FS-29.

【0007】さらに、本発明はリグニン分解能を有する
Bacillus sp.LB−5である。
Further, the present invention has a lignin decomposability.
Bacillus sp. LB-5.

【0008】さらに、本発明はリグニン分解能を有する
Debaryomyces sp.LB−31である。
Further, the present invention has lignin decomposability.
Debaryomyces sp. LB-31.

【0009】さらに、本発明はリグニン分解能を有する
Aspergillus sp.LF−3又はAspergillus sp.FS−3
5である。
Further, the present invention has lignin decomposability.
Aspergillus sp. LF-3 or Aspergillus sp. FS-3
5

【0010】さらに、本発明は上記微生物の少なくとも
一種と培養資材とを含む培養資材組成物である。
Further, the present invention is a culture material composition containing at least one of the above microorganisms and a culture material.

【0011】さらに、本発明は上記微生物とセルロース
分解能を有するBacillus sp. BS-1SMCP III の少なくと
も一種と培養資材とを含む培養資材組成物である。
Further, the present invention is a culture material composition comprising the above microorganism, at least one of Bacillus sp. BS-1SMCP III having cellulolytic ability, and a culture material.

【0012】前記培養資材としてはバーミキュライト、
ゼオライト、パーライト、モンモリロナイトなどの無機
質鉱物、硫酸アンモニウム、塩化アンモニウム、硝酸ア
ンモニウム、過燐酸石灰、リン酸アンモニウム、硫酸カ
リウム、塩化カリウムなどの化成肥料、硫酸第一鉄、塩
化第一鉄などの鉄化合物、ケイソウ土、焼成ケイソウ
土、サンゴ砂、木炭粉末、活性炭などの多孔質物、ナタ
ネ油かす、コメヌカ油かす、ヒマシ油かす、ダイズ油か
すなどの植物質肥料、蒸製骨粉、生骨粉、脱膠骨粉、肉
骨粉、肉かす、魚かす、フェザーミール、蒸製毛粉、カ
ニガラ、皮粉、さなぎかすなどの動物質肥料およびこれ
らの混合物からなる群より選抜されたものが挙げられ
る。
As the culture material, vermiculite,
Inorganic minerals such as zeolite, perlite, montmorillonite, ammonium fertilizers such as ammonium sulfate, ammonium chloride, ammonium nitrate, lime superphosphate, ammonium phosphate, potassium sulfate, potassium chloride, iron compounds such as ferrous sulfate and ferrous chloride, and diatomaceous Porous materials such as soil, calcined diatomaceous earth, coral sand, charcoal powder, and activated carbon; vegetable fertilizers such as rapeseed oil cake, rice bran oil cake, castor oil cake, and soybean oil cake, steamed bone meal, raw bone meal, deflocculated bone meal, and meat Examples include those selected from the group consisting of animal fertilizers such as bone meal, meat meal, fish meal, feather meal, steamed hair meal, crab, skin powder, and pupa, and mixtures thereof.

【0013】さらに、本発明は、上記微生物が上記培養
資材中で培養してなることを特徴とする培養資材組成物
である。
Further, the present invention is a culture material composition, wherein the microorganism is cultured in the culture material.

【0014】さらに、本発明は当該培養資材組成物を用
いた芝のフェアリーリング病の防除方法に関するもので
ある。
Further, the present invention relates to a method for controlling fairy fairy disease of turf using the culture material composition.

【0015】[0015]

【発明の実施の態様】以下、本発明を詳細に説明する。BEST MODE FOR CARRYING OUT THE INVENTION Hereinafter, the present invention will be described in detail.

【0016】本発明のリグニンまたはセルロース分解微
生物の分離、選抜方法及びこれら微生物を含む培養資材
組成物の製造法について説明する。
The method for separating and selecting lignin- or cellulose-degrading microorganisms of the present invention and the method for producing a culture material composition containing these microorganisms will be described.

