JPS5829273B2 - Fertilizer manufacturing method - Google Patents

Fertilizer manufacturing method

Info

Publication number
JPS5829273B2
JPS5829273B2 JP54142638A JP14263879A JPS5829273B2 JP S5829273 B2 JPS5829273 B2 JP S5829273B2 JP 54142638 A JP54142638 A JP 54142638A JP 14263879 A JP14263879 A JP 14263879A JP S5829273 B2 JPS5829273 B2 JP S5829273B2
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JP
Japan
Prior art keywords
bacteria
fermentation
slag
temperature
mixed
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
Application number
JP54142638A
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Japanese (ja)
Other versions
JPS5669291A (en
Inventor
義芳 門馬
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Individual
Original Assignee
Individual
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Filing date
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Application filed by Individual filed Critical Individual
Priority to JP54142638A priority Critical patent/JPS5829273B2/en
Publication of JPS5669291A publication Critical patent/JPS5669291A/en
Publication of JPS5829273B2 publication Critical patent/JPS5829273B2/en
Expired 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

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  • Fertilizers (AREA)

Description

【発明の詳細な説明】 本発明は動植物性堆肥材料に鉱滓(slag)の適量を
混合したものを基本とし、これに燻炭、泥炭、汚泥、糞
尿の中から選ばれた1種又はそれ以上を混合し、これに
セルローズ分解菌、糸状菌、硝化細菌、硫黄細菌、空気
窒素固定菌、根粒菌、放線菌を加え、酵母、シュウトモ
ナス属の菌、高温性細菌、高温性放線菌から選ばれた一
種又はそれ以上を加え高温醗酵を行うことを特徴とする
肥料製造法である。
DETAILED DESCRIPTION OF THE INVENTION The present invention is based on a mixture of animal and plant compost materials with an appropriate amount of slag, and one or more selected from smoky charcoal, peat, sludge, and excrement. To this, cellulose-degrading bacteria, filamentous fungi, nitrifying bacteria, sulfur bacteria, air nitrogen-fixing bacteria, rhizobia, and actinomycetes are added, and the mixture is selected from yeast, Shutomonas bacteria, thermophilic bacteria, and thermophilic actinomycetes. This is a fertilizer production method characterized by adding one or more of the above ingredients and carrying out high temperature fermentation.

本発明は上記の様に動植物性堆肥材料に鉱滓を混合した
ものを基材とし、これに燻炭、泥炭、汚泥各種糞尿(家
畜の糞尿、鶏糞等の家属の糞を含む)の1種又はそれ以
上を混合したものに上記の微生物又はそれ等の微生物を
含む醗酵促進材を加えて醗酵を行うことを特徴とする肥
料製造法である。
The present invention uses as a base material a mixture of animal and plant compost materials with mineral slag, which is combined with one of smoky charcoal, peat, sludge, various manures (including domestic animal manure, chicken manure, etc.), or This is a fertilizer production method characterized by adding the above-mentioned microorganisms or a fermentation promoter containing such microorganisms to a mixture of more than 100% of the above-mentioned microorganisms, and carrying out fermentation.

本発明に使用する鉱滓は、高温発酵の過程で微粒化され
るとともに、その成分が可溶化され、後記のように微量
要素を植物に供給する。
The slag used in the present invention is atomized in the process of high-temperature fermentation, and its components are solubilized to supply trace elements to plants as described below.

鉱滓中には酸化カルシウム(Cab) 、酸化マグネシ
ウム(MgO)、酸化マンガン(Mn O)、酸化第二
鉄(F e 203 )、酸化アルミニウム(A120
3)、酸化チタニウム(T i O2) 、五酸化燐(
P2O3)、多量の無水硅酸(Sin2)等の微量要素
を含んでおり、又有害な重金属を含んでおらず、アルカ
リ性を示している。
The slag contains calcium oxide (Cab), magnesium oxide (MgO), manganese oxide (MnO), ferric oxide (F e 203 ), and aluminum oxide (A120).
3), titanium oxide (T i O2), phosphorus pentoxide (
It contains trace elements such as P2O3) and a large amount of silicic anhydride (Sin2), does not contain harmful heavy metals, and is alkaline.

