JPH0363596B2 - - Google Patents

Info

Publication number
JPH0363596B2
JPH0363596B2 JP60147728A JP14772885A JPH0363596B2 JP H0363596 B2 JPH0363596 B2 JP H0363596B2 JP 60147728 A JP60147728 A JP 60147728A JP 14772885 A JP14772885 A JP 14772885A JP H0363596 B2 JPH0363596 B2 JP H0363596B2
Authority
JP
Japan
Prior art keywords
slag
soil
zeolite
coal ash
bacteria
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 - Lifetime
Application number
JP60147728A
Other languages
Japanese (ja)
Other versions
JPS627787A (en
Inventor
Teruo Higa
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.)
Ryoko Co Ltd
Original Assignee
Ryoko 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 Ryoko Co Ltd filed Critical Ryoko Co Ltd
Priority to JP60147728A priority Critical patent/JPS627787A/en
Publication of JPS627787A publication Critical patent/JPS627787A/en
Priority to US07/427,910 priority patent/US4985060A/en
Publication of JPH0363596B2 publication Critical patent/JPH0363596B2/ja
Granted legal-status Critical Current

Links

Landscapes

  • Soil Conditioners And Soil-Stabilizing Materials (AREA)

Description

【発明の詳細な説明】[Detailed description of the invention]

