JP5044179B2 - Method for producing deodorized organic fertilizer, deodorized organic fertilizer, and method for cultivating sugar beet or flower using the same - Google Patents
Method for producing deodorized organic fertilizer, deodorized organic fertilizer, and method for cultivating sugar beet or flower using the same Download PDFInfo
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Classifications
-
- Y—GENERAL 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
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02A—TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
- Y02A40/00—Adaptation technologies in agriculture, forestry, livestock or agroalimentary production
- Y02A40/10—Adaptation technologies in agriculture, forestry, livestock or agroalimentary production in agriculture
- Y02A40/20—Fertilizers of biological origin, e.g. guano or fertilizers made from animal corpses
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- Processing Of Solid Wastes (AREA)
- Treatment Of Sludge (AREA)
- Fertilizers (AREA)
Description
本発明は、消臭有機肥料の製造方法、消臭有機肥料およびそれを用いた蔬菜または花卉の栽培方法に関する。より詳しくは、本発明は、特定の多孔質担体および特定の微生物混合物を動物糞尿に混合することを特徴とする消臭有機肥料の製造方法に関する。 The present invention relates to a method for producing a deodorized organic fertilizer, a deodorized organic fertilizer, and a method for cultivating sugar beet or florets using the same. More specifically, the present invention relates to a method for producing a deodorized organic fertilizer characterized by mixing a specific porous carrier and a specific microorganism mixture with animal manure.
従来から飼育動物糞尿を用いた堆肥製造方法は、発酵中にアンモニアなどの窒素化合物および硫化水素が発生して悪臭がすること、切り返しを行わなければならないので労働力が必要であること、発酵に時間がかかること、悪臭をさせずに堆肥化するには大規模な設備が必要であることが問題とされ、解決のために下記の発明がなされてきた。 Traditionally, compost production methods using domestic animal manure produce nitrogen compounds such as ammonia and hydrogen sulfide during fermentation, which causes bad odors and requires reworking. The problem is that it takes time, and a large-scale facility is required for composting without causing bad odor, and the following inventions have been made to solve the problem.
例えば、強制通気または切り返しを行うことなく2〜5ヵ月程度通性嫌気発酵させ、仕上げ切り返しを行って1ヵ月程度好気発酵させることにより、悪臭を発生させずに畜糞を堆肥化する方法が報告されている(特許文献1参照)。この方法では大きな設備が必要である上、堆肥化にも時間がかかることが問題であった。 For example, a method of composting livestock manure without generating bad odor by performing facultative anaerobic fermentation for about 2 to 5 months without forced aeration or reversal, and performing aerobic fermentation for about 1 month with reversal finish is reported. (See Patent Document 1). This method requires large equipment and composting takes time.
有機廃棄物を粉砕し、微生物を混合して嫌気発酵させ、乾燥させる製造方法により、悪臭を発生させずに短時間で肥料化が可能になったが、堆肥製造設備は依然必要であった(特許文献2参照)。 The manufacturing method of pulverizing organic waste, mixing microorganisms, anaerobically fermenting, and drying makes it possible to fertilize in a short time without generating bad odors, but composting equipment is still necessary ( Patent Document 2).
また、土着菌微生物を採取・培養して堆肥製造に用いる方法が開発されているが、この方法では山林から採取した微生物を手間と時間をかけて培養する必要があった(特許文献3参照)。 In addition, a method of collecting and culturing indigenous microorganisms and using them for compost production has been developed. In this method, it is necessary to cultivate microorganisms collected from mountain forests with time and effort (see Patent Document 3). .
さらに、嫌気性種菌PTA−1773をエビおよび/またはカニの残渣等の有機素材に添加し、好気条件下かつ50〜90℃で発酵させることにより製造する堆肥が発明されているが、未知の細菌および/または放線菌との混合菌を用いることから、製造に使用する混合菌を入手することが難しいという問題があった(特許文献4参照)。 Furthermore, a compost produced by adding anaerobic inoculum PTA-1773 to organic materials such as shrimp and / or crab residue and fermenting at 50-90 ° C. under aerobic conditions has been invented. Since mixed bacteria with bacteria and / or actinomycetes are used, there is a problem that it is difficult to obtain mixed bacteria used for production (see Patent Document 4).
また、藁、糠および枯葉などの植物性原料、鶏糞およびバチルス・ズブチルス菌を混合し、切り返しを行って4ヵ月〜1年程度発酵させる堆肥の製造方法が報告されているが、発酵させるのに必要な期間が長いことが問題であった(特許文献5参照)。 In addition, a method for producing compost that has been mixed with plant raw materials such as straw, straw and dead leaves, chicken manure and Bacillus subtilis, turned over, and fermented for about 4 months to 1 year has been reported. The problem is that the required period is long (see Patent Document 5).
このように、種々の改良が検討されているが、動物糞尿を、アンモニアなどの悪臭を発生させず、切り返しを行わず、短期間に特別な装置を使わずに肥料化する方法は報告されていない。 As described above, various improvements have been studied. However, there has been reported a method for fertilizing animal manure without causing a bad odor such as ammonia, without turning it over, and without using a special device in a short period of time. Absent.
本発明は、アンモニアなどの悪臭を発生させず、短期間および低コストで製造可能な肥料の製造方法を提供することを目的とする。 An object of this invention is to provide the manufacturing method of the fertilizer which does not generate malodors, such as ammonia, and can be manufactured in a short period of time and low cost.
動物糞尿に特定の多孔質担体および特定の混合微生物を混合することにより、悪臭を発生させず短期間で肥料化できることを見出し、本発明を完成させた。また、この肥料が植物の生育を早め、非常に有用であることを見出した。 The present inventors have found that by mixing a specific porous carrier and a specific mixed microorganism with animal manure, a fertilizer can be produced in a short period of time without generating malodor. Moreover, it discovered that this fertilizer accelerated | stimulated the growth of a plant and was very useful.
すなわち、本発明は、バチルス・ズブチルス、バチルス・リケンホルミス、バチルス・サーキュランス、バチルス・ポリミキサ、クロストリジウム・セルロリィティカム、クロストリジウム・アエロトレランス、バチルス・アゾトフィクサンス、バチルス・マセランス、クロストリジウム・アセトブチリカムおよびクロストリジウム・パステリアナムからなる混合微生物、シラスおよび/またはシラスバルーンから選択される多孔質担体、ならびに動物糞尿を混合して発酵させることを特徴とする消臭有機肥料の製造方法に関する。 That is, the present invention relates to Bacillus subtilis, Bacillus rikenformis, Bacillus circulans, Bacillus polymixer, Clostridium cellulolyticum, Clostridium aerotolerance, Bacillus azotofixance, Bacillus macerans, Clostridium acetobutylicum and The present invention relates to a method for producing a deodorized organic fertilizer characterized by mixing and fermenting a mixed microorganism comprising Clostridium pasterianum, a porous carrier selected from Shirasu and / or Shirasu balloon, and animal manure.
前記製造方法において、発酵中に切り返しを行なわずに製造することが好ましい。 In the said manufacturing method, it is preferable to manufacture without performing turnover during fermentation.
前記製造方法において、発酵期間が20〜50日であることが好ましい。 In the production method, the fermentation period is preferably 20 to 50 days.
本発明はまた、前記製造方法によって得られる消臭有機肥料に関する。 The present invention also relates to a deodorized organic fertilizer obtained by the production method.
本発明はまた、バチルス・ズブチルス、バチルス・リケンホルミス、バチルス・サーキュランス、バチルス・ポリミキサ、クロストリジウム・セルロリィティカム、クロストリジウム・アエロトレランス、バチルス・アゾトフィクサンス、バチルス・マセランス、クロストリジウム・アセトブチリカムおよびクロストリジウム・パステリアナムからなる混合微生物、シラスおよび/またはシラスバルーンから選択される多孔質担体、ならびに動物糞尿を混合してなる消臭有機肥料に関する。 The present invention also includes Bacillus subtilis, Bacillus rikenformis, Bacillus circulans, Bacillus polymixer, Clostridium cellulolyticum, Clostridium aerotolerance, Bacillus azotofixance, Bacillus macerans, Clostridium acetobutylicum and Clostridium. -The present invention relates to a deodorized organic fertilizer formed by mixing a mixed microorganism comprising Pasterianum, a porous carrier selected from Shirasu and / or Shirasu balloon, and animal manure.
