JP2001026488A - Mineral enriched fertilizer - Google Patents

Mineral enriched fertilizer

Info

Publication number
JP2001026488A
JP2001026488A JP11233079A JP23307999A JP2001026488A JP 2001026488 A JP2001026488 A JP 2001026488A JP 11233079 A JP11233079 A JP 11233079A JP 23307999 A JP23307999 A JP 23307999A JP 2001026488 A JP2001026488 A JP 2001026488A
Authority
JP
Japan
Prior art keywords
mineral
organic waste
fertilizer
enriched fertilizer
shell
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
JP11233079A
Other languages
Japanese (ja)
Inventor
Sadako Ueda
貞子 上田
Yorihito Ueda
順仁 上田
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.)
GREEN CULTURE KK
Original Assignee
GREEN CULTURE KK
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 GREEN CULTURE KK filed Critical GREEN CULTURE KK
Priority to JP11233079A priority Critical patent/JP2001026488A/en
Publication of JP2001026488A publication Critical patent/JP2001026488A/en
Pending legal-status Critical Current

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Classifications

    • CCHEMISTRY; METALLURGY
    • C05FERTILISERS; MANUFACTURE THEREOF
    • C05FORGANIC FERTILISERS NOT COVERED BY SUBCLASSES C05B, C05C, e.g. FERTILISERS FROM WASTE OR REFUSE
    • C05F9/00Fertilisers from household or town refuse
    • C05F9/04Biological compost
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02ATECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
    • Y02A40/00Adaptation technologies in agriculture, forestry, livestock or agroalimentary production
    • Y02A40/10Adaptation technologies in agriculture, forestry, livestock or agroalimentary production in agriculture
    • Y02A40/20Fertilizers of biological origin, e.g. guano or fertilizers made from animal corpses
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02PCLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P20/00Technologies relating to chemical industry
    • Y02P20/141Feedstock
    • Y02P20/145Feedstock the feedstock being materials of biological origin

Landscapes

  • Health & Medical Sciences (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Molecular Biology (AREA)
  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Processing Of Solid Wastes (AREA)
  • Fertilizers (AREA)

Abstract

PROBLEM TO BE SOLVED: To provide a mineral enriched fertilizer which is free from environmental pollution, such as odors, in the composting process of organic waste, such as livestock waste, is alkaline, contains the minerals required by plants with good balance and has good quality. SOLUTION: This mineral enriched fertilizer is prepared by adding and mixing fossil seashells which are resulted from the embedment and deposition of various kinds of nekton, plankton, algae, seaweed, etc., consisting of calcareous materials, silicic acids, etc., and are the crystalline bodies having corrosive and soluble properties, to and with the organic waste, subjecting this mixture to adsorption of odors, etc., together with moisture control and subjecting the mixture to aerobic fermentation. As a result, the fertilizer which is free from the odors, etc., is weakly alkaline, contains the minerals with good balance and is adaptable to a recycling system of organic resources may be obtained. The fertilizer lends itself to the production structure of a resource circulating type and to the production of agricultural products keeping up with the standpoint of consumers, helping to provide the social structure of the next generation-oriented ideal area circulation type.

Description

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

【0001】[0001]

【発明の属する技術分野】本発明は、有機性廃棄物の臭
気等を抑えつつ好気性発酵させ、不足しがちなミネラル
を補充して利用価値を高めてなるミネラル強化肥料に関
する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a mineral-enriched fertilizer obtained by aerobically fermenting an organic waste while suppressing odor and the like, and replenishing a mineral which tends to be scarce, thereby increasing its utility value.

【0002】[0002]

【従来の技術】産業廃棄物及び一般廃棄物における有機
性廃棄物は、放置されると周辺の環境が様々な形態で汚
染されるから、何らかの処理が成され無害化されて廃棄
されるか、再利用される。この有機性廃棄物の中にあっ
て、扱い辛くかつ量的にも群を抜いて多いのが畜産廃棄
物、すなわち、糞尿である。この畜産廃棄物は、既に様
々な形態で再利用されている。例えば、乳用牛及び肉用
牛では充分に好気性発酵をして堆肥化する他、堆積だけ
の簡易的な堆肥化を行い、経営内で利用することが比較
的多い。また、豚では充分に好気性発酵をして堆肥化し
たり、乾燥しているが、農用地を持たない場合が大半で
あるから経営内で利用することがほとんどない。更に、
鶏では自然乾燥を含めた乾燥処理がほとんどで、経営外
利用となる。
2. Description of the Related Art Organic wastes in industrial wastes and general wastes are contaminated in various forms when left unattended. Reused. Among these organic wastes, livestock wastes, that is, manure, are the most difficult to handle and in terms of quantity. This livestock waste has already been reused in various forms. For example, in dairy and beef cattle, in addition to composting by sufficiently aerobic fermentation, simple composting of only sedimentation is performed and used relatively often in management. Pigs are sufficiently aerobic fermented to be composted or dried, but most of them do not have farmland, so they are rarely used in management. Furthermore,
Most chickens are dried, including natural drying, and are used outside of management.

【0003】そして、畜産廃棄物量は、牛、豚が85%
ほどを占めるから、その大半が簡易的なものを含めて堆
肥化されていることになる。牛、豚からの畜産廃棄物た
る糞尿は、畜舎から搬出された時点で、糞、糞+敷料、
糞+尿+敷料等の固形物の場合と、糞尿、糞尿+洗浄水
等のスラリーの場合とがあり、スラリーの場合は各種の
固液分離法により固形物化する。これらの固形物は、敷
料が充分あるときはそのまま堆肥化できるが、糞が主体
の分離固形物の場合や敷料があっても量が少なくそのま
ま堆肥化するのに水分が高い場合は、水分調整を行う必
要がある。この調整素材として、通常、藁、籾殻、おが
屑、バーク、ゼオライトやパーライトなどの無機質資材
が使用されている。いずれにしても、牛、豚に由来する
固形物の水分を70%程度にして、堆肥化施設にて好気
性発酵させて、堆肥化する。この堆肥化施設には、前述
のように、単に堆積させるだけの簡易的な堆肥化から、
完全な機械化を図り、充分に好気性発酵をさせた完全な
堆肥化まで種々ある。
The livestock waste amount is 85% for cattle and pigs.
Most of them are composted, including simple ones. Manure, which is livestock waste from cattle and pigs, is removed from the barn,
There are cases of solids such as feces + urine + litter, and cases of slurries such as manure, feces + washing water, and the like. In the case of slurries, they are solidified by various solid-liquid separation methods. These solids can be composted as they are when there is enough litter.However, in the case of separated solids mainly composed of feces or when there is only a small amount of litter and the moisture is high enough to be composted, moisture adjustment is required. Need to do. In general, inorganic materials such as straw, chaff, sawdust, bark, zeolite and perlite are used as the adjusting material. In any case, the water content of solid matter derived from cattle and pigs is reduced to about 70%, aerobic fermentation is performed in a composting facility, and composting is performed. As described above, this composting facility uses simple composting that simply deposits,
There are various types of composting that are fully mechanized and fully aerobic fermented.

【0004】このようにして生産された堆肥は、牛、豚
に由来する固形物や調整素材のうち、易分解性有機物は
好気性発酵し分解し、その過程で高温となり水分を蒸発
させると共に病原菌を死滅させ、安定化する。従って、
この充分に好気性発酵をさせた堆肥は、以後の悪臭、病
原菌、害虫の発生など環境汚染の原因とならず、農地、
緑地に施用すれば、良好な結果を得ることができるもの
となる。
[0004] The compost produced in this manner is an easily decomposable organic substance of solids and prepared materials derived from cattle and pigs, which undergoes aerobic fermentation and decomposes. To kill and stabilize. Therefore,
The compost that has been sufficiently aerobic fermented does not cause environmental pollution such as the generation of foul odors, pathogenic bacteria, and pests.
Good results can be obtained if applied to green spaces.