[産業上の利用分野] 本発明は微生物を含有せしめてなる土壌改良剤
に関する。 [従来の技術] 土壌改良においてはPHおよび無機栄養のバラン
スを主とする化学性の改良、透水性、通気性、保
水性を主とする物理性の改良および土壌有用微生
物の活動に関する生物性の改良が挙げられる。 従来より種々の土壌改良剤が知られているが、
これらはいずれも上記特性の1つ又は2つを改良
するものであり、上記特性を総合的に改良するも
のはまだ知られていない。 例えばスラグや石炭灰を用いて土壌を改良する
方法が知られているが、スラグや石炭灰は強アル
カリ性であり、酸性土壌の改良には約立つが、ア
ルカリ障害をもたらすことが多い。また、これを
避けようとしてスラグや石炭灰の添加量を減らす
と短期間で酸性土壌に戻り、効果が持続しなくな
るという欠点がある。 また、スラグは水硬反応により土壌が固くなる
という欠点もある。 さらにスラグや石炭灰は肥料補足力が弱く、雨
水等で肥料が流出しやすいという欠点もあつた。 物理性の改良としては発泡スチロール粒子等を
土壌に分散混合する方法が知られているがこれは
単に土壌に空隙を与えるだけのものであり大雨等
の場合にはその空隙の故に排水効果が助長され発
泡粒子が土壌中から浮き出て土壌表面に流出し、
土壌改良効果が無くなり、かつ、肥料も一緒に流
出することが多かつた。 又、土壌微生物をバーミキユライト等に吸着さ
せた土壌活性剤に関する出願(特開昭55−40723
号公報等)もあるが、これは植物の根に有害な炭
化水素の分解やエチレンの吸着等に対しては充分
これらを防止し得るとはいえないものであり、ひ
いては、連作障害防止に充分約立つとはいえない
ものである。各種の土壌改良剤の発達した今日、
物理性、化学性の改良は比較的容易に行ない得る
ようになつているが、生物性の改良、特に連作障
害の防止については充分な対策がない現状にあ
る。即ち、連作障害防止対策は現代農業がかえる
最も重要な課題であるが、その解決のためには化
学性、物理性、生物性が総合的に組合わされ、か
つ連動することが必要であり、従来の改良剤にお
いてはこのような機能を果すものがなく、連作障
害の防止に効果の優れた総合的な土壌改良剤の開
発が望まれていた。 [発明が解決しようとする問題点] 本発明は従来の土壌改良剤の有する上記の欠点
がなく、土壌の化学性、物理性、生物性のいずれ
をも改良することができ、連作障害を防止できる
土壌改良剤を提供することを目的とするものであ
る。 [問題点を解決するための手段] 即ち、本発明の要旨は石炭灰4乃至4.75重量
部、スラグ4乃至4.75重量部及びゼオライド0.5
乃至2重量部からなる基材に、光合成菌と、放線
菌と、基材に対し0.2〜2%の糖蜜とを含有せし
めてなる土壌改良剤にある。 本発明において用いられる石炭灰は硼素、カリ
ウム分に富み、スラグはカルシウム、マグネシウ
ム分に富むが硼素、カリウム分が少ないため、こ
れを組み合わせると無機肥料成分のバランスがよ
くなるという特徴がある。しかし、これだけでは
アルカル障害を起し易い、水硬反応により土壌が
固くなる、肥料捕捉力が弱いという欠点は解消さ
れない。しかし、これにゼオライトを5乃至20%
となるように配合してなる土壌改良剤は充分添加
してもアルカリ障害を起すようなことはなく、か
つ、アルカル性を長期間にわたつて維持できるよ
うになる。 また、ゼオライドは特開昭55−40723号公報等
に使用されているようなバーミキユライトとは異
なり、高いイオン交換性のみならず、エチレン吸
収、炭化水素発生防止等の機能に優れるという特
徴を有するため、微生物の保存性もよく、有害嫌
気性微生物の活動を押えるという効果を有する。 石炭灰とスラグの比率は1:0.5乃至2である
ことが好ましく、1:1であることがより好まし
い。石炭灰は通常の微粉状の物を用いることがで
きる。スラグとしては高炉スラグ、転炉スラグ、
電気炉スラグのいずれも用いることができるが、
その組成から高炉スラグが好ましい。該スラグは
微粒状であることが好ましく、水砕スラグが好ま
しく用いられる。 ゼオライトの添加量が0.5%未満であると上記
ゼオライト添加の効果が充分発揮されず、20%を
越えて添加してもそれ以上の効果はなく、コスト
の上昇を招くだけである。 本発明において基材に吸着させる光合成菌とし
てはチオスピリルム、クロマテイウム、チオシス
テイス、チオペデイア、エクトチオロドスピラ等
の紅色硫黄細菌、ロドバシルス、ロドコツカス、
ロドスピリルム、ロドシユードモナス等の紅色無
硫黄細菌、クロロビウム、プロステコクロリス等
の緑色硫黄細菌等を挙げることができ、紅色無硫
黄細菌が最も好ましく用いられる。放線菌として
は通常土中に見出されるどのような放線菌も用い
ることができる。 糖蜜はスラグや石炭灰の硬化防止はもとより、
吸着させた微生物が均一、且つ急速に繁殖し得る
ように添加するものであり、基材に対して0.2〜
2%の範囲であればその役目を充分に果すことが
できる。なお、スラグや石炭灰は高温を経過して
いるためほぼ無菌状態となつており、しかも強ア
ルカリであるため糖蜜を添加しても雑菌が発生す
るおそれはない。 本発明の土壌改良剤は 1 糖蜜、尿素、魚粉、糞尿等、但し魚粉、糞尿
については一旦熱処理して減菌したものを用
い、これに酵母を添加して曝気しながら培養す
る。 2 この一部をとりわけ、これに放射菌と光合成
菌とを入れて太陽光又は紫外線と赤外線をあて
ながら40〜50℃で通気培養し、この液をゼオラ
イトに吸着させる。 3 1の一部をとり、これに光合成菌をいれて嫌
気培養し、この液をゼオライトに吸着させる。 4 2で得られる吸着ゼオライトと、3で得られ
る吸着ゼオライトに、基材に対し0.2〜2%と
なるような量の糖蜜を添加した石炭灰とスラグ
を混合する ことにより得ることができる。 2における酵母と放射菌と光合成菌の比率は30
〜70:15〜35:15〜35であることが好ましく、40
〜60:20〜30:20〜30であることがより好まし
い。2のゼオライトと3のゼオライトの混合物は
放射菌と光合成菌の比率が1:2〜4となるよう
にするのが好ましい。これにさらに窒素固定菌や
糸状菌等有用な微生物を吸着させたゼオライトを
混合してもよい。 [発明の効果] 本発明の土壌改良剤は石炭灰とスラグが好適な
比率で存在するため無機肥料成分のバランスがよ
く、かつ、ゼオライトが共存しているため強アル
カリがあるにもかかわらずアルカル障害を起すこ
となく、しかもアルカリの効果が持続するという
特長があり、石炭灰もスラグも高温を受けている
ため、有害な雑菌が存在しておらず、また、ゼオ
ライトおよびアルカリが抜けた後のスラグがイオ
ン交換能を有する多孔質体であり、有用微生物の
すみかとなる。また、ゼオライトには酵母、放線
菌と光合成菌が吸着されており、ゼオライトに吸
着されスラグと石炭灰に混和された菌体は他に競
合する菌がなく、アイカリ性のため菌の休眠保存
に好適な条件となり、安定に長期保存ができ、ま
た、土壌に混合したときに添加された糖蜜のため
酵母の働きが活発になると同時に放線菌や光合成
菌をはじめとする有用な微生物が安定して繁殖す
る。その結果、スラグやゼオライドの持つイオン
交換能や有害な炭化水素化合物の分解能と連動し
有害菌の直接的な抑制の外に有害な嫌気性菌の繁
殖を助長する炭化水素や硫化水素の発生を防止
し、連作障害を軽減するという効果があり、線虫
を抑える効果も高い。さらに多孔質体であるため
通気性、通水性も適度に改良され、従来にない総
合的な土壌改良を可能とするものである。また、
糖蜜の添加はスラグや石炭灰に由来する固化防止
に効果があるのみならず雑菌の発生がなく吸着さ
れた有効微生物の増殖にも極めて効果的で優先菌
の地位を決定的にする役割役割を有している。 本発明における放線菌と光合成菌の組合せの代
りの放線菌を単独で用いたものは当初は効果があ
つても放線菌の働きが低下するのに対し、本発明
の組合せでは放線菌の働きの低下がない。又、上
記2で得た放線菌と光合成菌を吸着したゼオライ
トに上記3の嫌気培養した光合成菌を吸着したゼ
オライトを混合したものは工程3によるゼオライ
トを混合しないものにくらべ、線虫の排除効果が
格段に高いという特徴を有する。 [実施例] 以下に本発明を実施例を用いてさらに詳しく説
明する。 実施例 1 糖蜜2Kg、尿素100g、魚粉2Kgを溶解した水
溶液200に酵母を添加して曝気しながら30℃で
3日培養した。これの約2/3を分け、これに放線
菌アクチノミセス ヒストレプトスポランギウム
と光合成菌ロドシユードモナス、ロドビチリス、
ロドコツカスを添加し、PHを7.0〜7.5に調整して
太陽光をあてながら撹拌を行ないながら40〜50℃
で4日間培養した。一方、上記酵母醸酵液の残り
1/3に光合成菌ロドシユードモナス、ロドバチリ
ス、ロドコツカスを添加して30℃で4日間嫌気培
養を行なつた。これら2つの培養液にゼオライト
微粒子を各々5Kgずつ添加混合して吸着させこれ
らを取出して各々乾燥した。この両者と水砕高炉
スラグ45Kg、石炭灰45Kgとミキサーで均一に混合
して土壌改良剤を得た。 これを沖縄本島北部恩納村の強酸性の重粘質赤
