JPS6069184A - Anaerobic microbe-based soil conditioner - Google Patents

Anaerobic microbe-based soil conditioner

Info

Publication number
JPS6069184A
JPS6069184A JP58101399A JP10139983A JPS6069184A JP S6069184 A JPS6069184 A JP S6069184A JP 58101399 A JP58101399 A JP 58101399A JP 10139983 A JP10139983 A JP 10139983A JP S6069184 A JPS6069184 A JP S6069184A
Authority
JP
Japan
Prior art keywords
soil
microbe
anaerobic
microorganisms
humus
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Pending
Application number
JP58101399A
Other languages
Japanese (ja)
Inventor
Chiaki Kobayashi
小林 千明
Soji Iikawa
飯川 宗次
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.)
Individual
Original Assignee
Individual
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Filing date
Publication date
Application filed by Individual filed Critical Individual
Priority to JP58101399A priority Critical patent/JPS6069184A/en
Publication of JPS6069184A publication Critical patent/JPS6069184A/en
Pending legal-status Critical Current

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  • Cultivation Of Plants (AREA)
  • Pretreatment Of Seeds And Plants (AREA)
  • Cultivation Receptacles Or Flower-Pots, Or Pots For Seedlings (AREA)
  • Soil Conditioners And Soil-Stabilizing Materials (AREA)
  • Fertilizers (AREA)

Abstract

PURPOSE:To promote formation of lumps and granules of soil, supply humus of good quality and maintain well-balanced oxidation and reduction in soil, by inoculating an organic substance with a useful anaerobic microbe for selective propagation of the microbe and fixation of decomposition product and microbe in clayey mineral particles. CONSTITUTION:An organic substance consisting of sugar, protein, cellulose, lignin, etc. is inoculated with a useful anaerobic soil microbe which effectively decomposes the above components, to effect propagation of the microbe under anaerobic conditions and decomposition of the organic substance into humus of good quality. The resultant decomposition product and the microbe are mixed with a clayey mineral of good quality so that the microbe may be adsorbed by the mineral for fixation and a soil conditioner consisting mainly of clay, humus and microbe may be formed. Preferred clayey mineral is montmorillonite which has a high base exchange volume and a high swellability.

Description

【発明の詳細な説明】 この発明は、土壌有機物及び塩類の分解に有用な嫌気性
土壌微生物を含んだ土壌改良剤に関するものである。
DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a soil improvement agent containing anaerobic soil microorganisms useful for decomposing soil organic matter and salts.

自然または人為的に施される土壌有機物が作物に有用な
腐植として分解されるためには、土壌に生息する微生物
が大きな役割を果たしている。特に腐植の生成について
は、一般的に好気性微生物の作用とされており、従って
土壌有機物の分解のためには専ら好気的条件が必要とさ
れてきた。この好気的条件が満たされない場合は、一種
の酸欠状態となって未分解の部分が残り、悪臭やガスの
発生源となる。この現象は、蛋白質等が種々の微生物に
よって分解され、悪臭や毒性のある物質(ブトマイン、
硫化水素。
Microorganisms living in soil play a major role in decomposing soil organic matter applied naturally or artificially into humus useful for crops. In particular, the production of humus is generally considered to be the action of aerobic microorganisms, and therefore aerobic conditions have been exclusively required for the decomposition of soil organic matter. If this aerobic condition is not met, a type of oxygen deficiency will occur and undecomposed portions will remain, creating a source of foul odors and gas. This phenomenon occurs when proteins, etc. are decomposed by various microorganisms, producing foul-smelling and toxic substances (butomain,
Hydrogen sulfide.

インドール、メカトール1強いアンモニア等)を生じる
成る種の腐敗性の分解作用であり、従って肥料養分の生
成もなく、時には作物に有害な物質を発生させる。この
状態を一般に嫌気性醗酵と称しており、酪酸菌や腐敗菌
等の作用から来る一種の腐敗醗酵の現象である。
It is a putrefactive decomposition action of seeds that produce indole, mecatol (strong ammonia, etc.), therefore, there is no production of fertilizer nutrients, and sometimes substances harmful to crops are generated. This state is generally called anaerobic fermentation, and is a type of putrid fermentation phenomenon caused by the action of butyric acid bacteria, putrefactive bacteria, and the like.

この問題は嫌気的条件が強い水田において多々現れる。This problem often appears in rice fields with strong anaerobic conditions.