【0005】[0005]

【発明が解決しようとする課題】上記による堆肥は、環
境汚染の原因とならず、農地、緑地に施用すれば良好な
結果が得られて、極めて都合の良いものである。しかし
ながら、上記堆肥の生産地と消費地とのミスマッチか
ら、堆肥の余剰という新たな課題が発生して来ている。
また、牛、豚による廃棄物が堆肥化される過程での臭気
等の環境汚染に対しては不充分であり、特に簡易的な堆
肥化の場合に苦情が発生する。この臭気の面で調整素材
としてゼオライトを使用すれば、解消が可能となる。し
かし、ゼオライト自体は、酸性であり、堆肥内に含まれ
ているアンモニアを吸着することでアルカリサイドに働
くが、酸性サイドの多い日本の土壌に対する中和力は無
く、アンモニアが肥料として使用された後は、酸性サイ
ドのゼオライトが土中に残置されることになり、酸性サ
イドの多い日本の土壌における現状からベターでない。
The above-mentioned compost does not cause environmental pollution, and gives good results when applied to agricultural lands and green lands, and is extremely convenient. However, due to the mismatch between the compost production area and the consumption area, a new problem of surplus of compost has been generated.
In addition, it is not sufficient against environmental pollution such as odor in the process of composting waste by cattle and pigs, and complaints occur particularly in the case of simple composting. If zeolite is used as the adjusting material in terms of this odor, it can be eliminated. However, zeolite itself is acidic and works on the alkaline side by adsorbing ammonia contained in compost, but it has no neutralizing power on Japanese soil with many acidic sides, and ammonia was used as a fertilizer After that, the acidic side zeolite will be left in the soil, which is not better than the current situation in Japanese soil with many acidic sides.

【0006】更に、牛、豚による廃棄物に調整素材とし
て、藁、籾殻、おが屑、バーク、ゼオライトやパーライ
トなどの無機質資材が使用されて作られた堆肥であって
も、必要とするミネラル不足がある。すなわち、牛、豚
自体にミネラル不足が指摘されてから久しく、従って、
それに由来する廃棄物も当然ミネラル不足の状態であ
り、上記調整素材、特にゼオライトやパーライト等の無
機質資材が添加されていても、これらゼオライトやパー
ライトには、動植物が必要とするミネラルを全てバラン
ス良く含んでいるわけではないので、結局作られた堆肥
のミネラル不足を解消することは出来ていない。このよ
うなことから、必ずしも良質な堆肥とは言えず、運送費
用の面から堆肥の生産地と消費地とのミスマッチを解消
できず、余剰の堆肥の処分に奔走しなければならない状
況となっている。
[0006] Furthermore, even if the compost is made by using inorganic materials such as straw, rice husk, sawdust, bark, zeolite and perlite as waste materials for cattle and pigs, the required mineral deficiency will not occur. is there. That is, it has been a long time since the lack of minerals was pointed out in cattle and pigs,
The waste derived from it is naturally in a state of lack of minerals, and even if inorganic materials such as zeolite and pearlite are added to the above-mentioned adjusted materials, these zeolites and perlite have a good balance of all the minerals required by animals and plants. As it does not, it does not eliminate the mineral deficiency in the resulting compost. For this reason, compost is not always of good quality, and it is difficult to eliminate the mismatch between the compost production area and the consumption area in terms of transportation costs, and it is necessary to work hard to dispose of excess compost. I have.

【0007】そこで、本発明は、上記事情に鑑みてなさ
れたもので、畜産廃棄物等の有機性廃棄物が堆肥化され
る過程での臭気等の環境汚染が無く、アルカリであり、
しかも植物が必要とするミネラルをバランス良く含んだ
良質なミネラル強化肥料を提供することを課題とする。
Accordingly, the present invention has been made in view of the above circumstances, and has no environmental pollution such as odor in the process of composting organic waste such as livestock waste, and is alkaline.
Moreover, it is an object of the present invention to provide a high-quality mineral-enriched fertilizer containing minerals required by plants in a well-balanced manner.

【0008】[0008]

【課題を解決するための手段】本発明者らは、長年気体
や液体の吸着性を有すると共に自身がミネラルを供給で
きる貝化石の組成、性質について調査研究を続け、同時
に、家畜の飼育、飼育場の環境保全、家畜の廃棄物及び
その肥料としての利用についても調査研究を続けてき
た。その結果、飼育現場の環境保全を図り、特に家畜の
廃棄物を有効に処理し処分することが家畜の飼育にとっ
て不可欠であり、それには今まで環境汚染に繋がる公害
物とされていた家畜の糞尿を、貝化石の有するミネラル
効果、理化学的効果をプラスして好気性発酵効果により
堆肥化し、その堆肥を緑農地に還元し、環境ホルモンな
どの複合汚染の心配のないオーガニックで安心安全な良
質の農産物の生産を維持拡大し、資源循環型の生産構造
とし、真に消費者の立場に沿う農産物を生産して、次世
紀に向けた理想の地域循環型の社会構造とすることが理
に叶うことから、如何にして上記のような有機資源リサ
イクルシステムに乗せた肥料にするか、について鋭意研
究を重ねた。その成果として、家畜からの廃棄物に直ち
に貝化石を添加混合し、その混合物を好気性発酵させて
堆肥化すれば、臭気等が無く弱アルカリでミネラルをバ
ランス良く含んだ有機資源リサイクルシステムに乗せ易
い肥料を得られる、という貝化石の新たな利用側面を見
い出し、本発明に到達したのである。
Means for Solving the Problems The present inventors have long been investigating and studying the composition and properties of shell fossils that have gas and liquid absorptivity and can supply minerals at the same time. We have been conducting research on the environmental conservation of farms and the use of livestock waste and its use as fertilizer. As a result, it is essential to protect the environment of the breeding site, and in particular to effectively treat and dispose of livestock waste, for livestock breeding, including livestock manure, which has been regarded as a pollutant that has led to environmental pollution. Is composted by the aerobic fermentation effect by adding the mineral effect and physicochemical effect of shell fossils, and the compost is reduced to green farmland, and it is organic, safe and high quality without worrying about complex pollution such as environmental hormones. It makes sense to maintain and expand the production of agricultural products, create a recycling-oriented production structure, and produce agricultural products that truly meet the consumer's position, creating an ideal regional recycling-oriented social structure for the next century. Therefore, we have conducted intensive research on how to make a fertilizer on an organic resource recycling system as described above. As a result, if fossil shellfish is immediately added to and mixed with waste from livestock and the mixture is aerobically fermented and composted, it can be put on an organic resource recycling system that contains no odor, contains weak alkalis, and contains minerals in a well-balanced manner. The present inventors have found a new use aspect of shell fossils that can obtain easy fertilizer, and have reached the present invention.

【0009】すなわち、請求項1の発明は、石灰質や珪
酸等からなる各種ネクトン、プランクトン、藻類、海藻
等が埋没して堆積し、腐植溶性を帯びた結晶体である貝
化石を、有機性廃棄物に添加混合し、水分調整を兼ねる
と共に臭気等を吸着させ、該混合物を好気性発酵させて
なることを特徴とするミネラル強化肥料である。
[0009] That is, the invention of claim 1 is to dispose of shell fossils, which are humus-soluble crystals, in which various nekton, plankton, algae, seaweed, etc. made of calcareous or silicic acid are buried and deposited. It is a mineral-enriched fertilizer characterized by being added to and mixed with a substance, adjusting the water content, adsorbing odors and the like, and aerobically fermenting the mixture.

【0010】本発明のミネラル強化肥料は、気体や液体
の吸着性を有し自身はミネラル供与体となる貝化石を有
機性廃棄物に添加混合し、その混合物を好気性発酵させ
たものである。ここで、有機性廃棄物は、易分解性有機
成分を含む状態のものであれば、いかなるものでも良
く、特に限定がない。従って、易分解性有機成分を含ま
ない有機性廃棄物であっても、易分解性有機成分を含む
有機性廃棄物と混合すれば、易分解性有機成分を含む状
態のものであるから、ここで言う有機性廃棄物である。
但し、この有機性廃棄物は、最終的に肥料となるもので
あるから、肥料として適切でない有害物を含むものは最
終的に除去されることを条件として、使用可能である。
[0010] The mineral-enriched fertilizer of the present invention is obtained by adding and mixing shell fossils, which have a gas or liquid adsorbing property and are themselves a mineral donor, to organic waste and aerobic fermentation of the mixture. . Here, the organic waste is not particularly limited as long as it contains a readily decomposable organic component. Therefore, even if the organic waste does not contain the easily decomposable organic component, if it is mixed with the organic waste containing the easily decomposable organic component, the organic waste contains the easily decomposable organic component. It is organic waste.
However, since this organic waste finally becomes a fertilizer, it can be used on condition that those containing harmful substances that are not suitable as a fertilizer are finally removed.