土に1アール当り30Kg、1年後に10Kg、さらにそ
の1年後に5Kgをまいて耕転し、サトウキビ、ホ
ウレンソウの栽培を行つた。その結果を第1表に
示す。 実施例 2 実施例1と同様にして得られた改良剤を沖縄県
中部西原町の特に線虫被害の著しい連作ハウスに
おいて1アール当り30Kg使用し、トマトの5連作
のテストを行つた。その結果を第2表に無処理の
ものと比較して示す。
[Industrial Application Field] The present invention relates to a soil conditioner containing microorganisms. [Conventional technology] Soil improvement involves chemical improvement, mainly PH and inorganic nutrient balance, physical improvement, mainly water permeability, air permeability, and water retention, and biological improvement, mainly related to the activities of beneficial soil microorganisms. Improvements can be mentioned. Various soil conditioners have been known for a long time, but
All of these improve one or two of the above characteristics, and nothing that comprehensively improves the above characteristics is known yet. For example, methods of improving soil using slag and coal ash are known, but slag and coal ash are strongly alkaline, and although they are effective in improving acidic soil, they often cause alkaline damage. In addition, if the amount of slag or coal ash added is reduced in an attempt to avoid this, the soil will return to acidic soil in a short period of time, and the effect will no longer last. Another disadvantage of slag is that it hardens the soil due to hydraulic reactions. Furthermore, slag and coal ash have a weak ability to absorb fertilizer, and the fertilizer is easily washed away by rainwater. A known method for improving physical properties is to disperse and mix styrofoam particles into soil, but this simply creates voids in the soil, and in the event of heavy rain, etc., the voids will enhance the drainage effect. Foamed particles float out of the soil and flow onto the soil surface,
The soil improvement effect was lost, and the fertilizer was often washed away along with it. Also, an application regarding a soil activator in which soil microorganisms are adsorbed to vermiculite etc.
However, it cannot be said to be sufficient to prevent decomposition of hydrocarbons and adsorption of ethylene, which are harmful to plant roots, and furthermore, it cannot be said to be sufficient to prevent damage to continuous cropping. This cannot be said to be true. Today, with the development of various soil improvers,
Although it has become relatively easy to improve the physical and chemical properties, there are currently no sufficient measures to improve the biological properties, especially to prevent continuous cropping problems. In other words, measures to prevent continuous cropping damage are the most important issue faced by modern agriculture, but in order to solve this problem, it is necessary to comprehensively combine and work together chemical, physical, and biological properties. There is no soil conditioner that performs this function, and there has been a desire to develop a comprehensive soil conditioner that is highly effective in preventing continuous cropping problems. [Problems to be solved by the invention] The present invention does not have the above-mentioned drawbacks of conventional soil conditioners, can improve all of the chemical, physical, and biological properties of soil, and prevents continuous cropping failure. The purpose is to provide a soil improvement agent that can improve soil quality. [Means for Solving the Problems] That is, the gist of the present invention is that 4 to 4.75 parts by weight of coal ash, 4 to 4.75 parts by weight of slag, and 0.5 parts by weight of zeolide.
The soil conditioner comprises a base material containing 2 to 2 parts by weight of photosynthetic bacteria, actinomycetes, and 0.2 to 2% molasses based on the base material. The coal ash used in the present invention is rich in boron and potassium, and the slag is rich in calcium and magnesium but low in boron and potassium, so when they are combined, the inorganic fertilizer components are well balanced. However, this alone does not solve the disadvantages of easy alkal damage, hardening of soil due to hydraulic reaction, and weak fertilizer trapping ability. However, 5 to 20% zeolite is added to this.