【0017】[セルロース分解菌の分離]各地より採取
した土壌、堆肥などから、希釈平板法により分離した菌
株をCMC(カルボキシメチルセルロース)含有平板培
地(CMC 5g、KH2PO4 4g、Na2HPO4 6g、(NH4)2SO4 2g、
MgSO4・7H2O 200mg、CaCl2 1mg、Fe2(SO4)・7H2O、酵母
エキス 1g、H3BO3 10μg、MnSO4 10μg、ZnSO4 70μ
g、CuSO4 50μg、MoO3 10μg、寒天 15g、蒸留水 1000
ml、pH 7)を用いて、10℃、30℃、50℃で培養し、培地
上にクリアゾーンを形成した菌株を選抜した。この選抜
した菌株を0.5%CMC含有無機塩液体培地50mLに添加し
て、10℃、30℃、50℃で1週間培養後、培養液を遠心分
離した上澄み液を以下の分析に供した。すなわち、得ら
れた上澄み液の全糖量をフェノール硫酸法、還元糖量を
改変ソモギ法により定量し、全糖量の減少が著しい菌株
もしくは還元糖の生成量が多い菌株をセルロース分解能
が高い菌株として選抜した。同時に、イナワラを粉砕し
尿素を添加して炭素率を調整後、イナワラの最大保水量
相当量の蒸留水を加え、オートクレーブで121℃で30分
滅菌した。ここへ菌株を添加して選抜した温度で4週間
インキュベートした後の炭素率を測定した。その結果を
表1に示す。
[Isolation of Cellulose-Decomposing Bacteria] Strains isolated from soil, compost, etc. collected from various places by a dilution plate method were subjected to CMC (carboxymethylcellulose) -containing plate medium (5 g of CMC, 4 g of KH 2 PO 4, Na 2 HPO 4). 6 g, (NH 4 ) 2 SO 4 2 g,
MgSO 4 · 7H 2 O 200mg, CaCl 2 1mg, Fe 2 (SO 4) · 7H 2 O, yeast extract 1g, H 3 BO 3 10μg, MnSO 4 10μg, ZnSO 4 70μ
g, CuSO 4 50μg, MoO 3 10μg, agar 15 g, distilled water 1000
The strain was cultured at 10 ° C., 30 ° C., and 50 ° C., and a strain having a clear zone formed on the medium was selected. The selected strain was added to 50 mL of an inorganic salt liquid medium containing 0.5% CMC, cultured at 10 ° C., 30 ° C., and 50 ° C. for 1 week, and the supernatant obtained by centrifuging the culture was subjected to the following analysis. That is, the total amount of sugar in the obtained supernatant is quantified by the phenol sulfate method, and the amount of reducing sugar is quantified by the modified Somogi method. Was selected as At the same time, the rice straw was pulverized and urea was added to adjust the carbon content. Then, distilled water equivalent to the maximum water retention of the rice straw was added, and the mixture was sterilized in an autoclave at 121 ° C. for 30 minutes. The strain was added thereto, and the carbon ratio after incubation at the selected temperature for 4 weeks was measured. Table 1 shows the results.

【0018】[0018]

【表1】 [Table 1]

【0019】[リグニン分解菌の分離]各地より採取し
た土壌、堆肥などから、希釈平板法により分離した菌株
をリグニンスルホン酸含有平板培地(リグニンスルホン
酸Na 0.1g、NH4NO3 1.0g、K2HPO4 1.0g、MgSO4・7H2O
0.5g、蒸留水1000ml、pH6.8)を用いて、30℃で培養
し、バーベンダム反応陽性株、グアヤコール添加培地に
おける赤色反応陽性株の選抜、プロトカテキン酸分解能
による選抜により一次選抜を行った。
[Isolation of Lignin-Decomposing Bacteria] From a soil, compost, etc. collected from various places, a strain isolated by a dilution plate method was converted into a ligninsulfonic acid-containing plate medium (ligninsulfonic acid Na 0.1 g, NH 4 NO 3 1.0 g, K 2 HPO 4 1.0g, MgSO 4・ 7H 2 O
Using 0.5 g, 1000 ml of distilled water, pH 6.8), the cells were cultured at 30 ° C., and primary selection was performed by selecting a Barbendam reaction-positive strain, a red reaction-positive strain in a guaiacol-supplemented medium, and selection by protocatechinic acid resolution.

【0020】上記の方法により選抜した菌株を、木粉抽
出液体培地(木粉20g、 NH4NO3 1.0g、 K2HPO4 1.0g、 M
gSO4・7H2O 0.5g、蒸留水1000ml、pH6.8)へ接種し30
℃で2週間振とう培養を行い、この培養液を遠心分離し
た上澄み液を以下の分析に供した。すなわち、得られた
上澄み液の全糖量をフェノール硫酸法、還元糖量を改変
ソモギ法、蛋白質をLowry法、紫外部吸収物質を280nmに
おける吸光度測定により定量した。その結果を表2に示
す。
The strain selected by the above method was transformed into a wood flour extraction liquid medium (wood flour 20 g, NH 4 NO 3 1.0 g, K 2 HPO 4 1.0 g, M
gSO 4 · 7H 2 O 0.5g, distilled water 1000 ml, was inoculated into pH 6.8) 30
Shaking culture was performed at 2 ° C. for 2 weeks, and the supernatant obtained by centrifuging the culture was subjected to the following analysis. That is, the total amount of sugar in the obtained supernatant was quantified by the phenol sulfate method, the amount of reducing sugar was modified by the Somogi method, the protein was determined by the Lowry method, and the ultraviolet absorbing substance was measured by absorbance measurement at 280 nm. Table 2 shows the results.

【0021】[0021]

【表2】 [Table 2]

【0022】本発明で使用する新規微生物の由来及びそ
の菌学的性質について説明する。
The origin of the novel microorganism used in the present invention and its mycological properties will be described.

【0023】1)LB−5株は、バーク堆肥より分離し
た50℃前後の高温域でリグニン分解能を有する新規微生
物である。本菌株の特徴は表3に示した通りであり、形
態および生理試験からBacillusに属し、近縁種としてBa
cillus azotoformansがあげられるが、グルコース、マ
ンニトールの資化性およびデンプンの分解などで異な
り、したがって、この菌株を新種相当と認定した。そし
て、この菌株をBacillus sp.LB−5とした。この菌株
は工業技術院生命工学工業技術研究所にFERM P-16485
として寄託している。
1) The LB-5 strain is a novel microorganism having lignin degradability at a high temperature of about 50 ° C. isolated from bark compost. The characteristics of this strain are as shown in Table 3. It belongs to Bacillus from morphological and physiological tests,
cillus azotoformans, which differed in glucose, mannitol assimilation, and starch degradation. Therefore, this strain was identified as a new species. This strain was designated as Bacillus sp. LB-5. This strain was transferred to FERM P-16485 by the National Institute of Bioscience and Human Technology.
Has been deposited.