これ等の成分中、鉄は光合成に関与する葉緑素、葉緑体
の生成に必要であり、又根部にも茎葉部の5〜10倍も
含まれるので、適当の鉄分の施用は植物の生育に着効を
奏する。
Among these components, iron is necessary for the production of chlorophyll and chloroplasts involved in photosynthesis, and the roots contain 5 to 10 times more than the stems and leaves, so applying an appropriate amount of iron is necessary for plant growth. It has a great effect.

マンガンは鉄と同様に葉緑素の生成、従って植物の光合
成に必要である外、植物の呼吸作用、窒素の同化(硝酸
の後段に於ける還元)、植物体中のビタミンCの生成等
に役立つ。
Manganese, like iron, is necessary for the production of chlorophyll and therefore for photosynthesis in plants, and is also useful for plant respiration, nitrogen assimilation (reduction of nitric acid in the latter stage), and the production of vitamin C in plants.

石灰は堆肥材料及び土壌の酸性を中和する外、人糞尿、
干拓地等に於ける海水等に由来するナトリウムイオンに
より土壌が単粒構造になり、土壌の理学的性質が慈愛す
るが石灰の施用により土壌中のナトリウムイオンはカル
シウムイオンで置換され堆肥及び土壌コロイドは脱水凝
固し、団粒化しやすくなる。
Lime neutralizes the acidity of compost materials and soil, as well as human waste and urine.
Sodium ions derived from seawater in reclaimed land, etc., cause the soil to have a single-grain structure, and the physical properties of the soil are favorable, but by applying lime, the sodium ions in the soil are replaced with calcium ions, resulting in compost and soil colloids. dehydrates and coagulates, making it easier to aggregate.

硅酸は特に稲科の植物体に多量に含まれ、稲のイモチ病
予防並に秋落ち予防に着効を奏する。
Silicic acid is particularly contained in large amounts in plants of the rice family, and is effective in preventing rice blast disease and autumn drop.

又硅酸は植物の光合成及び根の酸化作用を増大する。Silicic acid also increases plant photosynthesis and root oxidation.

酸化マグネシウムは植物の硅酸の吸収を助は植物体を強
固にし、茎葉の多汁化徒長及び柔軟化を防ぎ稲のイモチ
病に対する抵抗性を強める。
Magnesium oxide helps plants absorb silicic acid, strengthens the plant body, prevents succulence, elongation and softening of stems and leaves, and strengthens rice's resistance to blast disease.

又或種の酵素特に燐酸代謝に関係がある酵素に深い関*
*係がある。
Also, there is a deep connection with certain enzymes, especially those related to phosphate metabolism.
*There is a person in charge.

酸化チタニウムは豆科植物の根粒の着生数を増化し、窒
素固定能を増加せしむる。
Titanium oxide increases the number of root nodules of leguminous plants and increases their nitrogen fixing ability.

尚高炉鉱滓の成分(%)を例示すると次の通りである。Examples of the components (%) of the blast furnace slag are as follows.

さらに、本発明において使用する鉱滓は水分調整材の作
用を兼有し、家畜糞尿に含まれる水分を吸収する。
Furthermore, the slag used in the present invention also functions as a moisture regulating material and absorbs moisture contained in livestock manure.

このため、鶏糞、牛糞はもとより、水分が極めて多く(
90%以上)従来使用が困難視されていた豚糞の肥料化
も容易にした。
For this reason, not only chicken manure and cow manure, but also extremely high water content (
(over 90%) It has also become easier to convert pig manure into fertilizer, which was considered difficult to use in the past.