A soil conditioner formulated in the following manner will not cause alkaline damage even when added sufficiently, and will be able to maintain alkalinity over a long period of time. Also, unlike vermiculite used in Japanese Patent Application Laid-Open No. 55-40723, zeolide has the characteristics of not only high ion exchange properties but also excellent functions such as ethylene absorption and prevention of hydrocarbon generation. Because of this, microorganisms have good storage stability and have the effect of suppressing the activity of harmful anaerobic microorganisms. The ratio of coal ash to slag is preferably 1:0.5 to 2, more preferably 1:1. Coal ash in the form of ordinary fine powder can be used. Slag includes blast furnace slag, converter slag,
Any electric furnace slag can be used, but
Blast furnace slag is preferred because of its composition. The slag is preferably in the form of fine particles, and granulated slag is preferably used. If the amount of zeolite added is less than 0.5%, the effect of the above-mentioned addition of zeolite will not be sufficiently exhibited, and if it is added in excess of 20%, there will be no further effect, and this will only lead to an increase in cost. In the present invention, the photosynthetic bacteria to be adsorbed to the substrate include purple sulfur bacteria such as Thiospirillum, Chromateium, Thiocysteis, Thiopedia, and Ectothiorhodospira, Rhodobacillus, Rhodococcus,
Examples include purple sulfur-free bacteria such as Rhodospirillum and Rhodoseudomonas, green sulfur bacteria such as Chlorobium and Prostecochloris, and purple non-sulfur bacteria are most preferably used. As the actinomycete, any actinomycete that is normally found in soil can be used. Molasses not only prevents the hardening of slag and coal ash, but also
It is added so that the adsorbed microorganisms can reproduce uniformly and rapidly, and it is added to the base material at a concentration of 0.2 to
If it is within the range of 2%, it can fully fulfill its role. In addition, since slag and coal ash have passed through high temperatures, they are almost sterile, and since they are strongly alkaline, there is no risk of bacteria forming even when molasses is added. The soil conditioner of the present invention is 1. Molasses, urea, fish meal, manure, etc. However, the fish meal and manure are once sterilized by heat treatment, and yeast is added thereto and cultured with aeration. 2 Particularly, actinobacteria and photosynthetic bacteria are added to a part of this, and aerated culture is carried out at 40 to 50°C while exposed to sunlight or ultraviolet rays and infrared rays, and this liquid is adsorbed to zeolite. 3 Take a portion of 1, add photosynthetic bacteria to it, culture it anaerobically, and adsorb this liquid onto zeolite. 4 It can be obtained by mixing the adsorbed zeolite obtained in 2 and the adsorbed zeolite obtained in 3 with coal ash and slag to which molasses is added in an amount of 0.2 to 2% based on the base material. The ratio of yeast, actinobacteria, and photosynthetic bacteria in 2 is 30
~70:15~35: preferably 15~35, 40
It is more preferable that it is 60:20-30:20-30. The mixture of zeolite 2 and zeolite 3 is preferably such that the ratio of actinobacteria to photosynthetic bacteria is 1:2 to 4. Zeolite to which useful microorganisms such as nitrogen-fixing bacteria and filamentous bacteria have been adsorbed may be further mixed. [Effects of the Invention] The soil conditioner of the present invention has a good balance of inorganic fertilizer components because coal ash and slag are present in a suitable ratio, and since zeolite coexists, it does not contain alkalis despite the presence of strong alkalis. It has the advantage that it does not cause any damage and the alkali effect lasts for a long time.Since the coal ash and slag are exposed to high temperatures, there