水を張った水田では温度が高くなるにつれて微生物の活
動が次第に盛んになり、そうすると土壌の酸素が消費さ
れ、極端な酸欠状態となってくる。この結果、水田の作
土は、ごく表面の酸化層と、還元が進んだその下の還元
層とに分かれる。
In water-filled rice fields, as the temperature rises, microbial activity gradually increases, which consumes the oxygen in the soil, resulting in an extreme oxygen deficiency. As a result, the paddy soil is divided into an oxidized layer on the very surface and a reduced layer below, where reduction has progressed.

水田に生息している好気性微生物の多(は、酸素が存在
しなくても生存できるいわゆる条件的好気性微生物であ
るが、これらの微生物はガス状の酸素が不足してくると
土壌の中に含まれる無機物と化合している酸素を吸収し
、これを還元する。先ず土壌にふくまれている硝酸が還
元され、窒素ガスとなるが、窒素ガスは水に溶は難いた
め空気中へ放出される。このように窒素が可吸態になら
ず、土壌から分離してしまう現象を一般に脱窒現象と呼
んでいる。
Many of the aerobic microorganisms that live in rice fields are so-called facultative aerobic microorganisms that can survive even in the absence of oxygen. It absorbs oxygen combined with inorganic substances contained in the soil and reduces it. First, the nitric acid contained in the soil is reduced and becomes nitrogen gas, but since nitrogen gas is difficult to dissolve in water, it is released into the air. This phenomenon in which nitrogen does not become absorbable and separates from the soil is generally called denitrification.

つぎに二酸化マンガンや酸化鉄等がそれぞれ一酸化マン
ガンや亜酸化鉄に還元される。酸化状態で存在する二酸
化マンガンや酸化鉄は水に熔けず、作土の中に保持され
るが、これが還元されてできる上記−酸化マンガンや亜
酸化鉄は水に溶けやすいため、潅概水によて作土から流
れ、還元状態で生成する硫化水素の影響を直接作物の根
に及ぼすこと\なる。
Next, manganese dioxide, iron oxide, etc. are reduced to manganese monoxide and iron suboxide, respectively. Manganese dioxide and iron oxide, which exist in an oxidized state, cannot be dissolved in water and are retained in the soil, but the above-mentioned manganese oxide and iron suboxide, which are produced by reduction, are easily soluble in water, so they are not dissolved in irrigation water. Therefore, the hydrogen sulfide that flows from the cultivated soil and is produced in a reduced state has a direct effect on the roots of crops.

気温が上昇し、微生物の活動が盛んになり、土壌がさら
に還元されると、土壌の中は極端な酸素不足となる。こ
うなるとそれまで活動していた好気性微生物は活動でき
なくなり、これに代わって嫌気性微生物が活動を始める
。その代表的なのがいわゆる硫酸還元菌であり、これに
よって土壌に含まれる硫黄化合物が還元され、これに水
素が化合することによって硫化水素が発生する。この硫
化水素は、稲にとって有害な物質であり、いわゆる根腐
れの主因となる。
As temperatures rise, microbial activity increases, and the soil is further reduced, the soil becomes extremely oxygen deficient. When this happens, the previously active aerobic microorganisms become inactive, and anaerobic microorganisms begin to take their place. A typical example of this is the so-called sulfate-reducing bacteria, which reduce sulfur compounds contained in soil and combine with hydrogen to generate hydrogen sulfide. This hydrogen sulfide is a substance harmful to rice and is the main cause of so-called root rot.

このような土壌の還元化は、水田の老朽化とも深く係わ
っている。もともと老朽化水田と呼ばれるところでは、
礫が多く砂質で土壌の活性分子である粘土が少ないうえ
に、酸化鉄や二酸化マンガンが土壌の還元化によって溶
脱してしまい、これらが極端に少ない。従って肥料の保
持力を示す塩基置換容積が小さく、水持ちも悪い。また
、水を張ると急速に還元化が進み、酸化還元電位(Rh
)が下がって硫化水素の発生が多くなる。このような水
田の老朽化に対しては、従来主として客土等の方策が採
られてきたが、これによって充分な成果を挙げるには至
っていないのが実情である。
This type of soil reduction is closely related to the aging of rice paddies. In what was originally called an aged paddy field,
The soil is sandy with a lot of gravel, and there is little clay, which is an active molecule in the soil, and iron oxide and manganese dioxide are leached out due to soil reduction, so these are extremely rare. Therefore, the base substitution volume, which indicates the fertilizer retention capacity, is small and water retention is poor. In addition, when water is added, reduction progresses rapidly, and the redox potential (Rh
) decreases and hydrogen sulfide generation increases. In the past, measures such as adding soil have been mainly taken to combat the aging of rice paddies, but the reality is that these measures have not yielded sufficient results.