【0024】[0024]

【表3】 [Table 3]

【0025】2)LB−31株は、北海道サロベツ泥炭
より分離した10℃前後の低温域でリグニン分解能を有す
る新規微生物である。本菌株の特徴は表4、5の通りで
あり、有胞子酵母類に分類され、栄養細胞、胞子の形態
および形成状況およびコロニーの形態、色などからDeba
ryomyces castelliiの近縁種であるが、糖の資化性等で
異なり、したがって、この菌株を新種相当と認定した。
そして、この菌株をDebaryomyces sp.LB−31とし
た。この菌株は工業技術院生命工学工業技術研究所にFE
RM P-16484として寄託している。
2) The LB-31 strain is a novel microorganism having a lignin degrading ability at a low temperature around 10 ° C. isolated from Hokkaido Sarobetsu peat. The characteristics of this strain are as shown in Tables 4 and 5, which are classified into spore-forming yeasts, and are characterized by vegetative cells, spore morphology and formation status, colony morphology and color, etc.
Although it is a related species of ryomyces castellii, it differs due to the assimilation of sugar and the like. Therefore, this strain was identified as a new species.
This strain was named Debaryomyces sp. LB-31. This strain was fed to the Institute of Biotechnology,
Deposited as RM P-16484.

【0026】[0026]

【表4】 [Table 4]

【0027】[0027]

【表5】 [Table 5]

【0028】3)CF−1株は、腐朽した木材より分離
した10℃前後の低温域でセルロース分解能を有する新規
微生物である。本菌株の特徴は表6、7の通りであり、
形態等の特徴から近縁種としてPenicillium glabrumが
あげられるが、糖の資化性の一部が異なり、したがっ
て、この菌株を新種相当と認定した。そして、この菌株
をPenicillium sp.CF−1とした。この菌株は工業技
術院生命工学工業技術研究所にFERM P-16479として寄
託している。
3) The strain CF-1 is a novel microorganism having a cellulose decomposing ability at a low temperature of about 10 ° C., which is isolated from decayed wood. The characteristics of this strain are as shown in Tables 6 and 7,
Penicillium glabrum is a closely related species due to its morphological characteristics and the like, but a part of the assimilation of sugar is different. Therefore, this strain was identified as a new species. This strain was designated as Penicillium sp. CF-1. This strain has been deposited with the National Institute of Bioscience and Biotechnology at the National Institute of Advanced Industrial Science and Technology as FERM P-16479.

【0029】[0029]

【表6】 [Table 6]

【0030】[0030]

【表7】 [Table 7]

【0031】4)LF−3株は、土壌より分離した30℃
前後の中温域でリグニン分解能を有する新規微生物であ
る。本菌株の特徴は表8、9の通りであり、形態等の特
徴から近縁種としAspergillus nidulansがあげられる
が、糖の資化性の一部が異なり、したがって、この菌株
を新種相当と認定した。そして、この菌株をAspergillu
ssp.LF−3とした。この菌株は工業技術院生命工学工
業技術研究所にFERM P-16482として寄託している。
4) The LF-3 strain was isolated from soil at 30 ° C.
It is a new microorganism that has lignin degradability in the middle temperature range before and after. The characteristics of this strain are as shown in Tables 8 and 9. Aspergillus nidulans is a closely related species based on the characteristics of the morphology, etc., but some of the assimilation of sugar is different. Therefore, this strain is recognized as equivalent to a new species. did. Then, this strain is called Aspergillu
ssp.LF-3. This strain has been deposited with the National Institute of Advanced Industrial Science and Technology as a FERM P-16482.

【0032】[0032]

【表8】 [Table 8]

【0033】[0033]

【表9】 [Table 9]

【0034】5)FS−26株は、泥炭より分離した10
℃〜30℃の低中温域でセルロース分解能を有する新規微
生物である。本菌株の特徴は表10、11の通りであ
り、形態等の特徴から近縁種としPenicillium funicul
osumがあげられるが、糖の資化性の一部が異なり、した
がって、この菌株を新種相当と認定した。そして、この
菌株をPenicillium sp.FS−26とした。この菌株は
工業技術院生命工学工業技術研究所にFERM P-16480とし
て寄託している。
5) The FS-26 strain was isolated from peat.
It is a novel microorganism that has the ability to degrade cellulose in the low to medium temperature range of ℃ to 30 ℃. The characteristics of this strain are as shown in Tables 10 and 11, and from the characteristics of morphology and the like, it was determined to be a closely related species and Penicillium funicul
osum, but some of the assimilation properties of the sugars were different, so this strain was identified as equivalent to a new species. This strain was named Penicillium sp. FS-26. This strain has been deposited as FERM P-16480 with the National Institute of Bioscience and Human Technology.

【0035】[0035]

【表10】 [Table 10]

【0036】[0036]

【表11】 [Table 11]

【0037】6)FS−29株は、北海道美唄市の泥炭
より分離した10℃〜30℃の低中温域でセルロース分解能
を有する新規微生物である。本菌株の特徴は表12、1
3の通りであり、形態等の特徴から近縁種としPenicill
ium glabrumがあげられるが、糖の資化性の一部が異な
り、したがって、この菌株を新種相当と認定した。そし
て、この菌株をPenicillium sp.FS−29とした。こ
の菌株は工業技術院生命工学工業技術研究所にFERM P-
16481として寄託している。
6) The FS-29 strain is a novel microorganism having cellulolytic ability at a low to medium temperature range of 10 ° C. to 30 ° C. isolated from peat in Bibai City, Hokkaido. The characteristics of this strain are shown in Tables 12 and 1.
As shown in Fig. 3, Penicill is considered to be a closely related species due to its morphological characteristics.
ium glabrum, but with some differences in the assimilation of sugars. Therefore, this strain was identified as a new species equivalent. This strain was named Penicillium sp. FS-29. This strain was sent to FERM P-
Deposited as 16481.