are no harmful bacteria, and after the zeolite and alkali are removed, Slag is a porous material with ion exchange ability and serves as a home for useful microorganisms. In addition, yeast, actinomycetes, and photosynthetic bacteria are adsorbed to zeolite, and the bacterial bodies that are adsorbed to zeolite and mixed with slag and coal ash have no competing bacteria, and because of their aikali nature, they can be stored dormant. The conditions are suitable and it can be stored stably for a long period of time, and the molasses added when mixed with the soil activates yeast activity and at the same time stabilizes useful microorganisms such as actinomycetes and photosynthetic bacteria. Breed. As a result, in conjunction with the ion exchange ability of slag and zeolide and the ability to decompose harmful hydrocarbon compounds, in addition to directly suppressing harmful bacteria, it also prevents the generation of hydrocarbons and hydrogen sulfide that promote the growth of harmful anaerobic bacteria. It is effective in preventing and reducing continuous crop failure, and is also highly effective in suppressing nematodes. Furthermore, since it is a porous material, its air permeability and water permeability are moderately improved, making it possible to improve soil in an unprecedented manner. Also,
The addition of molasses is not only effective in preventing solidification caused by slag and coal ash, but it is also extremely effective in proliferating the adsorbed effective microorganisms without the generation of miscellaneous bacteria, and plays a role that determines the status of priority bacteria. have. Using actinomycetes alone instead of the combination of actinomycetes and photosynthetic bacteria in the present invention may initially be effective, but the activity of actinomycetes is reduced, whereas the combination of the present invention reduces the activity of actinomycetes. There is no decline. In addition, a mixture of zeolite adsorbed with actinomycetes and photosynthetic bacteria obtained in step 2 above and zeolite adsorbed with photosynthetic bacteria cultivated anaerobically in step 3 above has a greater effect on eliminating nematodes than one in which the zeolite obtained in step 3 is not mixed. It has the characteristic of being extremely high. [Examples] The present invention will be explained in more detail below using Examples. Example 1 Yeast was added to 200 g of an aqueous solution containing 2 kg of molasses, 100 g of urea, and 2 kg of fish meal, and cultured at 30° C. for 3 days with aeration. Approximately 2/3 of this was divided into actinomycete Actinomyces histreptosporangium, photosynthetic bacteria Rhodosyudomonas, Rhodovitilis, and
Add Rhodococcus, adjust the pH to 7.0 to 7.5, and heat the mixture to 40 to 50℃ while stirring while exposing it to sunlight.
The cells were cultured for 4 days. On the other hand, photosynthetic bacteria Rhodoseudomonas, Rhodobacillus, and Rhodocoticus were added to the remaining 1/3 of the yeast fermentation solution, and anaerobic culture was performed at 30°C for 4 days. Five kilograms of zeolite fine particles were added to each of these two culture solutions, mixed, adsorbed, and then taken out and dried. Both of these were uniformly mixed with 45 kg of granulated blast furnace slag and 45 kg of coal ash in a mixer to obtain a soil conditioner. 30kg of this was sown per area in the strongly acidic heavy clay red soil of Onna Village in northern Okinawa's main island, then 10kg per area one year later, and 5kg after that one year, and cultivated sugarcane and spinach. The results are shown in Table 1. Example 2 The improver obtained in the same manner as in Example 1 was used at 30 kg per are in a continuous cropping house in Nishihara Town, central Okinawa Prefecture, where damage by nematodes is particularly severe, and a test was conducted on five consecutive crops of tomatoes. The results are shown in Table 2 in comparison with those without treatment.