また、これら糞尿の水分除去のために従来行われていこ
火力乾燥を不要とし、重油経費を節約するとともに、こ
れによる大気汚染、悪臭をなくした。
In addition, the conventional method of drying using electric power to remove moisture from these excreta is no longer necessary, saving heavy oil costs and eliminating air pollution and bad odors caused by this.

以上の堆肥材料に上記の微生物を混合し、攪拌混合し、
醗酵を行う。
Mix the above microorganisms with the above compost material, stir and mix,
Perform fermentation.

混合する微生物を例示するとCe l lu lomo
nasFlavigena (繊維素を分解する)Cl
ostridium Butyricum (窒素固定
菌)、Aspergillis oryzae (米麹
菌)、Nitrosomonas europas (
硝化細菌)、N1trobacter agilis
(硝化細菌)、Th1obacillus thio
parus (硫黄細菌)、Th1obacillus
thiooxidans (硫黄細菌)Azoto
bacter indicum(窒素固定菌)、Azo
tobacter vinlandii(窒素固定菌)
、Thermoactinomyces vulgar
is (好熱性放線菌)、Pseudomonas r
uhlandii(有機栄養細菌の1種)、Rhizo
bium属の菌(根粒菌)である。
Examples of microorganisms to be mixed are Ce l lu lomo
nasFlavigena (decomposes cellulose) Cl
ostridium Butyricum (nitrogen fixing bacteria), Aspergillis oryzae (rice koji mold), Nitrosomonas europas (
nitrifying bacteria), N1trobacter agilis
(nitrifying bacteria), Th1obacillus thio
parus (sulfur bacterium), Th1obacillus
thiooxidans (sulfur bacteria) Azoto
bacter indicum (nitrogen fixing bacteria), Azo
tobacter vinlandii (nitrogen fixing bacteria)
, Thermoactinomyces vulgar
is (thermophilic actinomycetes), Pseudomonas r
uhlandii (a type of organic trophic bacteria), Rhizo
It is a bacterium of the genus Bium (rhizobacteria).

これ等の微生物中、細菌、放線菌、高温性放細菌はポリ
ペプトン1%、肉エキス1%、食塩0.3%、寒天2%
を含むpH7の培地で30’C(但し高温放線菌は55
°C)で培養し、真菌、酵母、カヒは酵母エキス0.3
%、マルツエキス0.3%、ポリペプトン0.5%、グ
リコース1%、クロラムフェニコール0.01%、寒天
2%を含むpH6,0の培地で25℃で培養し、Rhi
zobium属の菌はマニット1%、燐酸2カリ0.0
7%、燐酸1カリ0.03%、硫酸マグネシウム0.0
1%、炭酸石灰0.03%、酵母エキス0.5%、寒天
2%を含むpH7,2の培地で25°Cで培養し、この
培養物を後記実施例記載の泥炭、燻炭、ベントナイト、
蔗糖、骨粉の混合物に1%程度混合したものを堆肥材料
総量の0.1%程度混合し、水分50〜60%程度にな
る様に水分調節し、醗酵を行わしめる。
Among these microorganisms, bacteria, actinomycetes, and thermophilic bacteria contain 1% polypeptone, 1% meat extract, 0.3% salt, and 2% agar.
30'C in a pH 7 medium containing
The fungi, yeast, and kahi were cultured at 0.3 °C) and the yeast extract was
The Rhi
Bacteria of the genus Zobium contain 1% manit and 0.0 dipotassium phosphate.
7%, monopotassium phosphate 0.03%, magnesium sulfate 0.0
1% of lime, 0.03% of lime carbonate, 0.5% of yeast extract, and 2% of agar at 25°C. ,
A mixture of sucrose and bone meal mixed at about 1% is mixed to make up about 0.1% of the total amount of compost material, the water content is adjusted to about 50-60%, and fermentation is carried out.