【0011】上記有機性廃棄物を例示すれば、牛、豚、
鶏等の畜産廃棄物,下水汚泥、し尿系汚泥、食品産業排
水汚泥、養魚場底泥、アオコ・湖沼底泥等の有機汚泥
類,ビールかす、焼酎かす、おから、製糖残渣、果汁残
渣、コーヒーかす、茶かす、畜産加工残渣、水産加工残
渣等の食品加工残渣,パルプ廃液、バーク、おがくず、
チップダスト、剪定枝葉、バガス、籾がら、わら類等の
林産・植物残渣,ちゅう芥類(通称「生ごみ」)、都市
収集可燃ごみ、事業系生ごみ等の生活ごみ,などであ
る。
[0011] The above-mentioned organic waste is exemplified by cows, pigs,
Livestock waste such as chicken, sewage sludge, human waste sludge, food industry drainage sludge, fish farm bottom mud, organic sludge such as aoko and lake bottom mud, beer cake, shochu cake, okara, sugar-making residue, fruit juice residue, Food processing residues such as coffee grounds, tea grounds, livestock processing residues, fishery processing residues, pulp waste liquor, bark, sawdust,
Forest dust and plant residues such as chip dust, pruned branches and leaves, bagasse, chaff, straw, etc., garbage (commonly known as "garbage"), city-collectable combustible waste, and household waste such as business-related waste.

【0012】本発明に使用される貝化石は、考古学名で
は有孔虫化石、地質学名では石灰質砂岩であり、日本で
は富山県、石川県能登半島に良質なものが産する他、各
地に産するが、産地による限定がない。以下に順次説明
する特性を有する貝化石であれば、いかなる産地の貝化
石であっても良い。その主な産地における貝化石の分析
値は、表1のとおりである。
The shell fossils used in the present invention are foraminiferal fossils in the archaeological name and calcareous sandstone in the geological name. In Japan, high quality ones are produced in Noto Peninsula, Toyama Prefecture and Ishikawa Prefecture, and also in various places. However, there is no limitation according to the place of production. Shell fossils from any locality may be used as long as the shell fossils have the following characteristics. Table 1 shows the analytical values of shell fossils in the main production areas.

【0013】本発明の貝化石は、より具体的には、富山
県内の数カ所の採掘場において採掘された試料について
の下記定量分析表(表2)によるものと、これらの採掘
場から採掘された表2に示す成分の貝化石の類似品と、
である。
More specifically, the shell fossils of the present invention are based on the following quantitative analysis table (Table 2) of samples mined at several mines in Toyama Prefecture, and mined from these mines. An analog of the fossil shell of the ingredients shown in Table 2,
It is.

【0014】[0014]

【表1】 [Table 1]

【0015】[0015]

【表2】 [Table 2]

【0016】なお、上記富山県において採掘されている
貝化石は、日本の他の地域で採掘される貝化石の成分構
成と、分子集合形態が大きく異なり、特に珪素もある程
度含有するが、炭酸カルシウムの含有率が非常に高いこ
とが特徴となっている。また、この貝化石は、生体より
分泌されたアラゴライト形の結晶構造をとり、一定の有
効径を持つ小孔が無数に有り、これら無数の小孔には結
晶水を含む場合と、含まない場合とがあり、様々であ
る。これら結晶水を含まない小孔は、活性炭と同様に吸
着性能を有し、被吸着物質の種類によっては活性炭の数
十倍の能力を示す場合がある。したがって、臭気等を吸
着するには結晶水を含まない小孔の多い貝化石が有効で
あるから、後に詳述する加熱処理により結晶水を除去し
た熱処理貝化石が多く使用される。
The shell fossils mined in Toyama Prefecture differ greatly in the molecular composition from those of shell fossils mined in other parts of Japan. Is characterized by a very high content of. In addition, this fossil shell has an aragolite-type crystal structure secreted from the living body, and has numerous counts of pores having a certain effective diameter, and the countless pores include and do not include water of crystallization. There are various cases. These pores that do not contain water of crystallization have adsorption performance similar to activated carbon, and may exhibit tens of times the capacity of activated carbon depending on the type of the substance to be adsorbed. Accordingly, shell fossils having many small pores containing no crystallization water are effective for absorbing odors and the like, and heat-treated shell fossils from which crystallization water is removed by a heat treatment described later in detail are often used.

【0017】なお、貝化石の粒径は、特に限定がない
が、一般的に小さい方が良いが、貝化石の吸着性能、ミ
ネラル供給性能から、貝化石の粒径を主な留意点とする
必要がある。すなわち、貝化石の粒径が細かければ細か
いほど比表面積が大きくなり、ミネラル供給性能は良く
なるが、臭気等を吸着する小孔より小さい粒径では吸着
性能上意味がなく、粉砕コストも上昇する。逆に粒径が
あまり大きいと、比表面積が小さくなり過ぎて、ミネラ
ル供給性能及び吸着性能も低下し、加えて、有機性廃棄
物中に貝化石を均一に分散させることがむずかしくな
る。したがって、貝化石の粒径は好ましくは0.5μm
〜800μmの範囲、より好ましくは74μm〜400
μmの範囲であり、少なくとも上記0.5μm〜800
μmの粒度分布内であれば、有機性廃棄物に添加混合し
易く、かつ均一分散と臭気等吸着効果及びミネラル供給
効果とを同時にバランス良く満足し、その性能を維持す
ることが容易となる。
The particle size of the shell fossils is not particularly limited, but it is generally preferable that the particle size be small. However, the particle size of the shell fossils is mainly taken into consideration from the adsorption performance of the shell fossils and the mineral supply performance. There is a need. In other words, the smaller the particle size of the shell fossil, the greater the specific surface area and the better the mineral supply performance, but if the particle size is smaller than the small holes that adsorb odors, etc., there is no meaning in the adsorption performance, and the crushing cost also increases I do. On the other hand, if the particle size is too large, the specific surface area becomes too small, the mineral supply performance and the adsorption performance are also reduced, and in addition, it becomes difficult to uniformly disperse the fossil shellfish in the organic waste. Therefore, the particle size of the shell fossil is preferably 0.5 μm
800800 μm, more preferably 74 μm〜400.
μm, and at least 0.5 μm to 800 μm
When the particle size distribution is within μm, it can be easily added to and mixed with the organic waste, and the uniform dispersion, the effect of adsorbing odors and the like, and the effect of supplying minerals can be simultaneously satisfied in a well-balanced manner, and its performance can be easily maintained.

【0018】本発明のミネラル強化肥料は、貝化石を有
機性廃棄物に添加混合し、その混合物を好気性発酵させ
たものであるから、これら貝化石及び有機性廃棄物に他
のもの、例えば、卵の殻、貝殻、エビ・カニ類の殻、魚
の骨・ウロコ、陸上動物の骨などの生体に由来する生体
ミネラル、これらの生体ミネラルの加工品を補助剤及び
増量剤として添加して、性能強化を図ろうとすることは
本発明の範囲内である。すなわち、上記生体ミネラル及
びその加工品のうち、卵の殻について詳述すれば、98
%が無機質で、その無機質の約95%がCaCOで、
この他に少量のMgCOとCa(POとを含
み、この卵の殻を微粉末化し、電子顕微鏡で見ると、無
数のホールがあり、ポーラスな構造をしている。したが
って、卵の殻の粉末は、吸着性を有し、自身はCa、M
g、Pの供給体となることも可能であるから、貝化石の
補助剤及び増量剤となり得る。その他の生体ミネラル及
びその加工品についても、卵の殻の場合と事情はほぼ同
様であるから、吸着性を有すると共に自身がミネラル供
給体となり、貝化石の補助剤及び増量剤となり得る。
The mineral-enriched fertilizer of the present invention is obtained by adding and mixing shell fossils to organic waste and aerobically fermenting the mixture. Egg shells, shells, shrimp and crab shells, fish bones and scales, biological minerals derived from living organisms such as bones of terrestrial animals, and processed products of these biological minerals are added as auxiliary agents and bulking agents, Attempts to enhance performance are within the scope of the present invention. That is, among the above-mentioned biological minerals and their processed products, the egg shell is described in detail as 98%
% Is mineral, and about 95% of the mineral is CaCO 3 ,
In addition, it contains a small amount of MgCO 2 and Ca (PO 4 ) 2, and the egg shell is finely powdered. When viewed with an electron microscope, it has a myriad of holes and a porous structure. Therefore, the egg shell powder has an adsorptive property and is itself Ca, M
Since it can also be a supplier of g and P, it can be an adjuvant and a filler for shell fossils. Other biological minerals and processed products thereof are almost the same as those in the case of egg shells, so that they have an adsorptive property and themselves become a mineral supplier, and can be an auxiliary and extender for shell fossils.