本発明はさらに、前記肥料を用いることを特徴とする蔬菜または花卉の栽培方法に関する。 The present invention further relates to a method for cultivating sugar beet or florets, characterized in that the fertilizer is used.
本発明の製造方法では、悪臭を発生させることなく、短期間・省労力にて優れた有機肥料を製造することができ、特別に大きな設備なども必要としない。 In the production method of the present invention, an excellent organic fertilizer can be produced in a short period of time and labor saving without generating malodors, and no specially large equipment is required.
本発明の製造方法では、牛、鶏、豚などの飼育動物の排泄物を、これら排泄物中の菌が繊維質などを腐熟させるときに発するアンモニアなどの悪臭のある物質の発生をおさえるため、切り返しなどの作業をしないで、時間と労働力と経費をかけないで消臭有機肥料として使用可能とすることができる。また、このため、得られる消臭有機肥料は元来排泄物に含まれる窒素、リンおよびカリウムなどの要素を通常の堆肥よりも多く含み有用である。 In the production method of the present invention, the excrement of domestic animals such as cattle, chickens and pigs is suppressed, and the generation of malodorous substances such as ammonia that are emitted when the fungi in these excretions ripen the fiber, etc. It can be used as a deodorized organic fertilizer without spending time, labor, and expenses without performing work such as turning over. For this reason, the deodorized organic fertilizer obtained is useful because it contains more elements such as nitrogen, phosphorus and potassium contained in the excrement than normal compost.
本発明の肥料は、悪臭を発生することなく、蔬菜または花卉を短期間で生育させることが可能である。 The fertilizer of the present invention can grow sugar beet or florets in a short period of time without generating malodor.
また、本発明の肥料は、作物の育成能力が高いため、少量の混合土、サイズの小さな箱および狭いスペースでも簡単に蔬菜または花卉を栽培することができ、高設栽培に非常に適している。 Further, since the fertilizer of the present invention has a high ability to grow crops, it is possible to easily cultivate sugar beet or flowers in a small amount of mixed soil, a small box and a narrow space, and it is very suitable for upland cultivation. .
さらに、本発明の肥料の使用により畑本来の地力が回復するため、蔬菜または花卉の抗菌性および抗害虫性が上昇し、農薬や化学肥料に頼ることなく蔬菜または花卉を栽培することが可能になる。 Furthermore, since the natural strength of the field is restored by the use of the fertilizer of the present invention, the antibacterial and anti-pest properties of sugar beet or flowers are increased, and it is possible to cultivate sugar beet or flowers without depending on agricultural chemicals or chemical fertilizers. Become.
本発明に用いる混合微生物は、バチルス・ズブチルス、バチルス・リケンホルミス、バチルス・サーキュランス、バチルス・ポリミキサ、クロストリジウム・セルロリィティカム、クロストリジウム・アエロトレランス、バチルス・アゾトフィクサンス、バチルス・マセランス、クロストリジウム・アセトブチリカムおよびクロストリジウム・パステリアナムであり、いずれの菌体も土壌由来である。これらの微生物は、通常土壌中で植物性繊維質の存在下、嫌気性条件下で繁殖可能である。これらは、一般的に試験研究に使用されている菌であり、市販されているものや微生物寄託機関および微生物保存機関に寄託されている容易に入手可能なものである。本発明の混合微生物には、リポペプタイド産生菌、セルラーゼ産生菌および窒素固定菌が含まれていることが好ましく、具体的には、たとえば、リポペプタイドおよびセルラーゼ産生菌であるバチルス・ズブチルス ATCC No.21332および6051ならびにバチルス・リケンホルミス ATCC No.39307および14580、セルラーゼ産生菌であるバチルス・サーキュランス ATCC No.9500、バチルス・ポリミキサ ATCC No.842、クロストリジウム・セルロリィティカム ATCC No.35319およびクロストリジウム・アエロトレランス ATCC No.43524、窒素を固定する菌であるバチルス・アゾトフィクサンス ATCC No.35681、バチルス・マセランス ATCC No.8244、クロストリジウム・アセトブチリカム ATCC No.824およびクロストリジウム・パステリアナム ATCC No.6013などの菌株を使用することが好ましい。 The mixed microorganisms used in the present invention include Bacillus subtilis, Bacillus rikenformis, Bacillus circulans, Bacillus polymixer, Clostridium cellulolyticum, Clostridium aerotolerance, Bacillus azotofix, Bacillus macerans, Clostridium. Acetobutylicum and Clostridium pasterianum, both of which are derived from soil. These microorganisms can reproduce in anaerobic conditions, usually in the presence of plant fibers in the soil. These are bacteria that are generally used for testing and research, and are commercially available or readily available that are deposited at microorganism depository institutions and microorganism preservation institutions. The mixed microorganism of the present invention preferably contains lipopeptide-producing bacteria, cellulase-producing bacteria, and nitrogen-fixing bacteria. Specifically, for example, Bacillus subtilis ATCC No. 21332 and 6051 and Bacillus rikenformis ATCC No. 39307 and 14580, Bacillus circulans ATCC No. 9500, Bacillus polymixer ATCC No. 842, Clostridium cellularity cam ATCC No. 35319 and Clostridium Aerotolerance ATCC No. 43524, Bacillus azotofixans ATCC No. 35681, Bacillus macerans ATCC No. 8244, Clostridium acetobutylicum ATCC No. 8 824 and Clostridium pasterianum ATCC No. It is preferred to use a strain such as 6013.
本発明の混合微生物における各微生物の割合は、特に限定されるものではないが、乾燥菌体重量で等量ずつ添加するのが好ましい。 The proportion of each microorganism in the mixed microorganism of the present invention is not particularly limited, but it is preferable to add an equal amount by dry cell weight.
本発明の混合微生物としては、細胞内水分を乾燥させ細胞の代謝機能の場である液相を除き微生物の活動を停止させた、休止状態の乾燥菌体をそのまま使用してもよく、あるいは乾燥菌体を培養液中に懸濁した形態で使用してもよい。また、乾燥菌体を培養液にて培養後、菌体懸濁液を少量の多孔質担体と混合し固定化して製造する混合微生物製剤として使用することもできる。取り扱いの容易さや、大量の糞尿や多孔質担体と均一に混ぜやすいという点から、混合微生物製剤を使用することが好ましい。 As the mixed microorganism of the present invention, a dry cell in a quiescent state in which intracellular moisture is dried and the activity of the microorganism is stopped except for a liquid phase which is a place of metabolic function of the cell may be used as it is, or dry You may use the microbial cell in the form suspended in the culture solution. Moreover, it can also be used as a mixed microorganism preparation produced by cultivating dried bacterial cells in a culture solution and then mixing and immobilizing the bacterial cell suspension with a small amount of a porous carrier. From the viewpoint of easy handling and easy mixing with a large amount of manure and porous carrier, it is preferable to use a mixed microorganism preparation.
混合微生物製剤は、培養液に微生物を懸濁した微生物懸濁液を多孔質担体に混合することにより製造することができる。具体的には、水に糖蜜を1mg〜3mgの割合で混合して培養液を500mg作製し、各微生物を乾燥重量で等量ずつ混合した乾燥混合微生物を0.3g〜0.5g添加する。これを2〜3日培養し、粒径20μm〜3mmのシラス(水分量0%〜5%)10kg〜20kgに混合して、固定化することにより製造することができる。 The mixed microorganism preparation can be produced by mixing a microorganism suspension obtained by suspending microorganisms in a culture solution with a porous carrier. Specifically, 500 mg of a culture solution is prepared by mixing molasses in water at a ratio of 1 mg to 3 mg, and 0.3 g to 0.5 g of dry mixed microorganisms in which each microorganism is mixed in an equal amount by dry weight is added. This can be produced by culturing for 2 to 3 days, mixing with 10 kg to 20 kg of shirasu (water content 0% to 5%) having a particle size of 20 μm to 3 mm, and immobilizing.