このような問題に対し、近年好気性微生物に代わって有
用嫌気性土壌微生物の利用が注目されつ\ある。この内
一部のものは、好熱性の腸内細菌として発見されたもの
で、高温醗酵の偏性嫌気性菌であり、これまで農業の分
野では、主に嫌気的条件下での堆肥の分解促進や畜糞の
分解促進といった面での利用が図られてきた。
To address these problems, the use of useful anaerobic soil microorganisms in place of aerobic microorganisms has recently been attracting attention. Some of these bacteria were discovered as thermophilic enteric bacteria, and are obligate anaerobic bacteria that ferment at high temperatures. It has been used to promote the decomposition of livestock manure.

この嫌気性微生物は、一般に完全嫌気性微生物或いは絶
対嫌気性微生物と呼ばれるもので、嫌気的条件のもとで
急速に発熱醗酵し、有機物を分解して良質の腐植を生成
し、その中で酸素。
These anaerobic microorganisms are generally called completely anaerobic microorganisms or obligate anaerobic microorganisms, and they rapidly perform exothermic fermentation under anaerobic conditions to decompose organic matter and produce high-quality humus, in which oxygen .

水素、エチレン及び二酸化炭素等を生成する。Generates hydrogen, ethylene, carbon dioxide, etc.

この発明は、有機物の分解に効果を発揮する上記のよう
な有用嫌気性土壌微生物の作用に着目してなされたもの
であって、土壌の団粒化を促進させると共に、良質の腐
植の供給を図り、同時に土壌の中の酸化と還元のバラン
スを保ことができるようにすることを目的とするもので
ある。
This invention was made by focusing on the action of the above-mentioned useful anaerobic soil microorganisms that are effective in decomposing organic matter. The purpose is to maintain the balance between oxidation and reduction in the soil.

この発明において使用される嫌気性土壌微生物は、成る
種の複合有機物を培地として接種培養することによって
、これらを多量に得ることができるが、この際使用され
る種菌としては、現在二つのグループの微生物を考える
ことができる。
The anaerobic soil microorganisms used in this invention can be obtained in large quantities by inoculating and culturing the complex organic matter of various species as a medium. I can think of microorganisms.

先ず一つは、一部特定の好気性菌を含むが、その殆どが
嫌気性のバクテリアからなる複合嫌気性微生物群(商品
名リサールL)で、これを構成する主な微生物を挙げる
と、プレクトリディウム スブマルム(Plectri
dium Spumarum) +ブレクトリディウム
 セルロリティウム(Pleatridiu+n Ce
llulolyticm ) + カデセウス セルロ
ーゼ デイゾルベンス(Caduceus Ce1lu
losae−Dissolνens) 、カデセウス 
セルロソルベンス(Caduceus Ce1lulo
−3olvens) 、カデセウスセルモアエロゲネス
(Caduceus Thermoaerogenes
) 、チルミノポラス セルモセラス(Thermin
osporus Thermocellus ) 、テ
ルミノポラスセルモセルロリティクム(Thermin
osporus Thermocellulolyti
cm)等と、必要に応じて好気性菌であるところのアス
ペルギル属の細菌を含んだものからなっている。
The first is the complex anaerobic microorganism group (trade name Rizal L), which includes some specific aerobic bacteria but mostly consists of anaerobic bacteria. Tridium subumarum (Plectri)
dium Spumarum) + Brectridium Celluloritium (Pleatridium+n Ce
llulololyticm) + Caduceus cellulose deisolbens (Caduceus Ce1lu
rosae-Dissolνens), Cadeseus
Cellulosolvens (Caduceus Ce1lulo)
-3olvens), Caduceus Thermoaerogenes
), Tilminoporus thermoceras (Thermin
osporus Thermocellus), Terminoporus thermocellulolyticum (Thermin
osporus thermocellulolyti
cm), etc., and, if necessary, bacteria of the genus Aspergillus, which is an aerobic bacterium.