【0019】更に、本発明のミネラル強化肥料としての
性状、すなわち、臭気等の環境汚染が無く、アルカリで
あり、しかも植物が必要とするミネラルをバランス良く
含むという性状を害しない範囲内で、他の薬剤などを添
加しても良く、この場合も無論本発明の範囲内である。
Further, the properties of the mineral-enriched fertilizer of the present invention, that is, the properties of being free from environmental pollution such as odors, being alkaline, and containing the minerals required by plants in a well-balanced manner, are not limited. May be added, and such a case is also within the scope of the present invention.

【0020】本発明のミネラル強化肥料は、有機性廃棄
物に貝化石を添加混合し、好気性発酵させて作られる。
その際、有機性廃棄物に含まれる易分解性有機成分の分
解による発熱が有機性廃棄物の温度を上昇させ、その温
度上昇により分解を担う微生物の活動条件を整え、その
結果一層活発な分解が進行するという因果の循環が起こ
っている。従って、本発明のミネラル強化肥料の製造に
あたり、上記の因果の循環が起こるような条件付けが必
要となる。同時に有機性廃棄物の易分解性有機成分は、
腐敗して悪臭や有害物を生成し易く、それを阻止しなけ
ればならない。以下、有機性廃棄物を好気性発酵させ肥
料を作る際の最も代表的な堆肥化について述べる。
The mineral-enriched fertilizer of the present invention is produced by adding and mixing shell fossils to organic waste and aerobic fermentation.
At this time, the heat generated by the decomposition of the easily decomposable organic components contained in the organic waste raises the temperature of the organic waste, and the temperature rise raises the operating conditions of the microorganisms responsible for the decomposition, resulting in more active decomposition. There is a causal cycle that progresses. Therefore, in the production of the mineral-enriched fertilizer of the present invention, it is necessary to condition such that the above-mentioned circulation of causation occurs. At the same time, easily decomposable organic components of organic waste
It easily rots and produces odors and harmful substances, which must be stopped. Hereinafter, the most typical composting for producing fertilizer by aerobic fermentation of organic waste will be described.

【0021】ミネラル強化肥料の具体的な製造は、有機
性廃棄物の性状により大きく変わる。従って、まず、有
機性廃棄物が堆肥原料となり得るか調査をし、有害物の
有無や易分解性有機成分の含有率など堆肥化するのに支
障がないことを確認する。次に、有機性廃棄物を前調整
する。この前調整は有機性廃棄物を順調に堆肥化させる
ための条件づくりである。従って、例えば、有機性廃棄
物が既に腐敗して悪臭や有害物を生成しているのであれ
ば、作業者の健康保持、周辺住民への影響から、直ちに
腐敗している有機性廃棄物に貝化石を添加混合して悪臭
や有害物を吸着することは、一つの前調整である。更
に、この有機性廃棄物が腐敗し易いものであれば、廃棄
される時点で直ちに貝化石を添加混合して、悪臭や有害
物を事前に吸着するようにしても差し支えない。一般的
には、設備面、運転面から、有機性廃棄物を堆積した
際、適度な空隙が生じ、空気が流通できるようにする前
調整の一環として貝化石の添加混合を行うことになる。
The specific production of mineral-enriched fertilizers will vary greatly depending on the nature of the organic waste. Therefore, first, it is investigated whether or not organic waste can be used as a compost material, and it is confirmed that there is no obstacle to composting such as presence of harmful substances and content of easily decomposable organic components. Next, the organic waste is preconditioned. This preconditioning is the creation of conditions for composting organic waste smoothly. Therefore, for example, if the organic waste has already spoiled to produce odors and harmful substances, the spoilage of the organic waste should be immediately changed to maintain the health of workers and affect the local residents. Adding and mixing fossils to adsorb odors and harmful substances is one precondition. Further, if the organic waste is easily perishable, fossil shellfish may be added and mixed immediately at the time of disposal to adsorb odors and harmful substances in advance. Generally, when organic waste is deposited from the viewpoint of facilities and operation, appropriate voids are generated, and addition and mixing of shell fossils is performed as part of preconditioning for allowing air to flow.

【0022】この前調整は、例えば、敷料無しの畜産廃
棄物のように水分過剰の場合は、空隙がなく堆積するこ
とも出来ないから、藁、もみ殻のように、空隙に富み水
分の少ない調整素材を水分調整として添加混合して、適
度な空隙を保持して堆積できるようにする。逆に、乾燥
が進んだ野菜くずのような有機性廃棄物の場合には、堆
積はできるが空隙が有りすぎ水分不足で堆肥化しないか
ら、水を添加し加圧して適度な空隙と水分とを付与す
る。なお、前調整で使用される調整素材は、最終的にミ
ネラル強化肥料となるから、調整素材自体も農地、緑地
に還元できるものでなければならい。
In this pre-adjustment, for example, in the case of excess moisture such as livestock waste without litter, there is no void and no accumulation is possible. The adjustment material is added and mixed as a water content adjustment so that an appropriate void can be maintained and deposited. Conversely, in the case of organic waste such as dried vegetable waste, it can be deposited, but there are too many voids and there is insufficient moisture to prevent composting. Is given. In addition, since the adjustment material used in the pre-adjustment is finally a mineral-enriched fertilizer, the adjustment material itself must be reducible to farmland and green space.

【0023】この前調整時、上記のように、有機性廃棄
物に貝化石が添加されるが、その添加量は、前調整後の
有機性廃棄物に対して、0.2〜15重量%の貝化石が
添加されることが好ましい。0.2重量%未満では貝化
石を添加したことによる効果が確認しづらく、15重量
%を越えるとコスト上昇に見合う効果が期待しづらい。
なお、貝化石は当然に前調整時の調整素材を兼ね得る。
すなわち、貝化石は、上述のように小孔が無数にありポ
ーラスであり、吸湿性もあるから十分調整素材を兼ねる
ことができるのである。従って、有機性廃棄物に貝化石
を添加する際、調整素材としての機能も考慮してその貝
化石及びその他の調整素材の添加量を決める必要があ
る。いずれにしても、貝化石は、最終的にミネラル強化
肥料となる前に、有機性廃棄物に添加される必要があ
る。そのことで、有機性廃棄物による臭気、有害物を吸
着させ、他に影響を及ぼさないように出来るからであ
る。
At the time of this pre-conditioning, as described above, shell fossils are added to the organic waste, and the amount of addition is 0.2 to 15% by weight based on the pre-conditioning organic waste. It is preferable to add the shell fossils. If the content is less than 0.2% by weight, it is difficult to confirm the effect of adding the shell fossil, and if it exceeds 15% by weight, it is difficult to expect an effect corresponding to the cost increase.
Note that the shell fossils can naturally also serve as the adjustment material at the time of the pre-adjustment.
That is, shell fossils have a myriad of small holes and are porous as described above, and also have a hygroscopic property, so that they can also serve as a material for adjustment. Therefore, when adding the shell fossil to the organic waste, it is necessary to determine the addition amount of the shell fossil and other adjustment materials in consideration of the function as the adjustment material. In any case, the shell fossils need to be added to the organic waste before finally becoming a mineral-enriched fertilizer. Thereby, odors and harmful substances due to the organic waste can be adsorbed so as not to affect others.