【表】【table】

【表】 トマトは通常連作障害がよく発生する作物であ
り、線虫が発生しなくても著しい収量の低下をき
たす。第2表の結果は、本発明の改良剤が線虫の
発生を著しく抑制するのみならず線虫以外の連作
障害の防止にも効果があることを示している。
[Table] Tomatoes are a crop that commonly suffers from continuous cropping problems, and even if no nematodes occur, the yield will drop significantly. The results in Table 2 show that the improving agent of the present invention not only significantly suppresses the occurrence of nematodes, but is also effective in preventing continuous cropping damage caused by causes other than nematodes.

Claims (1)

【特許請求の範囲】 1 石炭灰4乃至4.75重量部、スラグ4乃至4.75
重量部及びゼオライト0.5乃至2重量部からなる
基材に、光合成菌と、放線菌と、基材に対し0.2
〜2%の糖蜜とを含有せしめてなる土壌改良剤。 2 スラグが高炉スラグであることを特徴とする
特許請求の範囲第1項記載の土壌改良剤。 3 石炭灰とスラグが等重量部であることを特徴
とする特許請求の範囲第1項記載の土壌改良剤。
[Claims] 1. 4 to 4.75 parts by weight of coal ash, 4 to 4.75 parts by weight of slag.
A base material consisting of parts by weight and 0.5 to 2 parts by weight of zeolite, photosynthetic bacteria, actinomycetes, and 0.2 parts by weight of zeolite.
A soil improvement agent containing ~2% molasses. 2. The soil conditioner according to claim 1, wherein the slag is blast furnace slag. 3. The soil improvement agent according to claim 1, wherein the coal ash and slag are equal parts by weight.
JP60147728A 1985-07-04 1985-07-05 Soil amending agent Granted JPS627787A (en)

Priority Applications (2)

Application Number Priority Date Filing Date Title
JP60147728A JPS627787A (en) 1985-07-05 1985-07-05 Soil amending agent
US07/427,910 US4985060A (en) 1985-07-04 1989-10-24 Soil conditioners