尚、醗酵初期には全体の温度が60°C〜70℃の高温
を約2週間継続し、真後温度が漸次下降して来るので、
温度が25℃位になったら上記の菌培養物と稀釈材(担
体)の混合物を全体のo、i%又はそれ以下添加し、高
温により死滅した微生物を補給し、全体を切りかえし、
水分調整を行い約30日間で製品を得る。
In addition, in the early stage of fermentation, the overall temperature remains at a high temperature of 60°C to 70°C for about 2 weeks, and the temperature immediately after fermentation gradually decreases.
When the temperature reaches around 25°C, add O, i% or less of the mixture of the above bacterial culture and diluent (carrier) to the total, replenish the microorganisms killed by the high temperature, and switch the whole.
After adjusting the moisture content, the product can be obtained in about 30 days.

醗酵中鉱滓は資料の酸性を中和し、微生物の醗酵に適す
る作用をする外上記各種の鉱物性要素を補給する。
During fermentation, the slag neutralizes the acidity of the material, acts suitable for microbial fermentation, and replenishes the various mineral elements mentioned above.

醗酵中容微生物はその性能に応じ堆肥材料の分解熟成の
作用をし、家畜糞尿等の悪臭を脱臭する。
Depending on their performance, the fermenting microorganisms act to decompose and ripen compost materials, and deodorize foul odors such as livestock manure.

尚堆肥の醗酵中にも植物体中のリクニンは分解され難く
、又微生物により各堆肥材料の分解により生ずる粘質物
は堆肥を土壌に施用した場合上の団粒化を促進し、又土
壌の物理化学性を改良し、土壌中に有用微生物を補給す
る作用があるので、殊に農薬、化学肥料個用により荒廃
し、又土壌微生物の生態系が乱れた土壌の改良に著効を
奏するものである。
Likunin in plants is difficult to decompose even during fermentation of compost, and the mucilage produced by decomposition of each compost material by microorganisms promotes agglomeration when compost is applied to soil, and also affects soil physics. It has the effect of improving chemical properties and replenishing useful microorganisms in the soil, so it is particularly effective in improving soil that has been devastated by the use of pesticides and chemical fertilizers, and where the soil microbial ecosystem has been disturbed. be.

実施例 細砕した製鉄溶鉱炉から排出される鉱滓と細砕した泥炭
と、鶏糞を夫々400kg: 400kg:200kg
の割合に混合したもの1000kgに対し上記の微生物
の培養物を下記の担体に混合したもの1 kyを混合し
、水分が55〜60%になる様に水分調整し、醗酵させ
る。
Example: 400 kg each of crushed slag discharged from a steelmaking blast furnace, crushed peat, and chicken manure: 400 kg: 200 kg
To 1000 kg of the mixture, 1 ky of the above microorganism culture mixed with the following carrier is mixed, the water content is adjusted to 55-60%, and fermentation is carried out.

然る時は資料の温度が70’Cに3〜4日間、60℃前
後が約2週間続く、爾後漸次温度が下降し、30日位で
完熟堆肥を得る。
In such cases, the temperature of the material remains at 70'C for 3 to 4 days, and around 60°C for about 2 weeks, after which the temperature gradually decreases and a fully ripened compost is obtained in about 30 days.

醗酵過程で温度が30℃〜25℃(こなったとき上記微
生物培養物1%を下記の担体99%に混合したものを堆
肥資料に対し1 kg又はそれ以下混合し醗酵を行わし
むれば醗酵初期の高温により死滅又は減少した微生物を
補い醗酵を完了せしむることか出来る。
During the fermentation process, the temperature is between 30°C and 25°C (when the temperature reaches 30°C to 25°C, 1 kg or less of the above microbial culture mixed with 99% of the following carrier is mixed with the compost material and fermentation is completed. It is possible to supplement the microorganisms killed or reduced by the initial high temperature and complete the fermentation.

上記微生物培養物の担体を例示すれば次の通りであり、
これに上記微生物を培地に培養した物1%を混合して使
用する。
Examples of carriers for the above microbial culture are as follows:
This is mixed with 1% of the above microorganism cultured in a medium.