本発明に用いる多孔質担体は、シラスおよび/またはシラスバルーンから選択される。 The porous carrier used in the present invention is selected from Shirasu and / or Shirasu balloon.
シラスは一般的に灰白色で半固結状を呈し、多孔質で、幅広い粒形から構成されており、大部分は砂分および粒砂分からなる。鉱物組成は火山ガラス、斜長石を主成分とし、輝石、石英、磁鉄鋼などを副成分としている。シラスの真比重は、2.3〜2.5の範囲にある。化学組成はケイ酸分約70質量%、アルミナ分約14質量%、アルカリ酸化物約8質量%の順に含まれている。なお、シラスは、天然のものをそのまま使用することもできるが、加熱殺菌して使用してもよい。 Shirasu is generally grayish white, semi-consolidated, porous and composed of a wide range of particle shapes, most of which consists of sand and granular sand. Mineral composition is mainly composed of volcanic glass and plagioclase, and pyroxene, quartz, magnetic steel, etc. are minor components. The true specific gravity of Shirasu is in the range of 2.3 to 2.5. The chemical composition contains about 70% by mass of silicic acid, about 14% by mass of alumina, and about 8% by mass of alkali oxide. Shirasu can be used as it is, but may be used after heat sterilization.
シラスバルーンはシラスを800〜1200℃で熱処理し、発泡させることにより製造される多孔質、球状のものである。比重が軽いため軽量であり、かつ無色無害な耐化学薬品性に優れた環境にやさしい素材である。 The shirasu balloon is a porous and spherical product produced by heat-treating shirasu at 800 to 1200 ° C. and foaming. It is a lightweight material because of its low specific gravity, and is an environmentally friendly material that is colorless and harmless and has excellent chemical resistance.
本発明に使用するシラスおよびシラスバルーンの粒径は、共に20μm〜3mmであることが好ましい。20μm以下では保水力が下がるうえ、微生物の棲み処となる孔が少ないため微生物製剤として固定するにはあまり適さず、3mm以上の粒径では製造した肥料を畑、田んぼまたは鉢の土に混入した時に粒径が大き過ぎて団粒構造を壊すため好ましくない。 The particle diameters of the shirasu and shirasu balloon used in the present invention are preferably 20 μm to 3 mm. At 20 μm or less, water retention is reduced, and since there are few pores that can be used to absorb microorganisms, it is not very suitable for fixing as a microbial preparation. Fertilizer manufactured with a particle size of 3 mm or more is mixed with soil in fields, rice fields, or pots. Sometimes the particle size is too large, and the aggregate structure is broken, which is not preferable.
さらに、本発明に使用される動物糞尿は特に限定されることはないが、牛糞、鶏糞、豚糞のいずれか1つまたは2つ以上を選択して使用することができる。 Furthermore, the animal manure used in the present invention is not particularly limited, but any one or two or more of cow manure, chicken manure, and pig manure can be selected and used.
農作物に必要な3要素、窒素、リンおよびカリウムの含有率は、牛糞の生ふんでは窒素2.5%、リン4.1%、カリウム0.3%、鶏糞の生ふんでは窒素5.0%、リン4.7%、カリウム2.3%、豚糞の生ふんでは窒素4.3%、リン4.9%、カリウム0.6%(肥料便覧、第四版、社団法人、農山漁村文化協会発行)であるが、通常従来の堆肥では、製造に時間がかかり過ぎるため、これら3要素の含有率は非常に低いものとなる。ところが、本発明では、短期間で糞尿を使用可能な状態とすることができるため、3要素の含有率が通常の堆肥より高い非常に優れた肥料を得ることができる。 The three elements necessary for crops, nitrogen, phosphorus and potassium, are 2.5% for raw cow dung, 4.1% phosphorus, 0.3% potassium, and 5.0% nitrogen for raw chicken dung. , Phosphorus 4.7%, Potassium 2.3%, Pig manure raw nitrogen 4.3%, Phosphorus 4.9%, Potassium 0.6% (Fertilizer manual, 4th edition, corporation, farming and fishing village culture However, since conventional compost takes too much time to produce, the content of these three elements is very low. However, in the present invention, manure can be used in a short period of time, so that a very excellent fertilizer having a three-element content higher than that of normal compost can be obtained.
本発明の肥料に追加できる原料としては、えのきの廃培土、木炭などがあげられる。また、肥料や堆肥の製造に通常用いられる米糠、農業廃棄物、生活廃棄物、籾殻、サトウキビのバカス、米粉などを加えても良い。なかでも、米粉などはアミノ酸などが豊富に含まれており、目的により糞10kgに対して1〜3kgを加えることが好ましい。 Examples of raw materials that can be added to the fertilizer of the present invention include waste cultivated enoki mushrooms and charcoal. Further, rice bran, agricultural waste, domestic waste, rice husk, sugarcane bacus, rice flour, etc., which are usually used for producing fertilizer and compost may be added. Of these, rice flour and the like are rich in amino acids and the like, and it is preferable to add 1 to 3 kg to 10 kg of feces depending on the purpose.
本発明の消臭有機肥料の製造方法は、たとえば、混合微生物、動物糞尿、およびシラスおよび/またはシラスバルーンから選択される多孔質担体を混合し、表面を密閉し、数十日間放置することにより行なうことができる。 The method for producing a deodorized organic fertilizer of the present invention includes, for example, mixing a mixed carrier, animal excrement, and a porous carrier selected from Shirasu and / or Shirasu balloon, sealing the surface, and leaving it for several tens of days. Can be done.
本発明の消臭有機肥料のもう1つの製造方法は、たとえば、シラスおよび/またはシラスバルーンから選択される多孔質担体に、混合微生物の培養液を含浸させ固定した混合微生物製剤を、動物糞尿および多孔質担体と混合し、表面を密閉し、数十日間放置することにより行なうことができる。 Another method for producing the deodorized organic fertilizer of the present invention includes, for example, a mixed microorganism preparation in which a porous carrier selected from Shirasu and / or Shirasu balloon is impregnated with a culture solution of a mixed microorganism and fixed to animal manure and It can be performed by mixing with a porous carrier, sealing the surface, and leaving it for several tens of days.
本発明の肥料の製造場所はどこでも良く、例えばコンクリート上および土の上で製造することができる。表面は密閉できればどのような形でもよく、ビニールシートで覆うことが簡便で好ましい。 The fertilizer of the present invention can be produced at any place, for example, on concrete and soil. The surface may have any shape as long as it can be sealed, and it is convenient and preferable to cover the surface with a vinyl sheet.
通常、アンモニアの発生は発芽障害や初期発育の障害を引き起こすため、動物糞尿を使用可能な堆肥とするまでには数ヵ月から半年かかるものであるが、本発明の製造方法では、アンモニアの新たな発生がほとんどないため、混合微生物の混合後20〜50日で、播種・定植しても根をいためることのない使用可能な肥料とすることができる。発酵期間が20日より短いと、アンモニアが多少残留している場合があり、植物の生育を阻害しかねない。50日より長いと窒素、リンおよびカリウムなどの栄養素が減少し、肥料としての効力が低下する傾向にある。 Usually, the generation of ammonia causes a germination disorder and an initial development disorder, so it takes several months to half a year before animal manure can be used as compost. Since there is almost no generation | occurrence | production, it can be set as the usable fertilizer which does not hurt a root | route even after sowing and planting in 20 to 50 days after mixing of mixed microorganisms. If the fermentation period is shorter than 20 days, ammonia may remain to some extent, which may inhibit plant growth. When it is longer than 50 days, nutrients such as nitrogen, phosphorus and potassium are decreased, and the efficacy as a fertilizer tends to be decreased.