【0038】[0038]

【表12】 [Table 12]

【0039】[0039]

【表13】 [Table 13]

【0040】7)FS−35は、北海道サロベツ泥炭よ
り分離した30℃前後の中温域でリグニン分解能を有する
新規微生物である。本菌株の特徴は表14、15の通り
であり、形態等の特徴から近縁種としてAspergillus te
rreusがあげられるが、糖の資化性の一部が異なり、し
たがって、この菌株を新種相当と認定した。そして、こ
の菌株をAspergillus sp.FS−35とした。この菌株
は工業技術院生命工学工業技術研究所にFERM P-16483
として寄託している。
7) FS-35 is a novel microorganism having a lignin degrading ability at a medium temperature range of about 30 ° C. isolated from Hokkaido Sarobetsu peat. The characteristics of this strain are as shown in Tables 14 and 15. Aspergillus te
rreus, but some of the sugar assimilation properties were different. Therefore, this strain was identified as a new species. This strain was named Aspergillus sp. FS-35. This strain was transferred to FERM P-16483 by the National Institute of Biotechnology and Industrial Technology.
Has been deposited.

【0041】[0041]

【表14】 [Table 14]

【0042】[0042]

【表15】 [Table 15]

【0043】8)Bacillus sp.BS-1SMCP IIIは特開平5-
91869号公報に記載の通り根圏土壌より分離した菌株を
ニトロソグアニジン処理して得られたクロラムフェニコ
ール耐性を有するもので30℃前後の中温域でセルロース
分解能を有する微生物である。そして、この菌株は工業
技術院生命工学工業技術研究所にFERM P-12516として
寄託されている。また、その菌学的性質は次の通りであ
る。
8) Bacillus sp. BS-1SMCP III is disclosed in
As described in JP 91869, chloramphenicol-resistant microorganisms obtained by treating a strain isolated from rhizosphere soil with nitrosoguanidine are microorganisms having a cellulose-degrading ability at a medium temperature range of about 30 ° C. This strain has been deposited as FERM P-12516 with the National Institute of Biotechnology and Industrial Technology. The mycological properties are as follows.

【0044】[0044]

【表16】 [Table 16]

【0045】9)本発明の芝のフェアリーリング病の防
除剤は新規微生物CF−1、CF−3、FS−26、F
S−29、FS−35、LB−5、LB−31とBS-1SM
CP IIIの少なくとも一種以上を培養資材で培養すること
により調製する。
9) The novel agent for controlling turf fairy ring disease of the present invention is a novel microorganism CF-1, CF-3, FS-26, F
S-29, FS-35, LB-5, LB-31 and BS-1SM
It is prepared by culturing at least one or more of CP III with a culture material.

【0046】この防除剤はそのままでも用いられるが、
適当な個体担体、液体担体、乳化分散剤などを用いて、
粒剤、粉剤、錠剤、乳剤、水和剤等の任意の形状で使用
できる。この際、微生物の培養物の使用量は担体に対し
て0.1〜50%である。また、この防除剤は無機肥料、有
機肥料、除草剤等と共に使用することができる。
Although this controlling agent can be used as it is,
Using a suitable solid carrier, liquid carrier, emulsifying dispersant, etc.,
It can be used in any form such as granules, powders, tablets, emulsions and wettable powders. At this time, the used amount of the culture of the microorganism is 0.1 to 50% based on the carrier. The control agent can be used together with an inorganic fertilizer, an organic fertilizer, a herbicide and the like.

【0047】この防除剤のゴルフ場等の芝草への使用量
は、芝草1m2あたり1〜1000gが好ましい。
[0047] The amount of the turf of golf courses and the like of the control agent, turf grass 1m 2 per 1~1000g is preferable.

【0048】[0048]

【実施例】以下、選抜した微生物を用いて製造した培養
物を実施例により詳細に説明するが、本発明の範囲はこ
れらの実施例に限定されるものではない。
EXAMPLES Hereinafter, cultures produced by using selected microorganisms will be described in more detail with reference to Examples, but the scope of the present invention is not limited to these Examples.

【0049】〔実施例1〕本発明に関わる新規微生物C
F−1、CF−3、FS−26、FS−29、FS−3
5、LB−5、LB−31とBS-1SMCP IIIを各々PD液
体培地(ポテト抽出液20mL、グルコース20g、蒸留水100
0mL)を用いて、30℃で7日間振盪を行った。この培養
液625mlを等量混合した混合培養液5Lを水道水25Lへ加え
た後、培養資材100kg(コメヌカ51kg、蒸製骨粉10kg、
バーミキュライト28kg、木炭10kg、硫酸第一鉄1kg)へ
添加混合した。
[Example 1] Novel microorganism C related to the present invention
F-1, CF-3, FS-26, FS-29, FS-3
5, LB-5, LB-31 and BS-1SMCP III were each added to a PD liquid medium (potato extract 20 mL, glucose 20 g, distilled water 100
(0 mL) at 30 ° C. for 7 days. After adding 5 L of mixed culture solution obtained by mixing 625 ml of this culture solution to 25 L of tap water, 100 kg of culture material (51 kg of rice bran, 10 kg of steamed bone meal,
Vermiculite 28 kg, charcoal 10 kg, ferrous sulfate 1 kg).