もう一つのものは、酵母菌、乳酸菌等を複合的に培養し
たもの(商品名コーサンLB)で、これもやはり嫌気性
バクテリア主体の複合嫌気性微生物群である。その主な
ものを挙げると、サツカロミセス サケ(Saccha
roa+yces 5ake) 。
The other type is a complex culture of yeast, lactic acid bacteria, etc. (trade name Kosan LB), which is also a complex anaerobic microorganism group mainly composed of anaerobic bacteria. The main ones are Saccha
roa+yces 5ake).

サツカロミセス セレビシアエ(Saccharomy
ces Cerevisiae) * ラクトバシラス
 ブルガリカス(Lactobacillus Bul
garjcus) 、ラクトバシラス ブランクルーム
(Lactobacillus Plantarum 
) + ラクトバシラス アシドフィラス(Lacto
bacillus Ac1dophilus ) *バ
シラス アシディラクティス(Bacillus Ac
1dilactis)等からなる。
Saccharomyces cerevisiae
ces Cerevisiae) *Lactobacillus Bulgaricus
garjcus), Lactobacillus plantarum
) + Lactobacillus acidophilus (Lacto
bacillus Ac1dophilus) *Bacillus Acidilactis
1 dilactis), etc.

この発明では、糖分、蛋白質、セルロース。In this invention, sugar, protein, and cellulose.

リグニン等からなる有機物にこれらを分解するのに有効
な上記の有用嫌気性土壌微生物を接種して、嫌気的条件
のもとで同微生物を選択的に増殖させると同時に、これ
ら有機物を同微生物により分解して良質の腐植を得る。
The above-mentioned useful anaerobic soil microorganisms that are effective in decomposing organic substances such as lignin are inoculated, and the microorganisms are selectively grown under anaerobic conditions, and at the same time, these organic substances are destroyed by the microorganisms. Decompose to obtain high quality humus.

次ぎにこれにより得られた分解生成物を上記微生物と共
に良質の粘土鉱物に均一に混ぜ、同鉱物に上記微生物を
吸着させて固定させしめ、粘土、腐植。
Next, the resulting decomposition products are uniformly mixed with the above-mentioned microorganisms in a high-quality clay mineral, and the above-mentioned microorganisms are adsorbed and fixed on the minerals to form clay and humus.

微生物を主要素とする混合物を得る。この場合に使用す
る粘土鉱物としては、塩基置換容積が大きく、膨張性の
高いモンモリロナイトが適当であるが、この他の粘土鉱
物を使用することもできる。
A mixture containing microorganisms as the main element is obtained. As the clay mineral used in this case, montmorillonite, which has a large base displacement volume and high expandability, is suitable, but other clay minerals can also be used.

上記モンモリロナイトは、吸着作用が特に強いため、微
生物やこの生存に必要とする各種の栄養素を浸透吸収す
る働きが強く、混合した有機物や微生物を速やかに吸収
してその中に採り込む。また、一般に粘土は、互いに結
合して凝集体を作り、これが腐植の作用も加わってさら
に大きな凝集体となる働きを持つ。このように粘土と腐
植が互いに作用し合って直径数ミリメートルにも及ぶ土
壌団粒が形成されるが、特にモンモリロナイトは、塩基
置換容量が大きいため団粒を形成する作用が強い。これ
に加えて微生物に分解された有機物の上記中間生成物は
、一種の有機酸と粘液質のものを含み、土壌の団粒化を
促進させる。
The above-mentioned montmorillonite has a particularly strong adsorption effect, so it has a strong ability to penetrate and absorb microorganisms and the various nutrients necessary for their survival, and quickly absorbs mixed organic matter and microorganisms and incorporates them into the montmorillonite. Furthermore, clays generally combine with each other to form aggregates, which, when combined with the action of humus, function to become even larger aggregates. In this way, clay and humus interact to form soil aggregates with diameters of several millimeters, and montmorillonite in particular has a strong ability to form aggregates due to its large base substitution capacity. In addition, the intermediate products of organic matter decomposed by microorganisms include a type of organic acid and mucilage, which promotes soil agglomeration.