【0024】前調整後の有機性廃棄物は、易分解性有機
物に富み、適度の通気性があり、充分な水分もあるか
ら、堆積すれば自然通気により、あるいは易分解性有機
物が多い場合は強制通風により、好気性発酵が始まり、
上記した因果の循環が進行し、適度の切り返しにより発
酵が更に進み、温度上昇し水分が除去され、病源菌や害
虫も死滅して、一次発酵が終了する。施用の状況に応じ
て、一次発酵が終了した未熟ミネラル強化肥料をそのま
ま農地、緑地に施用しても良いし、更に、二次発酵させ
完熟させて完全なミネラル強化肥料としてから、農地、
緑地に施用しても良い。
The organic waste after the preconditioning is rich in easily decomposable organic substances, has a moderate air permeability, and has a sufficient amount of water. Due to forced ventilation, aerobic fermentation begins,
Circulation of the above-mentioned causal effect proceeds, fermentation further proceeds by appropriate switching, temperature rises, water is removed, pathogenic bacteria and pests are killed, and primary fermentation is terminated. Depending on the situation of application, the immature mineral-enriched fertilizer whose primary fermentation has been completed may be directly applied to agricultural land and green space, or may be further fermented and fully matured to form a complete mineral-enriched fertilizer,
May be applied to green spaces.

【0025】このミネラル強化肥料は、有機性廃棄物に
貝化石を添加混合したものであるから、その時点で貝化
石の有する吸着性を発揮し、有機性廃棄物からの臭気、
有害物を吸着し、水分も吸着する。従って、有機性廃棄
物の前調整時の調整素材を兼ね、発酵の際貝化石の有す
る無数の孔は発酵菌の恰好の棲家となり、発酵を促進さ
せるように働く。このミネラル強化肥料を農地、緑地に
施用すれば、ミネラルバランスの良い肥料を撒いたこと
になり、添加した貝化石は弱アルカリであるから、酸性
土壌を中和し土壌改良をしつつ、良好な作物を収穫でき
る。
Since the mineral-enriched fertilizer is a mixture of organic waste and fossil shellfish, the fertilizer exhibits the adsorptive properties of the shell fossil at that time, and the odor from the organic waste,
Adsorbs harmful substances and adsorbs moisture. Therefore, the myriad pores of the shell fossils during fermentation also serve as a conditioning material at the time of preconditioning of the organic waste, and serve as a suitable habitat for the fermenting fungi and promote the fermentation. If this mineral-enriched fertilizer is applied to agricultural lands and green lands, it means that fertilizer with good mineral balance has been scattered, and the added shell fossils are weakly alkaline. Crop can be harvested.

【0026】請求項2の発明は、有機性廃棄物を好気性
発酵させてなる発酵物に、石灰質や珪酸等からなる各種
ネクトン、プランクトン、藻類、海藻等が埋没して堆積
し腐植溶性を帯びた結晶体である貝化石を、混合してな
ることを特徴とするミネラル強化肥料である。
According to a second aspect of the present invention, in a fermented product obtained by aerobic fermentation of an organic waste, various nekton, plankton, algae, seaweed and the like made of calcareous or silicic acid are buried and deposited to have humus solubility. It is a mineral-enriched fertilizer characterized by mixing shell fossils, which are crystalline materials.

【0027】本請求項のミネラル強化肥料は、有機性廃
棄物を好気性発酵させてなる発酵物に前記貝化石を混合
して得たものでも良いことを示し、この時の発酵物に対
して0.5〜30重量%の貝化石を混合する。0.5重
量%未満では貝化石を添加したことによる効果が確認し
づらく、30重量%を越えるとコスト上昇に見合う効果
が期待しづらい。なお、このミネラル強化肥料は、上記
の請求項1の発明に係るミネラル強化肥料とほぼ同様の
ものであり、有機性廃棄物の易分解性有機物が比較的安
定し、臭気や有害物を出さないようなものである場合に
有効である。
[0027] The mineral-enriched fertilizer of the present invention indicates that a fermented product obtained by aerobic fermentation of an organic waste and the shell fossil may be mixed to obtain the fermented product. Mix 0.5-30% by weight of shell fossils. If the amount is less than 0.5% by weight, it is difficult to confirm the effect of adding the shell fossils, and if it exceeds 30% by weight, it is difficult to expect an effect corresponding to the cost increase. The mineral-enriched fertilizer is substantially the same as the mineral-enriched fertilizer according to the first aspect of the present invention. The easily decomposable organic matter of the organic waste is relatively stable and does not emit odors and harmful substances. It is effective when it is something like this.

【0028】請求項3の発明は、病原菌に汚染されてい
ない土と、有機性廃棄物と、石灰質や珪酸等からなる各
種ネクトン、プランクトン、藻類、海藻等が埋没して堆
積し腐植溶性を帯びた結晶体である貝化石とを混合し、
水分調整を兼ねると共に臭気等を吸着させ、該混合物を
好気性発酵させてなることを特徴とするミネラル強化肥
料である。
According to the invention of claim 3, the soil not contaminated by the pathogenic bacteria, the organic waste, and various nekton, plankton, algae, seaweed, etc. made of calcareous or silicic acid are buried and deposited to have humus solubility. Mixed with the shell fossils
The mineral-enriched fertilizer is characterized in that the mixture is aerobic fermented while also controlling moisture and adsorbing odor and the like.

【0029】本請求項のミネラル強化肥料は、通称「ボ
カシ肥」と呼ばれるもので、土に各種の有機性廃棄物を
混合して堆積腐熟させ、農地に施用する前に有機性廃棄
物に由来する肥料養分を土に馴染ませることにより、優
れた理化学性と微生物性を備えた肥料である。ここで、
病原菌に汚染されていない土として、通常山土が使用さ
れるが、道路法面の道路わきに堆積した「霜崩れ」なる
土が最高とされる。この「霜崩れ」なる上は、厳寒時に
凍結して法面に浮き上がった霜柱が凍結融解し、陽光で
崩れ落ちたサラサラな土を言い、べとつかず吸水性と透
水性に優れた土である。その外上記の土としては、飼料
作物を栽培しているため比較的病原菌に汚染されている
ことの少ない畑土、水田の土、浄水場発生土、砕石場に
おける発生土などが使用される。
The mineral-enriched fertilizer according to the present invention is commonly called "bokashi manure", and is mixed with various organic wastes in soil, sedimented and ripened, and is derived from organic wastes before being applied to agricultural land. It is a fertilizer with excellent physicochemical and microbial properties by adapting fertilizer nutrients to the soil. here,
Mountain soil is normally used as soil that is not contaminated with pathogenic bacteria, but the soil that has accumulated on the side of the road, called "frost lands," is considered the highest. Above this "frost collapse", the frost pillar that was frozen in the severe cold and floated on the slope was frozen and thawed, and it was a smooth soil that collapsed in sunlight and was excellent in water absorption and permeability without stickiness. In addition, as the above-mentioned soil, field soil, paddy soil, soil from a water purification plant, soil from a quarry, etc., which are relatively less contaminated with pathogenic bacteria since feed crops are cultivated, are used.

【0030】ここでの有機性廃棄物は、上記した有機性
廃棄物を使用できるが、その際米糠を含有させるのが良
い。その理由は、米糠が微生物の繁殖を促し、発酵促進
効果が大きいからである。その米糠添加量は土に対し
て、少なくとも1重量%以上を添加する必要がある。上
限は常識的に15重量%程度である。米糠以外の有機性
廃棄物は、前述の通りものを使用するが、その添加量は
施用する作物により変えた方が良い。更に、貝化石は、
前述の通りものを使用し、貝化石の有する吸着性を発揮
し、有機性廃棄物からの臭気、有害物を吸着し水分も吸
着し、更に発酵の際貝化石の有する無数の孔は発酵菌の
恰好の棲家となり、発酵を促進させるように働く。
As the organic waste here, the above-mentioned organic waste can be used, and in this case, rice bran is preferably contained. The reason is that rice bran promotes the propagation of microorganisms and has a large fermentation promoting effect. It is necessary to add at least 1% by weight or more of rice bran to soil. The upper limit is generally about 15% by weight. As the organic waste other than rice bran, the same as described above is used, but the amount of addition should be changed depending on the crop to be applied. In addition, shell fossils
As described above, the adsorbent of shell fossils is used, and it absorbs odors and harmful substances from organic wastes and adsorbs moisture. It works to promote fermentation.