【0050】この培養資材を厚さ10cmに堆積し、発酵温
度が40℃を越えないように適時切り返しを行い、添加微
生物を増殖させた。その後、この培養資材を水分が10%
になるまで自然乾燥させた。
This culture material was deposited to a thickness of 10 cm, and cut back as appropriate so that the fermentation temperature did not exceed 40 ° C., and the added microorganism was grown. After that, the culture material is
It was air-dried until it became.

【0051】〔試験例〕以下に、実施例1で製造した試
験品を用いた試験例を示す。
[Test Example] A test example using the test product manufactured in Example 1 is shown below.

【0052】〔試験例1〕イナワラ堆肥分解試験 〔試験区〕 [Test Example 1] Decomposition test of rice straw compost [Test plot]

【0053】[試験方法]200lポリ容器へ生わら12kg
を入れ上記試験区を設けて堆肥化試験を行った。試験開
始後16日と45日後に切り返しを行う。
[Test method] Straw 12kg in a 200l plastic container
And a composting test was conducted in the test plot. The test is reverted 16 days and 45 days after the test starts.

【0054】[試験結果]結果については図1に示した
通り、イナワラの炭素分解率は堆積初期から試験品を添
加した区で大きく、特に試験品+尿素区では36日経過し
た頃には30%以上になり、72日目では50%を超えた。試
験品単独区は次に分解率が高かった。
[Test Results] As shown in FIG. 1, the carbon decomposition rate of rice straw was large in the section where the test sample was added from the initial stage of deposition, and in particular, in the test sample + urea section, it was 30 after 36 days. % And over 50% on day 72. The test sample alone had the next highest decomposition rate.

【0055】〔試験例2〕 水田圃場での分解試験 〔試験区〕 [Test Example 2] Decomposition test in paddy field [Test plot]

【0056】[試験方法] 10月12日資材処理、11月16日、12月22日、
翌年4月12日 イナワラ採取 [試験結果]図2に示した通り、イナワラの分解は資材
施用初期から試験品添加区で高く、その後もこの傾向が
継続し、特に12月〜4月の低温期での分解も優れてい
た。
[Test Method] Material treatment on October 12, November 16, December 22,
April 12 of the following year Collecting rice straw [Test results] As shown in Fig. 2, degradation of rice straw was high in the test sample addition zone from the initial stage of material application, and this tendency continued thereafter, especially in the low temperature season from December to April. The decomposition was excellent.

【0057】〔試験例3〕 キノコ廃オガ分解試験 [試験方法]メッシュバッグへ廃オガ(エノキタケ等菌茸類
栽培残渣)と牛ふん尿および試験品を表1の割合で混合
して詰め込み、雨よけシートを被覆して野外堆積を行っ
た。
Test Example 3 Mushroom Waste Oga Decomposition Test [Test Method] Waste ogre (residue for cultivation of fungi and mushrooms such as enokitake mushrooms), cow manure and test products were mixed and packed in a mesh bag at the ratio shown in Table 1, and the sheet was protected from rain. For field deposition.

【0058】5月30日 堆積開始、7月18日 中間
採取、8月29日 最終採取 〔試験区〕
May 30 Deposition started, July 18 Interim sampling, August 29 Final sampling [Test plot]

【0059】[試験結果]堆積翌日より品温は急激に上
昇し、ほぼ10日間にわたり50℃以上を維持した。その後
は30℃前後で外気温より高く推移した。試験区(試験品
添加)は全期間通じて品温が高めに推移し、特に堆積初
期の温度差は大きく、分解促進効果が高かった。(図
3) 化学性は炭素が処理区で約13%程度低く推移しており、
微生物性についても試験品由来による糸状菌数が非常に
多く推移した。(表17)こうしたことから、試験品の
添加は廃オガの早期堆肥化に有効であった。
[Test Results] The temperature of the product rapidly increased from the day after the deposition, and was maintained at 50 ° C. or higher for almost 10 days. After that, it was higher than the outside temperature at around 30 ° C. In the test plot (addition of test product), the product temperature remained high throughout the entire period, and the temperature difference in the initial stage of deposition was particularly large, and the decomposition promoting effect was high. (Fig. 3) As for the chemical properties, carbon has been reduced by about 13% in the treated area.
Regarding the microbial properties, the number of filamentous fungi derived from the test products was very large. (Table 17) From the above, the addition of the test product was effective for the early composting of waste sawdust.

【0060】[0060]

【表17】 [Table 17]

【0061】〔試験例4〕 イナワラ堆肥化試験 〔試験区〕 [Test Example 4] Rice straw composting test [Test plot]

【0062】[試験方法]1区水田7.5ha分のイナワラ
を使用して、上記処理を行い野積みした。
[Test Method] The above treatment was carried out using rice straw for 7.5 ha of paddy field in one ward and piled up.