各成分の配合割合は、動物糞尿の重量に対して混合微生物を2〜3%、多孔質担体を5%〜7%の割合が好ましい。 The mixing ratio of each component is preferably 2 to 3% for mixed microorganisms and 5% to 7% for the porous carrier with respect to the weight of animal manure.
本発明の肥料は、種々の蔬菜または花卉の栽培に特に制限なく使用することが出来る。適したものとしては、水菜、小松菜、ミニ大根、ミニ人参、ミニかぶ、玉葱、苺、グリンピース、ほうれん草、きゅうり、ゴーヤ、なすび、レッドキャベツ、ソラマメ、スイートピー、クリサンセマムおよび菊などがあげられる。 The fertilizer of the present invention can be used without particular limitation for the cultivation of various sugar beet or florets. Suitable examples include mizuna, komatsuna, mini radish, mini carrot, mini turnip, onion, salmon, green peas, spinach, cucumber, bitter gourd, eggplant, red cabbage, broad bean, sweet pea, chrysanthemum and chrysanthemum.
以下に実施例をあげて本発明を詳細に説明するが、本発明はこれらに限定されるものではない。 Hereinafter, the present invention will be described in detail with reference to examples, but the present invention is not limited thereto.
製造例1
表1記載の微生物を乾燥重量で等量ずつ混合し、乾燥混合微生物を調製した。この乾燥混合微生物0.3gを、水500mgに糖蜜2gを含有させた培養液に添加し、18〜23℃で4日培養した。これを粒径20μm〜3mmのシラス(水分量0%〜5%)10kgに混合して固定させ、混合微生物製剤Aを製造した。
Production Example 1
The microorganisms listed in Table 1 were mixed in equal amounts by dry weight to prepare dry mixed microorganisms. 0.3 g of this dry mixed microorganism was added to a culture solution containing 2 g of molasses in 500 mg of water, and cultured at 18-23 ° C. for 4 days. This was mixed and fixed in 10 kg of shirasu (water content 0% to 5%) having a particle size of 20 μm to 3 mm to produce a mixed microorganism preparation A.
製造例2
シラスに代えて平均粒径141.92μmのシラスバルーンWB−601((株)アクシーズケミカル製)5kgを用いた以外は製造例1と同様にして混合微生物製剤Bを製造した。
Production Example 2
A mixed microorganism preparation B was produced in the same manner as in Production Example 1 except that 5 kg of Shirasu Balloon WB-601 (manufactured by Axes Chemical Co., Ltd.) having an average particle diameter of 141.92 μm was used instead of Shirasu.
下記実施例1〜6および比較例1〜6において、肥料は全てビニールシートで表面を密閉し、切り返しをしないで発酵させて製造した。 In the following Examples 1-6 and Comparative Examples 1-6, all fertilizers were manufactured by sealing the surface with a vinyl sheet and fermenting without turning back.
実施例1および比較例1
鹿児島県鹿屋市吾平の農地で、牛糞10kg、えのきの廃培土10kg、混合微生物製剤A200gおよび鹿児島県霧島市国分清水の山林で採取したシラス2kg(実施例1)または牛糞10kgおよびえのきの廃培土10kg(比較例1)を混ぜ合わせて土の上に置き、2002年7月10日から8月8日まで30日間発酵させた。
Example 1 and Comparative Example 1
10 kg of cow dung, 10 kg of enoki waste culture soil, 200 g of mixed microbial preparation A and 10 kg of shirasu collected in Kokubun Kiyomizu Forest of Kirishima City, Kagoshima Prefecture, or 10 kg of cow dung waste and 10 kg of enoki mushroom soil. (Comparative Example 1) was mixed and placed on the soil and fermented for 30 days from July 10 to August 8, 2002.
実施例1では堆肥がヘドロ状態になることもなく、悪臭の発生も抑制することができたが、比較例1の肥料は、ビニールシート中でヘドロ状になり、悪臭とガスで目も開けていられない状態となった。発酵中の温度およびアンモニア濃度の変化を1、10、20および30日目にガステック検知管式気体測定器(目盛範囲:1〜30ppm;(株)ガステック製、品番GV−100S)により測定した。結果を表2に示す。 In Example 1, the compost did not become sludge, and the generation of malodor could be suppressed, but the fertilizer of Comparative Example 1 became sludge in the vinyl sheet, and the eyes were opened with malodor and gas. I was unable to do so. Changes in temperature and ammonia concentration during fermentation were measured on the first, tenth, twenty and thirty days using a GASTEC detector tube type gas meter (scale range: 1 to 30 ppm; manufactured by GASTECH, product number GV-100S) did. The results are shown in Table 2.
表2より、実施例1の肥料は温度変化が穏やかで、発酵が徐々に進行した。また、10日目にはアンモニア濃度が3分の1程度まで低下し、20日目にはほぼアンモニアは発生しなくなっていることが明らかになった。比較例1の肥料では、30日目まで急激な温度上昇を続けた。またアンモニア濃度については、10日目ですでに検出上限の30ppm以上を示し、30日目まで30ppm以上の高いアンモニア濃度を示した。 From Table 2, the fertilizer of Example 1 had a mild temperature change, and the fermentation proceeded gradually. Moreover, it became clear that the ammonia concentration dropped to about one third on the 10th day, and almost no ammonia was generated on the 20th day. In the fertilizer of Comparative Example 1, a rapid temperature increase continued until the 30th day. As for the ammonia concentration, the upper limit of detection was already 30 ppm or more on the 10th day, and a high ammonia concentration of 30 ppm or more was shown until the 30th day.
実施例2および比較例2
鹿児島県霧島市国分の農地で、牛糞1t、混合微生物製剤A1kgおよび鹿児島県霧島市国分清水の山林で採取したシラス10kg(実施例2)を混ぜ合わせて畑に積み上げ、または牛糞1tのみ(比較例2)を土の上におき、2003年10月3日から11月3日まで31日間発酵させた。
Example 2 and Comparative Example 2
In farmland in Kirishima City, Kagoshima Prefecture, 1t of cow dung, mixed microorganism preparation A1kg and Shirasu 10kg (Example 2) collected from Kiribun Shimizu Forest in Kirishima City, Kagoshima Prefecture are mixed and stacked in the field, or only 1t of cow dung (comparative example) 2) was placed on the soil and fermented from October 3rd to November 3rd, 2003 for 31 days.
実施例2では堆肥がヘドロ状態になることもなく、悪臭の発生も抑制することができたが、比較例2の肥料は、ビニールシート中でヘドロ状になり、悪臭とガスで目も開けていられない状態となった。発酵中の温度およびアンモニア濃度の変化を1、10、20および30日目にガステック検知管式気体測定器(目盛範囲:1〜30ppm;(株)ガステック製、品番GV−100S)により測定した。結果を表3に示す。 In Example 2, the compost did not become sludge, and it was possible to suppress the generation of malodor, but the fertilizer of Comparative Example 2 became sludge in the vinyl sheet, and the eyes were opened with malodor and gas. I was unable to do so. Changes in temperature and ammonia concentration during fermentation were measured on the first, tenth, twenty and thirty days using a GASTEC detector tube type gas meter (scale range: 1 to 30 ppm; manufactured by GASTECH, product number GV-100S) did. The results are shown in Table 3.