本発明により製造された肥料の成分分析値を例示すれば
次のとおりである。
Examples of component analysis values of the fertilizer produced according to the present invention are as follows.

本発明の肥料製造法は、前記のように相当長期に渉り6
0℃〜70℃の高温発酵を継続するので、50℃前後で
処理する場合と明確に異なり鉱滓成分等の可溶化が著し
く促進される。
As mentioned above, the fertilizer manufacturing method of the present invention can be used for a fairly long period of time.
Since the high temperature fermentation of 0°C to 70°C is continued, the solubilization of slag components etc. is significantly promoted, which is clearly different from the case of processing at around 50°C.

これら鉱滓成分は例え肥料中に存在しても、可溶化しな
い限り植物に吸収されず、肥料としての役割を果さない
Even if these slag components are present in fertilizer, they will not be absorbed by plants unless they are solubilized and will not serve as a fertilizer.

例えば、高炉スラグ中のMgOは5.6〜8.1%であ
るが、可溶化されているのは0.1%にすぎない。
For example, MgO in blast furnace slag is 5.6 to 8.1%, but only 0.1% is solubilized.

ところが本発明の製造法によれば、0.5%が可溶化さ
れ、植物に吸収可能な量は5倍に増加する。
However, according to the production method of the present invention, 0.5% is solubilized, increasing the amount that can be absorbed by plants by five times.

本発明に用いる微生物中に含まれる硝化菌の作用と60
℃〜70℃の高温発酵との相乗作用により、石灰、苦土
、珪酸等の可溶化が促進され、これらは植物根に吸収さ
れ易い状態となる。
Effects of nitrifying bacteria contained in microorganisms used in the present invention and 60
Due to the synergistic effect with high temperature fermentation at a temperature of .degree. C. to 70.degree. C., solubilization of lime, magnesia, silicic acid, etc. is promoted, and these become easily absorbed by plant roots.

また、珪カル肥料との可溶化率の比較は次のとおりであ
る。
In addition, a comparison of the solubilization rate with silica fertilizer is as follows.

さらに、高温発酵の継続により鉱滓が微粉化される。Furthermore, the slag is pulverized by continuing high-temperature fermentation.

これらにより、水田のみならず畑作においても鉱滓含有
肥料の利用が可能となった。
These developments have made it possible to use slag-containing fertilizers not only in paddy fields but also in upland crops.

また、植物に有害な微生物の生育は50℃前後で阻止さ
れ、60℃を越えると死滅するものが多く、高温発酵の
過程でこれらを死滅させる効果を有する。
Furthermore, the growth of microorganisms that are harmful to plants is inhibited at around 50°C, and many of them die when the temperature exceeds 60°C, and it has the effect of killing these microorganisms during the high temperature fermentation process.

本発明に係る肥料の使用は従来肥料に比して50%以上
の増収を実現し、農家には70%を越す増益をもたらす
The use of the fertilizer according to the present invention achieves an increase in yield of more than 50% compared to conventional fertilizers, and provides farmers with an increase in profits of more than 70%.

栽培比較実験の結果は次のとおりである。The results of the comparative cultivation experiment are as follows.

さらに、本発明に係る肥料を施用して収穫した作物(玉
ねぎ)の栄養分析によれば、作物個体中の窒素分は従来
の肥料使用分に比して36%、燐酸、別事、カルシウム
、マグネシウムは74〜112%多く含有することが明
らかであり、この事実は、作物を食する人間の健康にと
っても重大な好影響を与えるものである。
Furthermore, according to nutritional analysis of crops (onions) harvested by applying the fertilizer of the present invention, the nitrogen content in the individual crops was 36% compared to the amount used in conventional fertilizers, phosphoric acid, other substances, calcium, It is clear that the magnesium content is 74-112% higher, and this fact has a significant positive impact on the health of humans who eat the crops.