このような土壌団粒は、より高度な微生物の生息場所を
形成しており、このことは、直径10〜20μmの土壌
粒子の保持する細菌細胞数が、これ以下の大きさの土壌
粒子に比べて急激に増大するという事実が明確に示して
いる。また、土壌団粒内の酸素拡散による研究によれば
、直径0.2m以下の土壌粒子の中には殆ど嫌気的条件
を充たす部位はなく、嫌気性微生物を保持するためには
これ以上の大きさを持つより発達した団粒が必要とされ
る。そしてこの大きさをもった団粒の中でも、嫌気的部
位は、団粒の表面部分ではなく、その内部に存在してい
ると考えられる。
These soil aggregates form a habitat for more advanced microorganisms, which means that soil particles with a diameter of 10 to 20 μm can hold a larger number of bacterial cells than soil particles with a smaller size. This is clearly shown by the fact that there is a rapid increase in Furthermore, according to research on oxygen diffusion within soil aggregates, there are almost no parts of soil particles with a diameter of 0.2 m or less that satisfy anaerobic conditions; More developed agglomerates are required. Even within aggregates of this size, the anaerobic sites are thought to exist within the aggregates rather than on their surface.

しかじ団粒の中に好気的な部位と嫌気的な部位があり、
微生物の生存条件が分化されていても、微生物はそれだ
けでは生存できず、成る程度の水分と栄養素(主として
有機物)を必要とする。これについて、粘土鉱物のうち
でもモンモリロナイトを含んだ土壌団粒では、水分や栄
養分を多量に保持することができ、かつこの場合の水分
や栄養分の量を成る程度任意に調整することができるこ
とから、その中を高度な生存条件にコントロールするこ
とができる。この場合、上記混合物に含まれる微生物を
休眠状態で保存する場合は、概ね20〜26%程度の含
水量とするのが適当である。
There are aerobic parts and anaerobic parts in shikaji aggregates,
Even if the survival conditions of microorganisms are differentiated, microorganisms cannot survive on their own; they require a certain amount of water and nutrients (mainly organic matter). Regarding this, soil aggregates containing montmorillonite among clay minerals can retain large amounts of moisture and nutrients, and the amount of moisture and nutrients in this case can be adjusted to an arbitrary degree. It is possible to control the inside to a high degree of survival conditions. In this case, if the microorganisms contained in the mixture are to be preserved in a dormant state, it is appropriate that the water content be approximately 20 to 26%.

この発明による土壌改良剤は、畑や水田等の土壌に直接
投入するのが一般的使用方法であるが、特に稲等の育苗
用の苗床としてそのま\使用することもできる。
The soil conditioner according to the present invention is generally used by directly applying it to the soil of fields, paddy fields, etc., but it can also be used as is, especially as a seedbed for raising rice seedlings.

例えば、水田に土壌改良剤が投入されると、この中の団
粒内部に存在している有用な嫌気性微生物が嫌気的条件
の強い水田土壌の中で活発に活動を始め、これによって
土壌有機物が分解されると共に、腐植に含まれる各種の
要素が可吸態に分解され、作物に吸収される。この時上
記嫌気性微生物は、酸素を吸収することなく逆に酸素を
生成しつ\有機物を分解するので、土壌が極端な還元状
態にならず、従って作物に害を与える硫化水素の発生を
抑えることができる。
For example, when a soil conditioner is added to a paddy field, useful anaerobic microorganisms present inside the aggregates of the soil improver become active in the paddy soil, which has strong anaerobic conditions. At the same time, the various elements contained in humus are decomposed into respirable form and absorbed by crops. At this time, the anaerobic microorganisms do not absorb oxygen, but instead produce oxygen and decompose organic matter, so the soil does not reach an extremely reduced state, thus suppressing the generation of hydrogen sulfide that can harm crops. be able to.

また、土壌改良剤に含まれる粘土鉱物は、水田土壌の中
でも土壌の団粒化を促進し、塩基置換容積を高めるので
、保水力、保肥力が高まる。
In addition, the clay minerals contained in the soil conditioner promote soil agglomeration even in paddy soil and increase base replacement volume, thereby increasing water retention and fertilizer retention.

加えてこのモンモリロナイト等の粘土鉱物は、多くの酸
化鉄を含んでいるので、これが作物の根の周りで発生し
ようとする硫化水素を吸着してこれを無害な硫化鉄に変
える。このため、硫化水素の発生が抑えられ、上記有用
嫌気性微生物の作用と相乗的にいわゆる根腐れ等の弊害
が防止される。
In addition, clay minerals such as montmorillonite contain a lot of iron oxide, which adsorbs hydrogen sulfide that is generated around crop roots and converts it into harmless iron sulfide. Therefore, the generation of hydrogen sulfide is suppressed, and harmful effects such as so-called root rot are prevented synergistically with the action of the useful anaerobic microorganisms.