表3より、実施例2の肥料は温度変化が穏やかで、発酵が徐々に進行した。また、10日目にはアンモニア濃度が2分の1程度まで低下し、20日目にはほぼアンモニアは発生しなくなっていることが明らかになった。比較例2の肥料では、30日目まで急激な温度上昇を続けた。またアンモニア濃度については、10日目ですでに検出上限の30ppm以上を示し、30日目まで30ppm以上の高いアンモニア濃度を示した。 From Table 3, the fertilizer of Example 2 had a mild temperature change, and fermentation proceeded gradually. Moreover, it became clear that the ammonia concentration dropped to about a half on the 10th day, and almost no ammonia was generated on the 20th day. In the fertilizer of Comparative Example 2, the rapid temperature increase continued until the 30th day. As for the ammonia concentration, the upper limit of detection was already 30 ppm or more on the 10th day, and a high ammonia concentration of 30 ppm or more was shown until the 30th day.
また、実施例2では、積み上げた肥料の周辺に雑草の生育が認められ、さらにビニールシートの中でも約20日後には雑草が生長した。これにより、実施例2では発酵が進むにつれ肥料からアンモニアガスなどの植物の害となるガスが発生しなくなることが実証された。 Moreover, in Example 2, weed growth was observed around the accumulated fertilizer, and the weed grew after about 20 days in the vinyl sheet. Thus, in Example 2, it was demonstrated that as fermenting progresses, no fertilizer generates gas that would harm plants such as ammonia gas.
実施例3および比較例3
鹿児島県霧島市国分の農地で、牛糞1t、混合微生物製剤A1kg、木炭5kg、米糠10kgおよび鹿児島県霧島市国分清水の山林で採取したシラス10kg(実施例3)または牛糞1tおよび米糠10kg(比較例3)を混ぜ合わせて畑の土の上に積み上げ、2004年1月13日から2月13日まで32日間発酵させた。
Example 3 and Comparative Example 3
In farmland in Kirishima City, Kagoshima Prefecture, 1 t of cow dung, 1 kg of mixed microorganism preparation, 5 kg of charcoal, 10 kg of rice bran, and 10 kg of shirasu collected in the mountain forest of Kokubun Kiyomizu, Kirishima City, Kagoshima Prefecture (Example 3) or 1 kg of cow dung and 10 kg of rice bran (comparative example) 3) was mixed and piled up on the soil of the field, and fermented for 32 days from January 13 to February 13, 2004.
実施例1では堆肥がヘドロ状態になることもなく、悪臭の発生も抑制することができたが、比較例1の肥料は、ビニールシート中でヘドロ状になり、悪臭とガスで目も開けていられない状態となった。発酵中の温度およびアンモニア濃度の変化を1、10、20および30日目にガステック検知管式気体測定器(目盛範囲:1〜30ppm;(株)ガステック製、品番GV−100S)により測定した。結果を表4に示す。 In Example 1, the compost did not become sludge, and the generation of malodor could be suppressed, but the fertilizer of Comparative Example 1 became sludge in the vinyl sheet, and the eyes were opened with malodor and gas. I was unable to do so. Changes in temperature and ammonia concentration during fermentation were measured on the first, tenth, twenty and thirty days using a GASTEC detector tube type gas meter (scale range: 1 to 30 ppm; manufactured by GASTECH, product number GV-100S) did. The results are shown in Table 4.
表4より、実施例3の肥料は温度変化が穏やかで、発酵が徐々に進行した。また、10日目にはアンモニア濃度が4分の3程度まで低下し、30日目にはほぼアンモニアは発生しなくなっていることが明らかになった。比較例3の肥料では、20日目まで急激な温度上昇を続けた。またアンモニア濃度については、10日目ですでに検出上限の30ppm以上を示し、30日目まで30ppm以上の高いアンモニア濃度を示した。 From Table 4, the temperature change of the fertilizer of Example 3 was gentle, and fermentation proceeded gradually. Moreover, it became clear that the ammonia concentration dropped to about three-quarters on the 10th day, and almost no ammonia was generated on the 30th day. In the fertilizer of Comparative Example 3, the temperature increased rapidly until the 20th day. As for the ammonia concentration, the upper limit of detection was already 30 ppm or more on the 10th day, and a high ammonia concentration of 30 ppm or more was shown until the 30th day.
また、実施例3では、積み上げた肥料の周辺に雑草の生育が認められ、さらにビニールシートの中でも約20日後には雑草が生長した。これにより、実施例3では発酵が進むにつれ肥料からアンモニアガスなどの植物の害となるガスが発生しなくなることが実証された。 Moreover, in Example 3, weed growth was recognized around the piled fertilizer, and weeds grew after about 20 days in the vinyl sheet. Thus, in Example 3, it was demonstrated that as fermenting progresses, no gas that would harm plants such as ammonia gas was generated from the fertilizer.
実施例4および比較例4
鹿児島県指宿市畜産農家の駐車場のコンクリートの上に、牛糞10t、混合微生物製剤A10kg、木炭20kg、米糠40kgおよび鹿児島県喜入町の山林から採取したシラス40kgを混ぜ合わせて積み上げ(実施例4)、または牛糞2tを積み上げ(比較例4)2004年2月5日から3月5日まで30日間発酵させた。
実施例4では悪臭とガスの発生を抑制することができたが、比較例4の肥料は悪臭とガスを発生させた。発酵中の温度およびアンモニア濃度の変化を1、10、20および29日目にガステック検知管式気体測定器(目盛範囲:1〜30ppm;(株)ガステック製、品番GV−100S)により測定した。結果を表5に示す。
Example 4 and Comparative Example 4
(Example 4) Mixing and stacking 10t of cattle manure, 10kg of mixed microorganism preparation A, 20kg of charcoal, 40kg of rice bran, and 40kg of shirasu collected from the forests of Kiiri-cho, Kagoshima Alternatively, 2 t of cow dung was stacked (Comparative Example 4) and fermented for 30 days from February 5, 2004 to March 5, 2004.
In Example 4, it was possible to suppress the generation of malodor and gas, but the fertilizer of Comparative Example 4 generated malodor and gas. Changes in temperature and ammonia concentration during fermentation were measured on day 1, 10, 20 and 29 using a GASTEC detector tube type gas meter (scale range: 1 to 30 ppm; manufactured by GASTECH, product number GV-100S) did. The results are shown in Table 5.
表5より、実施例4の肥料は温度変化が穏やかで、発酵が徐々に進行した。また、10日目にはアンモニア濃度が2分の1程度まで低下し、20日目にはほぼアンモニアは発生しなくなっていることが明らかになった。比較例3の肥料では、20日目まで急激な温度上昇を続けた。またアンモニア濃度については、10日目ですでに検出上限の30ppm以上を示し、29日目まで30ppm以上の高いアンモニア濃度を示した。これにより、実施例4では発酵が進むにつれ肥料からアンモニアガスなどの植物の害となるガスが発生しなくなることが実証された。 From Table 5, the temperature change of the fertilizer of Example 4 was gentle, and fermentation proceeded gradually. Moreover, it became clear that the ammonia concentration dropped to about a half on the 10th day, and almost no ammonia was generated on the 20th day. In the fertilizer of Comparative Example 3, the temperature increased rapidly until the 20th day. As for the ammonia concentration, the upper limit of detection was already 30 ppm or more on the 10th day, and a high ammonia concentration of 30 ppm or more was shown until the 29th day. As a result, it was demonstrated in Example 4 that as fermenting progresses, no fertilizer generates gas that would harm plants such as ammonia gas.
実施例5および比較例5
鹿児島県指宿市畜産農家の堆舎のコンクリートの上に、牛糞10t、混合微生物製剤B10kg、木炭20kg、米糠40kgおよびシラスバルーンSSB−400((株)アクシーズケミカル製、49.3〜1.4ミクロンの菌の増殖用基材)10kgを混ぜ合わせて積み上げ(実施例5)、または牛糞2tを積み上げ(比較例5)、2004年5月20日から6月20日までの32日間発酵させた。
Example 5 and Comparative Example 5
Cattle manure 10t, mixed microorganism preparation B10kg, charcoal 20kg, rice bran 40kg and Shirasu Balloon SSB-400 (manufactured by Axes Chemical Co., Ltd., 49.3-1.4 microns) (Example 5) or cow dung 2t was stacked (Comparative Example 5) and fermented for 32 days from May 20 to June 20, 2004.