Claims (1)

【特許請求の範囲】[Claims] 1 動植物性堆肥材料と鉱滓(slag)の混合物に燻
炭、泥炭、汚炭、糞尿の中から選ばれた1種又はそれ以
上を混合し弱アルカリ性に調整したものにセルローズ分
解菌、糸状菌、硝化細菌、硫黄細菌、空気窒素固定菌、
根粒菌、放線菌を加え、更に酵母とシュウトモナス属の
菌、高温性細菌、高温性放線菌から選ばれた1種又はそ
れ以上を加えて高温発酵を行い、温度低下後、必要に応
じて上記各微生物の培養物を再添加することを特徴とす
る肥料製造法。
1. A mixture of animal and plant compost materials and slag is mixed with one or more selected from smoky coal, peat, sludge, and excrement and adjusted to be slightly alkaline, and then mixed with cellulose-degrading bacteria, filamentous bacteria, nitrifying bacteria, sulfur bacteria, atmospheric nitrogen fixing bacteria,
Rhizobium and actinomycetes are added, and one or more selected from yeast and Shutomonas bacteria, thermophilic bacteria, and thermophilic actinomycetes are added to carry out high-temperature fermentation. After the temperature is lowered, as necessary. A method for producing fertilizer, which comprises re-adding a culture of each of the above-mentioned microorganisms.
JP54142638A 1979-11-02 1979-11-02 Fertilizer manufacturing method Expired JPS5829273B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP54142638A JPS5829273B2 (en) 1979-11-02 1979-11-02 Fertilizer manufacturing method

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP54142638A JPS5829273B2 (en) 1979-11-02 1979-11-02 Fertilizer manufacturing method

Publications (2)

Publication Number Publication Date
JPS5669291A JPS5669291A (en) 1981-06-10
JPS5829273B2 true JPS5829273B2 (en) 1983-06-21

Family

ID=15319996

Family Applications (1)

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

Country Link
JP (1) JPS5829273B2 (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
GB2266522A (en) * 1992-04-10 1993-11-03 Towakagaku Kabushiki Kaisya A microorganism fertilizer

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JPS5669294A (en) * 1979-11-12 1981-06-10 Nippon Steel Corp Blended fertilizer manufacture utilizing iron slag
JPS6126582A (en) * 1984-07-17 1986-02-05 栗原 克男 Fermentation fertilizer from chicken excrements
JPH0665639B2 (en) * 1985-03-19 1994-08-24 義芳 門馬 Fertilizer production method with soil temperature rise
JPS63134590A (en) * 1986-11-26 1988-06-07 土の素株式会社 Granular conpost and manufacture
JP2920259B2 (en) * 1990-11-26 1999-07-19 幸太郎 栗田 Compost material fermentation promoter, method for producing compost material fermentation promoter, and liquid containing active rhizobia for use therein
JP2504364B2 (en) * 1992-08-07 1996-06-05 忠彦 秋田 Liquid livestock waste treatment method
EP0745573A4 (en) * 1994-12-20 1998-10-21 Mitsuyo Kimura Fermentation product and process for producing the same
MY166426A (en) * 2011-02-10 2018-06-26 Nippon Steel & Sumitomo Metal Corp Method for promoting composting using steel slag, and compost obtained therefrom
CN103172414B (en) * 2011-12-22 2015-01-28 刘旭辉 Organic fertilizer and preparation method thereof
JP6099076B2 (en) * 2012-08-20 2017-03-22 多機能フィルター株式会社 Deodorant biodegradation promoting material and deodorant biodegradation promoting method

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JPS5018252A (en) * 1973-06-13 1975-02-26
JPS5034944A (en) * 1973-07-26 1975-04-03

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JPS5018252A (en) * 1973-06-13 1975-02-26
JPS5034944A (en) * 1973-07-26 1975-04-03

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
GB2266522A (en) * 1992-04-10 1993-11-03 Towakagaku Kabushiki Kaisya A microorganism fertilizer
GB2266522B (en) * 1992-04-10 1996-07-31 Towakagaku Kabushiki Kaisya A microorganism fertilizer for potato growth

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