この点は、畑の場合も同様に作用し、土壌構造の物理的
な改良と共に、耕土の中に残った作物の残根その他の未
分解有機物等が腐敗分解することなく、有効な土壌有機
物へと醗酵分解され、これによって良質の腐植生成物質
が供給される。
This works in the same way in the field, and in addition to physically improving the soil structure, crop roots and other undecomposed organic matter remaining in the cultivated soil are converted into effective soil organic matter without rotting and decomposing. It is fermented and decomposed, which provides high-quality humus-producing substances.

一方、これを播種の苗床として使用した場合は、作物が
最も酸素を必要とする発芽、育苗時期に苗床の酸欠状態
を起こすことなく、良質の腐植に含まれる各種の要素を
粘土等の粒子中に保持しつ一1可吸的に分解して適量宛
苗に与える。このため、良質の苗を得ることができ、そ
の後の稲の生育にも大きな影響を与える。
On the other hand, when this is used as a seedbed for sowing, various elements contained in high-quality humus can be absorbed by particles such as clay without causing oxygen deficiency in the seedbed during the germination and seedling-raising periods when crops require the most oxygen. It is retained in the container, decomposed into absorbable form, and given to the seedlings in an appropriate amount. For this reason, it is possible to obtain high-quality seedlings, which has a great influence on the subsequent growth of rice.

さらに、このような使用方法の他に、籾や種子をこの土
壌改良剤で包むようにして塊状に造粒し、これを水田や
畑作に直播することによっても高い成果を得ることがで
きる。この使用方法においては、発芽、育苗時において
上記土壌改良剤が籾を包み、その後は粒状及び塊状が崩
壊して土壌の中に残ることから、上記苗床時の環境の効
果に加え、土壌改良剤本来の効果と省力性を発揮させる
ことができる。この場合、粘土鉱物としてモンモリロナ
イトを使用した場合1 は、強い結合力を有すると同時に、膨張性が高いことか
ら、造粒しやすい一方で、播いて水を含むことよにって
容易に崩壊し、耕土と一体化する特徴を持つ。
Furthermore, in addition to this method of use, high results can also be obtained by wrapping paddy or seeds in this soil conditioner and granulating it into lumps, and directly sowing this into paddy fields or field crops. In this method of use, the above-mentioned soil conditioner envelops the paddy during germination and seedling-raising, and after that, the granules and clumps disintegrate and remain in the soil. The original effect and labor saving can be demonstrated. In this case, when montmorillonite is used as the clay mineral, it has strong binding strength and high expandability, so it is easy to granulate, but it also disintegrates easily when it is seeded and soaked with water. , which has the characteristic of being integrated with cultivated soil.

以上のようにして、この発明による土壌改良剤によれば
、土壌の団粒化の促進と良質な腐植の供給が図られると
共に、土壌の酸化と還元のバランスを保つことができる
ようになり、これによって水田や畑作の老朽化の防止及
び病虫害の防除等を生物学的、物理的に実現することが
できる。また、畑作においても土壌構造の改良と共に、
所期の生育障害の発生を抑え、良質の土壌有機物を供給
する等、所期の目的を達成することができる。
As described above, according to the soil conditioner according to the present invention, it is possible to promote soil agglomeration and supply high-quality humus, and also to maintain the balance between soil oxidation and reduction. This makes it possible to biologically and physically prevent aging of rice paddies and field crops and control pests and diseases. In addition, in field crops, along with improving soil structure,
It is possible to achieve the desired objectives, such as suppressing the occurrence of growth disorders and supplying high-quality soil organic matter.

特許出願人 小 林 千 明 同上 飯用宗次 代理人 弁理士 北 條 和 由 2Patent applicant Chiaki Kobayashi Same as above Munetsugu Iiyo Agent: Patent Attorney Kazuyuki Kitajo 2

Claims (1)