実施例5では悪臭とガスの発生を抑制することができたが、比較例5の肥料は悪臭とガスを発生させた。発酵中の温度およびアンモニア濃度の変化を1、10、20および30日目にガステック検知管式気体測定器(目盛範囲:1〜30ppm;(株)ガステック製、品番GV−100S)により測定した。結果を表6に示す。 In Example 5, it was possible to suppress the generation of malodor and gas, but the fertilizer of Comparative Example 5 generated malodor and gas. Changes in temperature and ammonia concentration during fermentation were measured on the first, tenth, twenty and thirty days using a GASTEC detector tube type gas meter (scale range: 1 to 30 ppm; manufactured by GASTECH, product number GV-100S) did. The results are shown in Table 6.
表6より、実施例5の肥料は温度変化が穏やかで、発酵が徐々に進行した。また、10日目にはアンモニア濃度が2分の1程度まで低下し、20日目にはほぼアンモニアは発生しなくなっていることが明らかになった。比較例5の肥料では、30日目まで急激な温度上昇を続けた。またアンモニア濃度については、10日目ですでに検出上限の30ppm以上を示し、30日目まで30ppm以上の高いアンモニア濃度を示した。これにより、実施例5では発酵が進むにつれ肥料からアンモニアガスなどの植物の害となるガスが発生しなくなることが実証された。 From Table 6, the temperature change of the fertilizer of Example 5 was gentle, and fermentation proceeded gradually. Moreover, it became clear that the ammonia concentration dropped to about a half on the 10th day, and almost no ammonia was generated on the 20th day. In the fertilizer of Comparative Example 5, the rapid temperature increase continued until the 30th day. As for the ammonia concentration, the upper limit of detection was already 30 ppm or more on the 10th day, and a high ammonia concentration of 30 ppm or more was shown until the 30th day. As a result, in Example 5, it was demonstrated that as fermenting progresses, no gas that would harm plants such as ammonia gas was generated from the fertilizer.
実施例6および比較例6
鹿児島県曽於郡大崎町の駐車場のコンクリートの上に、牛糞500kg、鶏糞500kg、混合微生物製剤A1kgおよび鹿児島県曽於郡大崎町の山林から採取したシラス10kg(実施例6)、または牛糞500kgおよび鶏糞500kg(比較例6)を混ぜ合わせて積み上げ、2005年8月21日から9月21日までの32日間発酵させた。
Example 6 and Comparative Example 6
On the concrete in the parking lot in Osaki-cho, Kagoshima Prefecture, 500 kg of cow dung, 500 kg of chicken dung, 1 kg of mixed microorganism preparation, and 10 kg of shirasu collected from the mountain forest of Osaki-cho, Kagoshima Prefecture (Example 6), or 500 kg of cow dung and chicken dung 500 kg (Comparative Example 6) was mixed and stacked, and fermented for 32 days from August 21, 2005 to September 21, 2005.
実施例6では悪臭とガスの発生を抑制することができたが、比較例6の肥料はビニールシートの中でヘドロ状になり、悪臭とガスを発生させた。発酵中の温度およびアンモニア濃度の変化を1、10、20および30日目にガステック検知管式気体測定器(目盛範囲:1〜30ppm;(株)ガステック製、品番GV−100S)により測定した。結果を表7に示す。 In Example 6, the generation of malodor and gas could be suppressed, but the fertilizer of Comparative Example 6 became sludge in the vinyl sheet and generated malodor and gas. Changes in temperature and ammonia concentration during fermentation were measured on the first, tenth, twenty and thirty days using a GASTEC detector tube type gas meter (scale range: 1 to 30 ppm; manufactured by GASTECH, product number GV-100S) did. The results are shown in Table 7.
表7より、実施例6の肥料は温度変化が穏やかで、発酵が徐々に進行した。また、20日目にはアンモニア濃度が3分の1程度まで低下し、30日目にはほぼアンモニアは発生しなくなっていることが明らかになった。比較例6の肥料では、20日目まで急激な温度上昇を続けた。またアンモニア濃度については、10日目ですでに検出上限の30ppm以上を示し、30日目まで30ppm以上の高いアンモニア濃度を示した。これにより、実施例6では発酵が進むにつれ肥料からアンモニアガスなどの植物の害となるガスが発生しなくなることが実証された。 From Table 7, the fertilizer of Example 6 had a mild temperature change, and the fermentation proceeded gradually. Moreover, it became clear that the ammonia concentration dropped to about one third on the 20th day, and almost no ammonia was generated on the 30th day. In the fertilizer of Comparative Example 6, the rapid temperature increase continued until the 20th day. As for the ammonia concentration, the upper limit of detection was already 30 ppm or more on the 10th day, and a high ammonia concentration of 30 ppm or more was shown until the 30th day. Thus, in Example 6, it was demonstrated that as fermenting progressed, no fertilizer generated gas that would harm plants such as ammonia gas.
実施例7 水菜栽培
実施例1の肥料5kg、黒土2.5kgおよび腐葉土2.5kgを混ぜ、ネットハウスの中で育苗用のプラスチックの箱(W60cm×D30cm×H4cm)に入れ、9月5日に水菜の種を5cm間隔で数個ずつ20ヵ所蒔いた。4日後に発芽し、その後間引きして1ヵ所1株とし、40〜45日後に20株全てを収穫することができた。葉の長さは25〜30cmまで生長した。
Example 7 Mizuna Cultivation Mix 5kg of fertilizer of Example 1, 2.5kg of black soil and 2.5kg of humus soil, put them in a plastic box for raising seedlings (W60cm x D30cm x H4cm) in a net house, and on September 5 Several 20 mizuna seeds were planted at 5 cm intervals. It germinated after 4 days, and then thinned out to one strain at one place, and all 20 strains could be harvested after 40 to 45 days. Leaf length grew to 25-30 cm.
また、組合化成7号(三菱化学(株)製)の肥料1kgと黒土3kgと腐葉土3kgを混ぜ、4月5日に水菜の種を5cm間隔に数個ずつ20ヵ所蒔いた。4日後に発芽し、45〜65日後までかけて17株を収穫することができたが、3株は収穫できる大きさに満たなかった。収穫した葉の長さは15〜20cmであった。 Also, 1 kg of fertilizer from Kunsei Kasei No. 7 (Mitsubishi Chemical Co., Ltd.), 3 kg of black soil and 3 kg of humus were mixed, and on April 5, 20 seeds of mizuna were planted at 5 cm intervals. Germination occurred after 4 days, and 17 strains could be harvested from 45 to 65 days later, but 3 strains were not large enough to be harvested. The length of the harvested leaves was 15-20 cm.
実施例8 小松菜栽培
実施例1の肥料を5kgと黒土2.5kgと腐葉土2.5kgを混ぜ、9月5日に、ネットハウスの中で育苗用のプラスチックの箱(W60cm×D30cm×H4cm)に入れ、これに小松菜の種を5cm間隔に数個ずつ40ヵ所蒔いた。4日後に発芽し、12日後に間引きして1ヵ所1株とし、44〜49日後に40株全てを収穫することができた。葉の長さは26〜33cmまで生長した。
Example 8 Komatsuna cultivation 5 kg of fertilizer of Example 1, 2.5 kg of black soil and 2.5 kg of humus soil were mixed, and on September 5 in a plastic box for raising seedlings in a net house (W 60 cm x D 30 cm x H 4 cm) Into this, several seeds of Komatsuna were seeded at 40 places at intervals of 5 cm. It germinated after 4 days, thinned out after 12 days to give one strain at one place, and all 40 strains could be harvested after 44 to 49 days. Leaf length grew to 26-33 cm.