【0063】11月15日資材処理、12月24日、翌
年4月25日 イナワラ採取 [試験結果]炭素率は堆積1か月後の無処理区で54.4に
比較して、試験品+尿素区では19.3と1/3程度の数値
となった。5か月後でも分解の程度に変化はなく、試験
品+尿素区<試験品区<尿素区<無処理区の順に炭素率
は低下した(図4)。
Material treatment on November 15, December 24, April 25 of the next year Inawara collection [Results of test] The carbon ratio was 1 month after deposition, compared with 54.4 in the untreated section and the test article + urea section. Then it was 19.3, about 1/3 of the figure. Even after 5 months, the degree of decomposition did not change, and the carbon ratio decreased in the order of test article + urea section <test article section <urea section <untreated section (FIG. 4).

【0064】各処理を行った堆肥を土壌に施用してえん
麦を栽培した結果、無処理区で生育抑制を若干示した以
外は障害が認められなかった。試験品+尿素区のえん麦
の生育は著しく向上した(図5)。
As a result of applying the compost subjected to each treatment to the soil and cultivating oats, no obstacle was observed except that the growth was suppressed slightly in the untreated plot. The growth of oats in the test product + urea group was significantly improved (FIG. 5).

【0065】〔試験例5〕 フェアリーリング防除試験 [試験方法]ゴルフ場グリーン周りのフェアリーリング
病が発生した場所へ、試験品を500g/m2となるように散
布し、2ヶ月後に同じ場所へ200g/m2 となるように散布
した。
[Test Example 5] Fairy ring control test [Test method] A test product was sprayed at a rate of 500 g / m 2 around a golf course green at a place where fairy ring disease occurred. It was sprayed to 200 g / m 2 .

【0066】[試験結果]試験品を散布した場所では、
フェアリーリングの発生が抑制され、芝草が正常に生育
した(図6、図7)。
[Test Results] At the place where the test product was sprayed,
The occurrence of fairy ring was suppressed, and the lawn grass grew normally (FIGS. 6 and 7).

【0067】〔実施例2〕本発明に関わる新規微生物C
F−1、FS−35、LB−31、BS-1SMCP IIIを各々
PD液体培地(ポテト抽出液20mL、グルコース20g、蒸
留水1000mL)を用いて、30℃で7日間振盪を行った。こ
の培養液1250mlを等量混合した混合培養液5Lを水道水25
Lへ加えた後、培養資材100kg(コメヌカ51kg、蒸製骨粉
10kg、バーミキュライト28kg、木炭10kg、硫酸第一鉄1k
g)へ添加混合した。
[Example 2] Novel microorganism C related to the present invention
F-1, FS-35, LB-31, and BS-1 SMCP III were shaken at 30 ° C. for 7 days using PD liquid medium (potato extract 20 mL, glucose 20 g, distilled water 1000 mL). 5 L of a mixed culture obtained by mixing 1250 ml of this culture with an equal volume
After adding to L, 100 kg of culture material (51 kg of rice bran, steamed bone meal)
10kg, vermiculite 28kg, charcoal 10kg, ferrous sulfate 1k
g).

【0068】この培養資材を厚さ10cmに堆積し、発酵温
度が40℃を越えないように適時切り返しを行い、添加微
生物を増殖させた。その後、この培養資材を水分が10%
になるまで自然乾燥させた。
This culture material was deposited to a thickness of 10 cm, and cut back as appropriate so that the fermentation temperature did not exceed 40 ° C., and the added microorganism was grown. After that, the culture material is
It was air-dried until it became.

【0069】〔試験例〕以下に、実施例2で製造した試
験品を用いた試験例を示す。
[Test Example] A test example using the test product manufactured in Example 2 is shown below.

【0070】〔試験例1〕 水田圃場での分解試験 〔試験区〕 [Test Example 1] Decomposition test in paddy field [Test plot]

【0071】[試験方法]10月30日資材処理、翌年
4月10日 イナワラ採取 [試験結果]表18に示した通り、イナワラの分解を示
す炭素含量が試験区で低く、よってC/Nが最も低かっ
た。
[Test Method] Material treatment on October 30 and collection of rice straw on April 10 of the following year [Test results] As shown in Table 18, the carbon content indicating degradation of rice straw was low in the test plot, and thus C / N was low. It was the lowest.

【0072】[0072]

【表18】 [Table 18]

【0073】〔試験例2〕 刈り芝の分解試験 〔試験区〕 [Test Example 2] Decomposition test of cut grass [Test plot]

【0074】[試験方法]1/2000aワグネルポットに刈
り芝2kgと資材20gを混合し、水を加えて56日間堆
積し、芝の窒素、炭素および微生物性を測定した。
[Test method] 2 kg of cut turf and 20 g of material were mixed in a 1 / 2000a Wagner pot, water was added thereto and the turf was deposited for 56 days, and nitrogen, carbon and microbial properties of the turf were measured.

【0075】[試験結果]表19に示した通り、刈り芝
の分解を示す炭素含量が試験区で低く、分解活性を示す
微生物数も試験区が非常に多かった。
[Test Results] As shown in Table 19, the carbon content indicating the decomposition of cut grass was low in the test plot, and the number of microorganisms exhibiting the decomposition activity was very large in the test plot.