【0031】そして、病原菌に汚染されていない土と、
米糠を含有する有機性廃棄物と、貝化石と、更に種菌と
して既に出来上がっているミネラル強化肥料とを混合
し、水分調整しながら堆積して、冬期で3〜4か月間、
夏期で1.5か月間ほど自然通気乃至強制通気させれ
ば、通称「ボカシ肥」と呼ばれるミネラル強化肥料が出
来る。このミネラル強化肥料を農地、緑地に施用すれ
ば、ミネラルバランスの良い肥料を撒いたことになり、
添加した貝化石は弱アルカリであるから、酸性土壌を中
和し土壌改良をしつつ、更に害虫からの被害を抑制し良
好な作物を収穫できる。なお、堆肥を生産する過程で病
原菌に汚染されていない土を添加しても、「ボカシ肥」
に類似したミネラル強化肥料が出来る。
And soil not contaminated by pathogenic bacteria;
Organic waste containing rice bran, fossil shellfish, and mineral-enriched fertilizer that has already been made as a seed fungus are mixed and deposited while adjusting the water content. In winter, 3-4 months,
If natural ventilation or forced ventilation is performed for about 1.5 months in summer, a mineral-enriched fertilizer commonly called "bokashi manure" can be obtained. If this mineral-enriched fertilizer is applied to farmland and green space, it means that fertilizer with good mineral balance is scattered,
Since the added shell fossils are weakly alkaline, it is possible to neutralize acidic soil and improve the soil while also suppressing damage from pests and harvesting good crops. In addition, even if soil not contaminated by pathogenic bacteria is added during the process of compost production, "Bokashi manure"
A mineral-enriched fertilizer similar to that of.

【0032】請求項4の発明は、病原菌に汚染されてい
ない土と有機性廃棄物とを混合し、水分調整を兼ねると
共に臭気等を吸着させ、該混合物を好気性発酵させてな
る混合発酵物に、石灰質や珪酸等からなる各種ネクト
ン、プランクトン、藻類、海藻等が埋没して堆積し腐植
溶性を帯びた結晶体である貝化石を混合してなることを
特徴とするミネラル強化肥料である。。
According to a fourth aspect of the present invention, there is provided a mixed fermented product obtained by mixing soil not contaminated with pathogenic bacteria with organic waste, adjusting the water content, adsorbing odors, and aerobically fermenting the mixture. A mineral-enriched fertilizer comprising a mixture of fossil shells, which are humus-soluble crystalline materials, in which various nekton, plankton, algae, seaweed, and the like made of calcareous or silicic acid are buried and deposited. .

【0033】本請求項のミネラル強化肥料は、病原菌に
汚染されていない土と、有機性廃棄物との混合物を好気
性発酵させてなる混合発酵物に、前記貝化石を混合して
得たものでも良いことを示し、この時の混合発酵物に対
して0.25〜10重量%の貝化石を混合する。0.2
5重量%未満では貝化石を添加したことによる効果が確
認しづらく、10重量%を越えるとコスト上昇に見合う
効果が期待しづらい。なお、このミネラル強化肥料は、
上記の請求項3の発明に係るミネラル強化肥料とほぼ同
様のものであり、有機性廃棄物の易分解性有機物が比較
的安定し、臭気や有害物を出さないようなものである場
合に有効である。
The mineral-enriched fertilizer according to the present invention is obtained by mixing the fossil shell with a mixed fermentation product obtained by aerobic fermentation of a mixture of soil not contaminated with pathogenic bacteria and organic waste. It is shown that the mixture fermented product is mixed with 0.25 to 10% by weight of shell fossil. 0.2
If it is less than 5% by weight, the effect of adding shell fossils is difficult to confirm, and if it exceeds 10% by weight, it is difficult to expect an effect commensurate with the cost increase. In addition, this mineral-enriched fertilizer
It is almost the same as the mineral-enriched fertilizer according to the third aspect of the invention, and is effective when the easily decomposable organic matter of the organic waste is relatively stable and does not emit odor or harmful substances. It is.

【0034】請求項5の発明は、前記貝化石は、その小
孔に含まれている結晶水が加熱処理により除去されてい
るミネラル強化肥料である。
According to a fifth aspect of the present invention, the shell fossil is a mineral-enriched fertilizer in which water of crystallization contained in its pores is removed by heat treatment.

【0035】結晶水が加熱処理により除去されている貝
化石、すなわち、熱処理貝化石は、未熱処理の貝化石を
150℃〜300℃の範囲内で加熱処理され、小孔に含
まれている結晶水がほぼ完全に除去され、吸着性能が高
められていると共に、加熱処理により未熱処理の貝化石
に付着している雑菌が死滅している。すなわち、この熱
処理貝化石は、小孔に含まれている結晶水を除去した
分、吸着性能が向上し、更に雑菌を死滅させているか
ら、好気性発酵の際の悪影響がない。
Shell fossils from which water of crystallization has been removed by heat treatment, that is, heat-treated shell fossils, are obtained by heat-treating unheated shell fossils in the range of 150 ° C. to 300 ° C. Water has been almost completely removed, the adsorption performance has been enhanced, and heat treatment has killed various bacteria adhering to unheated shell fossils. In other words, the heat-treated shell fossil has improved adsorption performance and further kills various bacteria by removing the water of crystallization contained in the pores, so that there is no adverse effect during aerobic fermentation.

【0036】[0036]

【発明の実施の形態】以下、本発明の実施の態様につい
て詳述する。まず、上記構成になるミネラル強化肥料の
種々の効果を確認するための調査及び試験を行ったの
で、その状況を説明する。 〔実施例1〕まず、貝化石の脱臭性についての実験室的
な試験を行う。試験の詳細は以下の通りである。1lの
各バッグに0.5gの粉末状の貝化石をそれぞれ入れ、
更に簡易的に濃度調整をした各臭気ガス、すなわち、ア
ンモニア、アセトアルデヒド、酢酸、硫化水素、トリメ
チルアミンを封入し、各臭気ガスの初期濃度、30分
後、60分後の濃度をガステック社製の各臭気ガス用の
検知管にて測定する。なお、アンモニア、アセトアルデ
ヒド、酢酸については、対比のために活性炭についても
同じ方法により測定する。その結果を表3に示す。
DESCRIPTION OF THE PREFERRED EMBODIMENTS Embodiments of the present invention will be described below in detail. First, investigations and tests for confirming various effects of the mineral-enriched fertilizer having the above configuration were performed, and the situation will be described. Example 1 First, a laboratory test is performed on the deodorizing properties of shell fossils. The details of the test are as follows. Put 0.5 g of powdered shell fossils in each 1 liter bag,
Further, each odor gas whose concentration was simply adjusted, that is, ammonia, acetaldehyde, acetic acid, hydrogen sulfide, and trimethylamine were sealed, and the initial concentration of each odor gas, after 30 minutes and after 60 minutes, was measured by Gas Tech. It is measured with the detector tube for each odor gas. In addition, ammonia, acetaldehyde, and acetic acid are also measured for activated carbon by the same method for comparison. Table 3 shows the results.

【0037】[0037]

【表3】 [Table 3]

【0038】表3によれば、アセトアルデヒド以外の臭
気ガスについて充分な除去性が認められ、その除去能力
は活性炭とほぼ同等である。
According to Table 3, sufficient odor gas other than acetaldehyde can be removed, and the odor gas has almost the same removal ability as activated carbon.

【0039】〔実施例2〕次に、実際規模での測定を行
う。1日牛1頭あたり500gの貝化石を牛床、バンク
リーナー、尿溝、通路に散布し、上記臭気ガスの内最も
影響のあるアンモニアについて、散布前、散布直後、散
布1週間後、散布2週間後、散布3週間後の濃度をガス
テック社製のNo.3Lの検知管にて測定する。試験結
果を表4に示す。
[Embodiment 2] Next, measurement on an actual scale is performed. Spray 500 g of fossil shellfish per cow per day on cow beds, bank cleaners, urinary ditches, and passages. For the most influential ammonia among the above odor gases, before spraying, immediately after spraying, one week after spraying, spraying 2 After three weeks, the concentration after three weeks of spraying was measured using No. Measure with a 3L detector tube. Table 4 shows the test results.