組合化成7号(三菱化学(株)製)の肥料1kgと黒土3kgと腐葉土3kgを混ぜ、4月5日に小松菜の種を5cm間隔に数個ずつ40ヵ所蒔いた。4日後に発芽し、15日目に間引きして1ヵ所1株とし、50〜60日までかけて15株を収穫することができたが、25株は収穫できる大きさに満たなかった。収穫した葉の長さは15〜20cmであった。 We mixed 1 kg of fertilizer from Kunsei Kasei 7 (Mitsubishi Chemical Co., Ltd.), 3 kg of black soil and 3 kg of humus soil, and on April 5, we planted several seeds of komatsuna at several intervals of 5 cm. It germinated after 4 days, and it was thinned out on the 15th day to make one strain at one place, and 15 strains could be harvested from 50 to 60 days, but 25 strains were not large enough to be harvested. The length of the harvested leaves was 15-20 cm.
実施例9 ミニ大根栽培
実施例1の肥料を5kgと黒土2.5kgと腐葉土2.5kgを混ぜ、ネットハウスの中でプラスチックの箱(W45cm×D35cm×H8cm)に入れ、2月28日にミニ大根の種を5cm間隔に数個ずつ40ヵ所蒔いた。5日後に発芽し、9日後に間引きして1ヵ所1株とし、49日後に40株全てを収穫することができた。ミニ大根の直径は2〜3cm、長さが5〜6cmまで生長した。
Example 9 Mini Radish Cultivation 5 kg of fertilizer of Example 1, 2.5 kg of black soil, and 2.5 kg of humus soil are mixed and placed in a plastic box (W45 cm x D35 cm x H8 cm) in a net house. Several radish seeds were planted at intervals of 5 cm at 40 locations. It germinated after 5 days, thinned out after 9 days to give one strain at one place, and all 40 strains could be harvested after 49 days. The mini radish had a diameter of 2 to 3 cm and a length of 5 to 6 cm.
組合化成3号(片倉チッカリン(株)製)の肥料1kgと黒土5kgと腐葉土3kgを混ぜ、2月28日にミニ大根の種を4cm間隔に数個ずつ40ヵ所蒔いた。5日後に発芽し、10日後に間引きして1ヵ所1株とし、45〜60日後までかけて38株を収穫することができたが、2株は収穫できる大きさに満たなかった。収穫したミニ大根の直径は平均約2.0cm、長さが約4.9cmであった。 We mixed 1 kg of fertilizer and 5 kg of black soil and 3 kg of humus soil from Kunsei Kasei No. 3 (manufactured by Katakura Chikkarin Co., Ltd.). On February 28, 40 seeds of mini radish were seeded at 4 cm intervals. It germinated after 5 days, and after 10 days, it was thinned to one strain at one place, and 38 strains could be harvested from 45 to 60 days later, but the two strains were not large enough to be harvested. The harvested mini radish had an average diameter of about 2.0 cm and a length of about 4.9 cm.
実施例10 ミニカブ栽培
実施例1の肥料を5kgと黒土2.5kgと腐葉土2.5kgを混ぜ、2月28日に、プラスチックの箱(W45cm×D35cm×H8cm)に入れ、これにミニカブの種を5cm間隔に数個ずつ40ヵ所蒔いた。5日後に発芽し、9日後に間引きして1ヵ所1株とし、49日後に40株全てを収穫することができた。ミニカブの直径は2〜3cm、長さが2〜3cmまで生長した。
Example 10 Mini Turnip Cultivation Mix 5kg of fertilizer of Example 1, 2.5kg of black soil, and 2.5kg of humus soil and put it in a plastic box (W45cm x D35cm x H8cm) on February 28th. Several 40 pieces were placed at 5 cm intervals. It germinated after 5 days, thinned out after 9 days to give one strain at one place, and all 40 strains could be harvested after 49 days. The mini-cube grew to 2 to 3 cm in diameter and 2 to 3 cm in length.
組合化成3号(片倉チッカリン(株)製)の肥料1kgと黒土5kgと腐葉土3kgを混ぜ、2月28日にミニカブの種を4cm間隔に数個ずつ40ヵ所蒔いた。5日後に発芽し、10日後に間引きして1ヵ所1株とし、45〜60日後までかけて35株を収穫することができたが、5株は収穫できる大きさに満たなかった。収穫したミニカブの直径は平均約1.9cm、長さが平均約2cmまで生長した。 We mixed 1 kg of fertilizer and 5 kg of black soil and 3 kg of humus soil from Kunsei Kasei No. 3 (manufactured by Katakura Chikkarin Co., Ltd.). It germinated after 5 days and thinned out after 10 days to give one strain at one place, and 35 strains could be harvested from 45 to 60 days later, but 5 strains were not large enough to be harvested. The harvested mini-cubs grew to an average diameter of about 1.9 cm and an average length of about 2 cm.
実施例11 クリサンセマム栽培
実施例1の肥料を5kgと黒土2.5kgと腐葉土2.5kgを混ぜ、プランター(W40cm×D20cm×H25cm)に入れ、高さ10cmほどのクリサンセマムの花2株を7月13日に移植した。1ヵ月後、クリサンセマムは高さが30cmほどに生長し、プランターからあふれるほど大きくなった。
Example 11 Chrysanthemum cultivation 5 kg of fertilizer of Example 1, 2.5 kg of black soil, and 2.5 kg of humus soil were mixed and placed in a planter (W40 cm × D20 cm × H25 cm). Transplanted on the day. A month later, Chrysanthemam grew to a height of about 30 cm and became so large that it overflowed from the planter.
組合化成3号(片倉チッカリン(株)製)の肥料1kgと黒土3kgと腐葉土3kgを混ぜ、高さ10cmほどの2株を7月13日に移植した。1ヵ月後、クリサンセマムは高さが25〜28cmほどに生長した。 1 kg of fertilizer, 3 kg of black soil, and 3 kg of humus soil from Union Chemical No. 3 (manufactured by Katakura Chikkarin Co., Ltd.) were mixed, and two strains about 10 cm in height were transplanted on July 13. One month later, Chrysanthemam grew to a height of about 25-28 cm.
実施例12 タマネギ栽培
5坪の畑に250kgの実施例2の肥料を撒き、12月21日にタマネギを移植し、4月5日に収穫した。
Example 12 Onion cultivation 250 kg of the fertilizer of Example 2 was sown in a 5 tsubo field, and the onion was transplanted on December 21 and harvested on April 5.
今回利用した畑では、過去10年間、組合化成7号(三菱化学(株)製)や、通常の牛糞、鶏糞を施しても直径10cmほどのタマネギしかできなかったが、実施例2の肥料を施したことで直径12〜15cmのタマネギができた。農薬は1度も使用しなかった。 In the field used this time, only the onion of about 10 cm in diameter was produced even if it applied union chemical No. 7 (Mitsubishi Chemical Co., Ltd.), normal cow dung, and chicken dung for the past 10 years, but the fertilizer of Example 2 was used. The onion of diameter 12-15cm was made by giving. No pesticides were used.
実施例13 イチゴ栽培
10坪の畑に500kgの実施例2の肥料を撒き、12月21日にイチゴを移植、3月21日に収穫した。この畑では過去10年間、組合化成7号(三菱化学(株)製)、通常の牛糞、鶏糞を施しても直径2cmほどのイチゴしかできなかったが、実施例2の肥料を施したことで例年の倍近い直径3〜4cmのイチゴが多数できた。例年は3、4回散布する殺虫殺菌剤オレート液剤(大塚化学(株)製)は1回だけ散布した。
Example 13 Strawberry cultivation 500 kg of the fertilizer of Example 2 was planted in a 10 tsubo field, and strawberries were transplanted on December 21 and harvested on March 21. In this field, union chemical 7 (manufactured by Mitsubishi Chemical Co., Ltd.), ordinary cow dung, and chicken dung, only a strawberry with a diameter of about 2 cm was produced, but the fertilizer of Example 2 was applied. Many strawberries with a diameter of 3 to 4 cm, which is almost twice the average year, were made. In the usual year, the insecticide bactericide Olate solution (Otsuka Chemical Co., Ltd.) sprayed three or four times was sprayed only once.