【0076】[0076]

【表19】 [Table 19]

【0077】[0077]

【発明の効果】本発明によればオガクズ、バークなどの
木質物、イナワラ、ムギワラなどのワラ類、モミガラ、
フスマなどの穀物残さ、茶・果樹等の剪定枝、野菜等収
穫残さ、ゴルフ場などよりでる刈り芝、家庭から排泄さ
れる生ゴミ、家畜排泄物、食品産業廃棄物等の難分解性
有機物の早期分解が可能となり、良質な堆肥ができる。
また、本発明によりフェアリーリング病を防除すること
ができる。
According to the present invention, woody materials such as sawdust and bark, straws such as rice straw and wheat straw, Japanese peach,
It is used to remove hard-to-decompose organic matter such as grain residues such as bran, pruned branches such as tea and fruit trees, harvest residues such as vegetables, cut grass from golf courses, raw garbage excreted from homes, livestock excrement, and food industry waste. Early decomposition is possible, and high quality compost can be obtained.
Further, the present invention can control fairy ring disease.

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

【図1】堆積イナワラの炭素分解率を示す図。FIG. 1 is a view showing the carbon decomposition rate of deposited rice straw.

【図2】試験期間中におけるイナワラの炭素分解率を示
す図。
FIG. 2 is a view showing the carbon decomposition rate of rice straw during the test period.

【図3】廃オガ堆積に伴う品温の推移を示す図。FIG. 3 is a diagram showing a change in product temperature accompanying the accumulation of waste sawdust.

【図4】堆積イナワラの炭素率を示す図。FIG. 4 is a view showing a carbon ratio of deposited rice straw.

【図5】堆積イナワラによるえん麦栽培試験結果の示す
図。
FIG. 5 is a view showing the results of oat cultivation test using deposited rice straw.

【図6】フェアリーリング病により芝が枯れた状態を示
す写真。
FIG. 6 is a photograph showing turf withered due to fairy ring disease.

【図7】試験品施用によりフェアリーリング病の抑制を
示す写真。
FIG. 7 is a photograph showing suppression of fairy ring disease by application of a test article.

───────────────────────────────────────────────────── フロントページの続き (51)Int.Cl.6 識別記号 FI C12N 1/16 C12N 1/16 G D // C05F 11/08 C05F 11/08 (C12N 1/20 C12R 1:07) (C12N 1/14 C12R 1:80) (C12N 1/14 C12R 1:66) (C12N 1/16 C12R 1:645) (72)発明者 赤澤 貴徳 茨城県土浦市並木5丁目5511番地 片倉チ ッカリン株式会社筑波総合研究所内──────────────────────────────────────────────────の Continued on the front page (51) Int.Cl. 6 Identification symbol FI C12N 1/16 C12N 1/16 GD // C05F 11/08 C05F 11/08 (C12N 1/20 C12R 1:07) (C12N 1/14 C12R 1:80) (C12N 1/14 C12R 1:66) (C12N 1/16 C12R 1: 645) (72) Takanori Akazawa 5-551 Namiki, Tsuchiura-shi, Ibaraki Pref. Chika Katakura Tsukuba Co., Ltd. Within the Research Institute

Claims (10)