【0040】[0040]

【表4】 [Table 4]

【0041】アンモニア臭は、2ppm以下になると、
普通の人では臭気を感じなくなるから、貝化石を散布す
ることで、ほぼアンモニア臭を感じない程度までにする
ことが出来た。
When the ammonia odor becomes 2 ppm or less,
Ordinary people do not feel the odor, so spraying the shell fossils reduced the odor to almost no ammonia odor.

【0042】〔実施例3〕100坪の鶏舎内に敷藁を
し、その上に900kgの粉末状貝化石を散布し、50
00羽の雛を入れ、49日後、55日後の鶏舎内のアン
モニア濃度をガステック社製のNo.3Lの検知管にて
測定する。 〔比較例1〕粉末状貝化石の散布無しの状態で、実施例
3と同様に鶏舎内のアンモニア濃度をガステック社製の
No.3Lの検知管にて測定する。試験結果を表5に示
す。
Example 3 A straw was placed in a poultry house of 100 tsubo and 900 kg of powdered shell fossils were sprayed on the straw.
No. 00 chicks were placed, and the ammonia concentration in the poultry house after 49 days and 55 days was measured using a No. Measure with a 3L detector tube. [Comparative Example 1] In the state where the powdered shell fossils were not sprayed, the ammonia concentration in the poultry house was measured by Gastech No. Measure with a 3L detector tube. Table 5 shows the test results.

【0043】[0043]

【表5】 [Table 5]

【0044】1坪あたり9kgの粉末状貝化石を散布す
ることにより、通算で49日後、55日後でも2ppm
以下であり、極めて良好な環境を提供できる。その後敷
藁と共に堆肥化可能である。
By spraying 9 kg of powdered shell fossils per square meter, 2 ppm even after 49 days and 55 days in total
The following is an extremely favorable environment. It can then be composted with the litter.

【0045】〔実施例4〕牛舎におがくずの敷料を敷き
詰め、その上で肉牛を飼い糞尿を敷料に吸収させたもの
を搬出時に約500kgとり、これを堆肥原料とした。
この時の堆肥原料の水分は3か所の平均で71%であっ
た。この堆肥原料に20kg(添加率4重量%)の粉末
状貝化石を添加混合し、小山状に堆積し2日おきに切り
返しを行い、2か月間(3、4月)発酵させてミネラル
強化肥料とした。このミネラル強化肥料を以下の飼料作
物につき施用する。 1.土壌概要及び試験規模 M牧場は弱酸性の火山性黒色土 30m×1 N牧場は弱酸性の火山性赤色土 30m×1 2.供試飼料作物 デントコーン 3.品種・播種量 M牧場は、デントコーンのゴールデンデント(110)
を4kg/10a播く。 N牧場は、デントコーンのホワイトデント(125)を
5kg/10a播く。 4.播種時期 M牧場 5月13日 N牧場 5月11日 5.施肥内容(10aあたり換算) M牧場のデントコーン 4月下旬に1.5t N牧場のデントコーン 4月下旬に1.5t 6.刈取日 M牧場のデントコーン 9月5日 N牧場のデントコーン 9月2日 7.収量調査 10aあたりの生草量及び乾物量に換算する。 〔比較例2〕実施例4と同様の堆肥原料を貝化石粉末を
混合することなく、そのまま同じように発酵させて堆肥
とした。この堆肥を実施例4と同様に施用して得られた
収穫物のデントコーンにつき、10aあたりの生草量及
び乾物量に換算する。 〔実施例5〕実施例4のミネラル強化肥料をM牧場の弱
酸性の火山性黒色土30m×1にてリードカナリーつ
き施用する。このリードカナリーは永年牧草で、4、5
年経過したものである。施肥内容(10aあたり換算)
は4月下旬に実施例4のミネラル強化肥料を1.5tで
施用した。刈取日は6月4日、7月29日の2回であ
る。収量調査は10aあたりの生草量及び乾物量に換算
する。 〔比較例3〕実施例4と同様の堆肥原料を貝化石粉末を
混合することなく、そのまま同じように発酵させて堆肥
とした。この堆肥を実施例5と同様に施用して得られた
収穫物のリードカナリーにつき10aあたりの生草量及
び乾物量に換算する。以上の結果を表6、7に示す。
Example 4 A beef barn was laid with a litter of sawdust, a beef was raised on the litter, and manure was absorbed into the litter. About 500 kg of the litter was taken out and used as a compost material.
At this time, the water content of the compost material was 71% on average at three locations. 20 kg (addition rate 4% by weight) of powdered shell fossils are added to and mixed with this compost material, piled up in a mound, cut back every two days, and fermented for two months (March / April) to be mineral-enriched fertilizer. And This mineral-enriched fertilizer is applied to the following forage crops. 1. 1. Outline of soil and test scale M ranch is a weakly acidic volcanic black soil 30 m 2 × 1 N ranch is a weakly acidic volcanic red soil 30 m 2 × 1 2. Test feed crop Dent corn 3. Varieties and sowing amount M ranch is a dent corn golden dent (110)
4 kg / 10a. N ranch seeds 5 kg / 10a of white dent (125) of dent corn. 4. Seeding time M ranch May 13 N ranch May 11 5. 5. Fertilizer application (converted per 10a) Dent corn at M ranch 1.5t in late April Dent corn at N ranch 1.5t in late April 6. Harvesting date Dent corn at Ranch September 5 Dent corn at Ranch September 2 7. Yield survey Converted to the amount of fresh grass and dry matter per 10a. [Comparative Example 2] The same compost raw material as in Example 4 was fermented in the same manner without mixing with shell fossil powder to obtain a compost. This compost is converted to the amount of fresh grass and the amount of dry matter per 10a for the dent corn of the harvest obtained by applying the compost in the same manner as in Example 4. Example 5 The mineral-enriched fertilizer of Example 4 is applied with a lead canary on a weakly acidic volcanic black soil of 30 m 2 × 1 at M Farm. This lead canary is a perennial pasture, 4,5
Years have passed. Fertilizer content (converted per 10a)
Applied the mineral-enriched fertilizer of Example 4 at 1.5 t in late April. The harvest date is twice on June 4 and July 29. The yield survey is converted into the amount of fresh grass and the amount of dry matter per 10a. [Comparative Example 3] The same compost raw material as in Example 4 was fermented in the same manner without mixing with shell fossil powder to obtain a compost. This compost is converted to the amount of fresh grass and the amount of dry matter per 10a for the lead canary obtained by applying the compost in the same manner as in Example 5. Tables 6 and 7 show the above results.

【0046】[0046]

【表6】 [Table 6]

【0047】[0047]

【表7】 [Table 7]

【0048】表6、7によれば、デントコーンの生草量
及び乾物量並びにリードカナリーの生草量及び乾物量と
もに、単なる堆肥よりもミネラル強化肥料の方がかなり
多く収穫できた。
According to Tables 6 and 7, both the amount of fresh grass and dry matter of dent corn and the amount of fresh grass and dry matter of reed canary can be harvested considerably more with mineral-enriched fertilizer than with simple compost.