実施例14 グリンピース栽培
5坪の畑に250kgの実施例2の肥料を撒いて、12月28日にグリンピースを播種し、3月28日に収穫した。この畑では過去10年間、IB化成(三菱化学アグリ(株)製)や、通常の牛糞を施しても高さ約1.7mまでしか生長しなかったが、実施例2の肥料を施したことで高さ約2.2mまで生長した。例年4、5回散布する殺虫剤マラソン乳剤(日本農薬(株)製)は本発明の肥料を施すと2回のみの散布で済んだ。
Example 14 Green pea cultivation 250 kg of the fertilizer of Example 2 was sown in a 5 tsubo field, the green peas were sown on December 28, and harvested on March 28. In this field, IB Kasei (manufactured by Mitsubishi Chemical Aguri Co., Ltd.) and normal cow dung only grew to about 1.7m in height, but the fertilizer of Example 2 was applied. And grew to about 2.2m in height. The pesticide marathon emulsion (manufactured by Nippon Agricultural Chemicals Co., Ltd.) sprayed four or five times a year only needs to be sprayed only twice when the fertilizer of the present invention is applied.
実施例15 ほうれん草栽培
宮崎県綾町のビニールハウス内に、高さ0.7m×幅1.2m×長さ15mの台の上に、綾町の山林から採取した土を15cmの厚さに盛り、ほうれん草を15cm間隔で50列播種すると、5、6日後に発芽した。20日後、50列のうち15列に30kgの実施例3の肥料を、残りの35列に20kgの化学肥料くみあい尿素入り硫化リン安555(コープケミカル(株)製)を施肥した。その後、発芽から60日後には、化学肥料を施肥したほうれん草は5〜10cmの生長しか見られず、まだ収穫できる大きさになっていなかったのに比べて、実施例3の肥料を施肥したほうれん草は25〜30cmまでに生長し、収穫することができた。
Example 15 Spinach cultivation In a greenhouse in Aya-cho, Miyazaki Prefecture, a soil sampled from a mountain forest in Aya-machi is placed on a stand of 0.7 m height x 1.2 m width x 15 m length, and spinach is added. When 50 rows were seeded at intervals of 15 cm, germination occurred after 5 or 6 days. Twenty days later, 15 kg of the fertilizer of Example 3 was applied to 15 rows out of 50 rows, and 20 kg of the chemical fertilizer mixture was added to the remaining 35 rows, and phosphorus ammonium sulfide 555 (manufactured by Corp Chemical Co., Ltd.) was applied. Then, 60 days after germination, spinach fertilized with chemical fertilizer showed only 5-10 cm of growth and was not yet large enough to be harvested compared to spinach fertilized with fertilizer of Example 3. Grew to 25-30 cm and could be harvested.
実施例16 きゅうり栽培
4tの実施例4の肥料を鹿児島県指宿市の農地300坪に投入し、きゅうりを栽培した。9月2日、約20cmのきゅうり20株を移植し、10月20日に収穫した。きゅうりの長さは30〜40cm、直径が5〜8cmと、例年のものに比べて30%ほど大きく生長し、収穫量も例年より約20%増加した。害虫の発生はなく、農薬の散布は行わなかった。
Example 16 Cucumber cultivation 4 t of the fertilizer of Example 4 was added to 300 tsubo of farmland in Ibusuki City, Kagoshima Prefecture, and cucumbers were cultivated. On September 2, 20 cucumber strains of about 20 cm were transplanted and harvested on October 20. The length of the cucumbers was 30-40 cm and the diameter was 5-8 cm, growing 30% larger than that of the usual year, and the yield increased by about 20%. There was no generation of pests, and no pesticides were sprayed.
実施例17 ゴーヤ栽培
4tの実施例4の肥料を鹿児島県指宿市の農地300坪に投入し、ゴーヤを栽培した。9月5日、約20cmのゴーヤの苗10株を移植し、11月20日に収穫した。ゴーヤの実の長さは20〜30cm、直径が8〜10cmと、例年のものよりも約35%大きく生長し、収穫量も20%増加した。この間農薬は使用していないが、害虫の発生はなかった。
Example 17 Bitter gourd cultivation 4t of the fertilizer of Example 4 was introduced into 300 tsubo of farmland in Ibusuki City, Kagoshima Prefecture, and bitter gourd was grown. On September 5, 10 seedlings of bitter gourd approximately 20 cm were transplanted and harvested on November 20. The bitter gourd was 20-30 cm in length and 8-10 cm in diameter, growing about 35% larger than the average year, and the yield increased by 20%. Pesticides were not used during this period, but no pests were generated.
実施例18 なすび栽培
4tの実施例4の肥料を鹿児島県指宿市の農地300坪に投入し、9月5日に約15cmのなすびの苗を10株移植して11月15日に収穫した。長さが20〜30cm、直径が5〜8cmと、例年のものよりも約20%大きく生長し、収穫量も25%増加した。この間農薬は使用していないが、害虫の発生はなかった。
Example 18 Eggplant cultivation 4 t of the fertilizer of Example 4 was introduced into 300 tsubo of farmland in Ibusuki City, Kagoshima Prefecture. On September 5, 10 seedlings of approximately 15 cm of eggplant were transplanted and harvested on November 15. The length was 20-30 cm and the diameter was 5-8 cm, growing about 20% larger than the usual one, and the yield increased by 25%. Pesticides were not used during this period, but no pests were generated.
実施例19 レッドキャベツ栽培
6tの実施例5の肥料を鹿児島県指宿市の農地400坪に投入し、10月15日に10cmのレッドキャベツの苗を移植した。例年の外側の葉は移植66日後には15〜20cmであるのに対し、本発明の肥料を施したレッドキャベツの外側の葉は30〜45cmにまで大きく生長した。また、例年は4回行う農薬散布は1回も行なわなかった。
Example 19 Red Cabbage Cultivation 6 t of the fertilizer of Example 5 was introduced into 400 tsubo of farmland in Ibusuki City, Kagoshima Prefecture, and on October 15 a 10 cm red cabbage seedling was transplanted. The outer leaves of the normal year were 15-20 cm 66 days after transplanting, whereas the outer leaves of the red cabbage to which the fertilizer of the present invention was applied grew greatly to 30-45 cm. In addition, the pesticide spraying performed four times in the normal year was not performed once.
実施例20 ソラマメ栽培
12tの実施例5の肥料を鹿児島県指宿市の農地1000坪に8月25日に投入して、9月4日に2〜5cmのソラマメの苗を50cm間隔で移植した。例年の収穫予定より約1週間早い11月10日には1回目の収穫をすることができた。根腐れ病やアブラムシによる被害は例年の20%に対し、10%に抑えることができた。殺菌剤ダイセンステンレス(ダウケミカル日本(株)製)の散布も例年は4回行なうのに対して、2回で済んだ。補助剤アファーム乳剤(シンジェンタ ジャパン(株)製)は例年6回であるのに対し、4回使用した。
Example 20 Broad bean cultivation 12 t of the fertilizer of Example 5 was introduced on 1000 tsubo of farmland in Ibusuki City, Kagoshima Prefecture on August 25, and 2-5 cm broad bean seedlings were transplanted at 50 cm intervals on September 4. The first harvest was made on November 10, about one week earlier than the usual harvest schedule. The damage caused by root rot and aphids was reduced to 10% compared to 20% in the previous year. The spraying of the disinfectant Daisen Stainless (manufactured by Dow Chemical Japan Co., Ltd.) was performed twice, while it was performed four times a year. Adjuvant Affirm Emulsion (manufactured by Syngenta Japan Co., Ltd.) was used 4 times compared to 6 times per year.
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