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP60147728A JPS627787A (en) 1985-07-05 1985-07-05 Soil amending agent

Publications (2)

Publication Number Publication Date
JPS627787A JPS627787A (en) 1987-01-14
JPH0363596B2 true JPH0363596B2 (en) 1991-10-01

Family

ID=15436820

Family Applications (1)

Application Number Title Priority Date Filing Date
JP60147728A Granted JPS627787A (en) 1985-07-04 1985-07-05 Soil amending agent

Country Status (1)

Country Link
JP (1) JPS627787A (en)

Families Citing this family (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2002256266A (en) * 2001-02-15 2002-09-11 Soruteko Kk Soil improvement and moisture regulator composition mainly composed of industrial waste and a method for producing the same
CU23590A1 (en) * 2007-04-30 2010-10-30 Ct Ingenieria Genetica Biotech BIOFERTILIZING COMPOSITION
US8734560B2 (en) * 2010-09-10 2014-05-27 Harsco Corporation Agricultural blend and process of forming an agricultural blend
JP2014156500A (en) * 2011-05-20 2014-08-28 Sumitomo Forestry Co Ltd Soil improvement cultivation method for peat bog soil
JP2022089338A (en) * 2020-12-04 2022-06-16 学校法人東京農業大学 Soil conditioner containing methane fermentation digestive fluid as active ingredient
CN113371783A (en) * 2021-06-11 2021-09-10 东北大学 Method for treating nitrogen and phosphorus wastewater by using water-quenched slag-fly ash-based 4A zeolite

Family Cites Families (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5540723A (en) * 1978-09-19 1980-03-22 Ishida Kazuyoshi Soil activator and its preparation
JPS5665081A (en) * 1979-11-02 1981-06-02 Nippon Steel Corp Soil conditioner for plant culture
JPS5755986A (en) * 1980-09-19 1982-04-03 Ooya:Kk Manufacture of soil conditioner

Also Published As

Publication number Publication date
JPS627787A (en) 1987-01-14

Similar Documents

Publication Publication Date Title
Zhu et al. Reducing odor emissions from feces aerobic composting: additives
US12331001B2 (en) Plant growth matrix
CN102531781B (en) Substrate for raising or cultivating vegetable seedling and preparation method thereof
KR102114840B1 (en) Manufacturing method for environment friendly fertilizer using livestock excretion
CN119242312A (en) A biochar composite improver for soil carbon increase and stabilization and preparation method thereof
KR100332368B1 (en) Method of the preparation of multi-functional and porous ceramics
CN115010550A (en) Technical method for preparing efficient soil conditioner by utilizing excess sludge
JPH0363596B2 (en)
JP3439701B2 (en) Production method of wood raw material compost
CN115119701B (en) Rice cultivation method using straw compost and environment-friendly ferment as base fertilizer
CN1359876A (en) Mud fertilizer and its preparing process
CN111925240A (en) Nitrogen-preserving deodorant for high-temperature composting of livestock and poultry manure
CN115918492B (en) Seedling substrate and preparation method thereof
CN116924856A (en) Preparation method of solid waste base artificial soil
JP2001047086A (en) Activator for nitric nitrogen denitrification
JPH11130573A (en) Composting accelerator composition
CN115594533A (en) Additive for improving decomposition degree of cow dung compost and application thereof
CN1045766A (en) Improving Organic Waste Fermentation Using Calcium Sulfate
CN117778027B (en) Vegetation concrete ecological modifier based on organic phosphonic acid and sulfur powder composite alkali reduction, and preparation method and application thereof
JPH10152385A (en) Production of organic fertilizer
JPS593089A (en) Manufacture of organic fertilizer
FI127616B (en) Compositions for the treatment of nitrogenous organic wastes
AU2021101370A4 (en) Compost Containing Silicic Pumice And Preparation Method And Use Thereof
JPH0363595B2 (en)
JPH09286684A (en) Soil conditioner

Legal Events

Date Code Title Description
R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250

EXPY Cancellation because of completion of term