【特許請求の範囲】[Claims] 【請求項1】 セルロース分解能を有するペニシリウム
・エスピー(Penicillium sp.)CF−1、ペニシリウ
ム・エスピー(Penicillium sp.)FS−26又はペニ
シリウム・エスピー(Penicillium sp.)FS−29か
ら選ぶ微生物。
1. A microorganism selected from Penicillium sp. CF-1, which has a cellulose decomposing ability, Penicillium sp. FS-26 or Penicillium sp. FS-29.
【請求項2】 リグニン分解能を有するバチルス・エス
ピー(Bacillus sp.)LB−5。
2. Bacillus sp. LB-5 having lignin decomposability.
【請求項3】 リグニン分解能を有するデバリオミセス
・エスピー(Debaryomyces sp.)LB−31。
3. Debaryomyces sp. LB-31 having lignin degradability.
【請求項4】 リグニン分解能を有するアスペルギルス
・エスピー(Aspergillus sp.)LF−3又はアスペル
ギルス・エスピー(Aspergillus sp.)FS−35。
4. Aspergillus sp. LF-3 or Aspergillus sp. FS-35 having lignin decomposability.
【請求項5】 請求項1〜4記載の微生物の少なくとも
一種と培養資材とを含む培養資材組成物。
5. A culture material composition comprising at least one of the microorganisms according to claim 1 and a culture material.
【請求項6】 請求項1〜4記載の微生物の少なくとも
一種とバチルス・エスピー(Bacillus sp.)BS-1SMCP I
IIと培養資材とを含む培養資材組成物。
6. Bacillus sp. BS-1SMCP I and at least one of the microorganisms according to claims 1 to 4.
A culture material composition comprising II and a culture material.
【請求項7】 前記培養資材がバーミキュライト、ゼオ
ライト、パーライト、モンモリロナイトなどの無機質鉱
物、硫酸アンモニウム、塩化アンモニウム、硝酸アンモ
ニウム、過燐酸石灰、リン酸アンモニウム、硫酸カリウ
ム、塩化カリウムなどの化成肥料、硫酸第一鉄、塩化第
一鉄などの鉄化合物、ケイソウ土、焼成ケイソウ土、サ
ンゴ砂、木炭粉末、活性炭などの多孔質物、ナタネ油か
す、コメヌカ油かす、ヒマシ油かす、ダイズ油かすなど
の植物質肥料、蒸製骨粉、生骨粉、脱膠骨粉、肉骨粉、
肉かす、魚かす、フェザーミール、蒸製毛粉、カニガ
ラ、皮粉、さなぎかすなどの動物質肥料およびこれらの
混合物からなる群より選抜されたものであることを特徴
とする請求項5および6記載の培養資材組成物。
7. The culture material is an inorganic mineral such as vermiculite, zeolite, perlite or montmorillonite; a chemical fertilizer such as ammonium sulfate, ammonium chloride, ammonium nitrate, lime superphosphate, ammonium phosphate, potassium sulfate or potassium chloride; ferrous sulfate. , Iron compounds such as ferrous chloride, diatomaceous earth, calcined diatomaceous earth, coral sand, charcoal powder, porous material such as activated carbon, rapeseed oil residue, rice bran oil residue, castor oil residue, plant fertilizer such as soybean oil residue, Steamed bone meal, raw bone meal, deglutinated bone meal, meat-and-bone meal,
7. A material selected from the group consisting of animal material fertilizers such as meat meal, fish meal, feather meal, steamed flour, crab, husk, pupa and the like, and a mixture thereof. Culture material composition.
【請求項8】 バーミキュライト、ゼオライト、パーラ
イト、モンモリロナイトなどの無機質鉱物、硫酸アンモ
ニウム、塩化アンモニウム、硝酸アンモニウム、過燐酸
石灰、リン酸アンモニウム、硫酸カリウム、塩化カリウ
ムなどの化成肥料、硫酸第一鉄、塩化第一鉄などの鉄化
合物、ケイソウ土、焼成ケイソウ土、サンゴ砂、木炭粉
末、活性炭などの多孔質物、ナタネ油かす、コメヌカ油
かす、ヒマシ油かす、ダイズ油かすなどの植物質肥料、
蒸製骨粉、生骨粉、脱膠骨粉、肉骨粉、肉かす、魚か
す、フェザーミール、蒸製毛粉、カニガラ、皮粉、さな
ぎかすなどの動物質肥料およびこれらの混合物からなる
群より選抜された培養資材中で請求項1〜4記載の微生
物の少なくとも一種を培養してなることを特徴とする培
養資材組成物。
8. Mineral minerals such as vermiculite, zeolite, perlite and montmorillonite; chemical fertilizers such as ammonium sulfate, ammonium chloride, ammonium nitrate, lime superphosphate, ammonium phosphate, potassium sulfate and potassium chloride; ferrous sulfate; Iron compounds such as iron, diatomaceous earth, calcined diatomaceous earth, coral sand, charcoal powder, porous materials such as activated carbon, rapeseed oil residue, rice bran oil residue, castor oil residue, plant fertilizers such as soybean oil residue,
A culture selected from the group consisting of animal and animal fertilizers such as steamed bone meal, raw bone meal, deglutinated bone meal, meat-and-bone meal, meat meal, fish cake, feather meal, steamed hair meal, crab, skin powder, and pupa meal, and mixtures thereof. A culture material composition obtained by culturing at least one of the microorganisms according to claims 1 to 4 in the material.
【請求項9】 バーミキュライト、ゼオライト、パーラ
イト、モンモリロナイトなどの無機質鉱物、硫酸アンモ
ニウム、塩化アンモニウム、硝酸アンモニウム、過燐酸
石灰、リン酸アンモニウム、硫酸カリウム、塩化カリウ
ムなどの化成肥料、硫酸第一鉄、塩化第一鉄などの鉄化
合物、ケイソウ土、焼成ケイソウ土、サンゴ砂、木炭粉
末、活性炭などの多孔質物、ナタネ油かす、コメヌカ油
かす、ヒマシ油かす、ダイズ油かすなどの植物質肥料、
蒸製骨粉、生骨粉、脱膠骨粉、肉骨粉、肉かす、魚か
す、フェザーミール、蒸製毛粉、カニガラ、皮粉、さな
ぎかすなどの動物質肥料およびこれらの混合物からなる
群より選抜された培養資材中で請求項1〜4記載の微生
物の少なくとも一種とバチルス・エスピー(Bacillus s
p.)BS-1SMCP IIIを培養してなることを特徴とする培養
資材組成物。
9. Mineral minerals such as vermiculite, zeolite, perlite and montmorillonite; chemical fertilizers such as ammonium sulfate, ammonium chloride, ammonium nitrate, lime superphosphate, ammonium phosphate, potassium sulfate and potassium chloride; ferrous sulfate; Iron compounds such as iron, diatomaceous earth, calcined diatomaceous earth, coral sand, charcoal powder, porous materials such as activated carbon, rapeseed oil residue, rice bran oil residue, castor oil residue, plant fertilizers such as soybean oil residue,
A culture selected from the group consisting of animal and animal fertilizers such as steamed bone meal, raw bone meal, deglutinated bone meal, meat-and-bone meal, meat meal, fish cake, feather meal, steamed hair meal, crab, skin powder, and pupa meal, and mixtures thereof. Bacillus sp. And at least one of the microorganisms according to claims 1 to 4 in the material.
p.) A culture material composition obtained by culturing BS-1SMCP III.
【請求項10】 請求項5〜9記載の培養資材組成物を
用いることを特徴とする芝のフェアリーリング病の防除
方法。
10. A method for controlling turf fairy ring disease, comprising using the culture material composition according to claim 5.
JP02953798A 1998-02-12 1998-02-12 Organic matter-degrading microorganism, culture material composition thereof, and method for controlling fairy ring disease using the culture material composition Expired - Lifetime JP3283228B2 (en)

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