【特許請求の範囲】 1、有機物の分解作用を持つ有用嫌気性土壌微生物を糖
分、蛋白質、セルロース、リグニン等からなる有機物に
接種して、これを嫌気的条件のもとで選択的に増殖させ
ると共に、上記有機物を分解させ、得られた分解生成物
を上記微生物と共に粘土鉱物に均一に混合して吸着せし
め、その粒子の中に固定させたことを特徴とする嫌気性
微生物系土壌改良剤。 2、粘土鉱物がモンモリロナイトである特許請求の範囲
第1項記載の嫌気性微生物系土壌改良材。
[Scope of Claims] 1. Useful anaerobic soil microorganisms that have the ability to decompose organic matter are inoculated into organic matter consisting of sugars, proteins, cellulose, lignin, etc., and selectively grown under anaerobic conditions. Further, an anaerobic microbial soil improvement agent characterized in that the above-mentioned organic matter is decomposed, the obtained decomposition product is uniformly mixed with the above-mentioned microorganisms into clay minerals, adsorbed, and fixed in the particles. 2. The anaerobic microbial soil improvement material according to claim 1, wherein the clay mineral is montmorillonite.
JP58101399A 1983-06-07 1983-06-07 Anaerobic microbe-based soil conditioner Pending JPS6069184A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP58101399A JPS6069184A (en) 1983-06-07 1983-06-07 Anaerobic microbe-based soil conditioner

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP58101399A JPS6069184A (en) 1983-06-07 1983-06-07 Anaerobic microbe-based soil conditioner

Publications (1)

Publication Number Publication Date
JPS6069184A true JPS6069184A (en) 1985-04-19

Family

ID=14299652

Family Applications (1)

Application Number Title Priority Date Filing Date
JP58101399A Pending JPS6069184A (en) 1983-06-07 1983-06-07 Anaerobic microbe-based soil conditioner

Country Status (1)

Country Link
JP (1) JPS6069184A (en)

Cited By (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS62179324A (en) * 1986-02-01 1987-08-06 株式会社 大塚産業 Bacteria incorporated artificial culture soil and its production
JPH01256589A (en) * 1988-04-07 1989-10-13 Tokai Hakko Biseibutsu Kenkyusho:Kk Soil conditioner and production thereof
WO1991009820A1 (en) * 1989-12-22 1991-07-11 Bruce Roy Thompson Treatment of carbonaceous material
JPH07109191A (en) * 1993-10-07 1995-04-25 Ii M Aasu Kk Production of organic fermented material mixed with microorganism
JPH07233370A (en) * 1994-02-23 1995-09-05 Aqua Green:Kk Soil improving material
US5753003A (en) * 1993-02-16 1998-05-19 Canon Kabushiki Kaisha Method for bio-remedying polluted soil
WO2000034413A1 (en) * 1998-12-04 2000-06-15 G F Murdoch Patents Limited Improvements in and relating to humic compositions
AU2004205304B2 (en) * 1998-12-04 2007-05-17 P.R. & Associates Pty Ltd Improvements in and relating to humic compositions

Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5288171A (en) * 1976-01-14 1977-07-23 Nitsuken Kensetsu Kk Process for comverting human manure into soil
JPS5540723A (en) * 1978-09-19 1980-03-22 Ishida Kazuyoshi Soil activator and its preparation
JPS55137186A (en) * 1979-04-11 1980-10-25 Sato Ichitaro Soil activator

Patent Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5288171A (en) * 1976-01-14 1977-07-23 Nitsuken Kensetsu Kk Process for comverting human manure into soil
JPS5540723A (en) * 1978-09-19 1980-03-22 Ishida Kazuyoshi Soil activator and its preparation
JPS55137186A (en) * 1979-04-11 1980-10-25 Sato Ichitaro Soil activator

Cited By (9)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS62179324A (en) * 1986-02-01 1987-08-06 株式会社 大塚産業 Bacteria incorporated artificial culture soil and its production
JPH0318850B2 (en) * 1986-02-01 1991-03-13 Ootsuka Sangyo Kk
JPH01256589A (en) * 1988-04-07 1989-10-13 Tokai Hakko Biseibutsu Kenkyusho:Kk Soil conditioner and production thereof
WO1991009820A1 (en) * 1989-12-22 1991-07-11 Bruce Roy Thompson Treatment of carbonaceous material
US5753003A (en) * 1993-02-16 1998-05-19 Canon Kabushiki Kaisha Method for bio-remedying polluted soil
JPH07109191A (en) * 1993-10-07 1995-04-25 Ii M Aasu Kk Production of organic fermented material mixed with microorganism
JPH07233370A (en) * 1994-02-23 1995-09-05 Aqua Green:Kk Soil improving material
WO2000034413A1 (en) * 1998-12-04 2000-06-15 G F Murdoch Patents Limited Improvements in and relating to humic compositions
AU2004205304B2 (en) * 1998-12-04 2007-05-17 P.R. & Associates Pty Ltd Improvements in and relating to humic compositions

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