【0049】〔実施例6〕富山県立山産の山土50(容
量%、以下同じ)、実施例4の堆肥原料30、鶏糞8、
米ぬか8、粉末状貝化石4を良く混合し、水分60%程
度になるように調整する。小山となるように堆積し、空
気穴を明け、1週間に1回の割合で切り返し、10週間
(3〜5月)間発酵させてミネラル強化肥料(ボカシ
肥)とした。このミネラル強化肥料を以下の飼料作物に
つき施用する。 1.土壌概要及び試験規模 表層多腐植黒ぼく土壌 30m×1 2.供試飼料作物 小松菜を先に栽培し、収穫後ほうれん草を植えて収穫す
る。 3.播種時期 小松菜は、5月28日に播種し7月15日に収穫する。
ほうれん草は、9月25日に播種し11月10日に収穫
する。 4.施肥内容(10aあたり換算) 4月下旬に1.5t 5.収量調査 小松菜及びほうれん草の各30株あたりの総重量を測定
し、更に、収穫後の土壌のpH値を測定する。 〔比較例4〕粉末状貝化石を添加しないで実施例6と同
様のミネラル強化肥料を作り、実施例6と同様の条件で
小松菜及びほうれん草を栽培し収穫し、収量調査を行
う。以上の結果を表8に示す。
Example 6 Mountain soil 50 (volume%, hereinafter the same) from Tateyama, Toyama Prefecture, compost raw material 30 of Example 4, chicken dung 8,
The rice bran 8 and the powdered shell fossil 4 are mixed well and adjusted so that the water content is about 60%. It was piled up to form a hill, air holes were opened, cut back once a week, and fermented for 10 weeks (3 to 5 months) to obtain a mineral-enriched fertilizer (bokashi manure). This mineral-enriched fertilizer is applied to the following forage crops. 1. 1. Outline of soil and test scale Surface layer humus Kuroboku soil 30m 2 × 1 2. Test feed crop Komatsuna is first cultivated, and after harvest, spinach is planted and harvested. 3. Sowing time Komatsuna is sown on May 28 and harvested on July 15.
Spinach is sown on September 25 and harvested on November 10. 4. Fertilizer application (converted per 10a) 1.5t in late April 5. Yield survey The total weight of each of the 30 strains of Komatsuna and spinach is measured, and the pH value of the soil after harvest is measured. [Comparative Example 4] A mineral-enriched fertilizer similar to that of Example 6 was prepared without adding powdery shellfish fossils, and cultivated and harvested komatsuna and spinach under the same conditions as in Example 6, and investigated the yield. Table 8 shows the above results.

【0050】[0050]

【表8】 [Table 8]

【0051】表8によれば、小松菜及びほうれん草とも
に、単なる堆肥よりもミネラル強化肥料の方がかなり多
く収穫でき、特に続けて栽培したほうれん草では大きな
差となり、かつ収穫後の土壌pH値も中性に近い。
According to Table 8, it is found that the mineral-enriched fertilizer can harvest significantly more than the simple composts of both Komatsuna and spinach. Especially, the spinach grown continuously has a large difference, and the soil pH after harvesting is also neutral. Close to.

【0052】[0052]

【発明の効果】以上詳述したように、本発明のミネラル
強化肥料によれば、以下のような効果がある。請求項1
の発明は、有機性廃棄物に貝化石を添加混合した時点で
貝化石の有する吸着性を発揮し、有機性廃棄物からの臭
気、有害物を吸着し水分も吸着して、有機性廃棄物の前
調整時の調整素材を兼ね、発酵の際貝化石の有する無数
の孔は発酵菌の恰好の棲家となり、発酵を促進させるよ
うに働く。従って、畜産廃棄物等の有機性廃棄物が堆肥
化される過程での臭気等の環境汚染が無く、このミネラ
ル強化肥料を農地、緑地に施用すれば、ミネラルバラン
スの良い肥料を撒いたことになり、添加した貝化石は弱
アルカリであるから、酸性土壌を中和し土壌改良をしつ
つ、良好な作物を収穫できる。
As described in detail above, the mineral-enriched fertilizer of the present invention has the following effects. Claim 1
The invention of the present invention exhibits the adsorptivity of shell fossils at the time of adding and mixing shell fossils to organic wastes, adsorbs odors and harmful substances from organic wastes, adsorbs moisture, and removes organic wastes. During fermentation, the innumerable holes of the shell fossils serve as a good home for fermenting bacteria and promote fermentation during fermentation. Therefore, there is no environmental pollution such as odor in the process of composting organic waste such as livestock waste, and if this mineral-enriched fertilizer is applied to farmland and green space, it is possible to spread fertilizer with good mineral balance. Since the added fossil shells are weakly alkaline, good crops can be harvested while neutralizing the acidic soil and improving the soil.

【0053】請求項2の発明は、有機性廃棄物を先に好
気性発酵させ、その発酵物に貝化石を混合しても、上記
効果と同様の効果を得ることが出来る。
According to the second aspect of the present invention, the same effects as described above can be obtained even if the organic waste is first subjected to aerobic fermentation and the fermented product is mixed with fossil shellfish.

【0054】請求項3の発明は、土に有機性廃棄物及び
貝化石を混合し発酵させることで、農地に施用する前に
有機性廃棄物に含有する肥料成分を土に馴染ませ、土壌
中の微生物との拮抗や共生に、より順応し易くなってい
る。従って、上記効果以外に、土壌病害や害虫による被
害の回避が容易となる効果がある。
According to the third aspect of the present invention, the fertilizer component contained in the organic waste is adapted to the soil before being applied to agricultural land by mixing and fermenting the organic waste and shell fossils in the soil. It is easier to adapt to antagonism and symbiosis with microorganisms. Therefore, in addition to the above effects, there is an effect that it is easy to avoid damage from soil diseases and pests.

【0055】請求項4の発明は、土に米糠を含有する有
機性廃棄物を混合し発酵させるた混合発酵物に貝化石を
混合しても、上記効果と同様の効果を得ることが出来
る。
According to the fourth aspect of the present invention, the same effect as described above can be obtained by mixing shell fossils with a mixed fermented product obtained by mixing and fermenting organic waste containing rice bran in soil.

【0056】請求項5の発明は、加熱処理されているか
ら、なお一層強力な吸着性能が付与され、上記効果が一
層強力になる。
According to the fifth aspect of the present invention, since the heat treatment is performed, more powerful adsorption performance is imparted, and the above effect is further enhanced.

───────────────────────────────────────────────────── フロントページの続き (51)Int.Cl.7 識別記号 FI テーマコート゛(参考) C05F 11/02 B09B 3/00 ZABD ──────────────────────────────────────────────────続 き Continued on the front page (51) Int.Cl. 7 Identification symbol FI Theme coat ゛ (Reference) C05F 11/02 B09B 3/00 ZABD

Claims (5)

【特許請求の範囲】[Claims] 【請求項1】石灰質や珪酸等からなる各種ネクトン、プ
ランクトン、藻類、海藻等が埋没して堆積し、腐植溶性
を帯びた結晶体である貝化石を、有機性廃棄物に添加混
合し、水分調整を兼ねると共に臭気等を吸着させ、該混
合物を好気性発酵させてなることを特徴とするミネラル
強化肥料。
1. A fossil shell, which is a humus-soluble crystalline body in which various kinds of nekton, plankton, algae, seaweed, etc. made of calcareous or silicic acid are buried and deposited, mixed and added to organic waste. A mineral-enriched fertilizer, which is obtained by aerobically fermenting the mixture while simultaneously adjusting and adsorbing odors.
【請求項2】有機性廃棄物を好気性発酵させてなる発酵
物に、石灰質や珪酸等からなる各種ネクトン、プランク
トン、藻類、海藻等が埋没して堆積し腐植溶性を帯びた
結晶体である貝化石を、混合してなることを特徴とする
ミネラル強化肥料。
2. A fermented product obtained by aerobic fermentation of an organic waste is a humus-soluble crystalline material in which various nekton, plankton, algae, seaweed and the like made of calcareous or silicic acid are buried and deposited. A mineral-enriched fertilizer characterized by mixing shell fossils.
【請求項3】病原菌に汚染されていない土と、有機性廃
棄物と、石灰質や珪酸等からなる各種ネクトン、プラン
クトン、藻類、海藻等が埋没して堆積し腐植溶性を帯び
た結晶体である貝化石とを混合し、水分調整を兼ねると
共に臭気等を吸着させ、該混合物を好気性発酵させてな
ることを特徴とするミネラル強化肥料。
3. A humus-soluble crystalline material that is buried with soil that is not contaminated by pathogenic bacteria, organic waste, and various nekton, plankton, algae, seaweed, and the like made of calcareous or silicic acid. A mineral-enriched fertilizer, which is obtained by mixing fossil shellfish, adjusting moisture, adsorbing odors, and aerobically fermenting the mixture.
【請求項4】病原菌に汚染されていない土と有機性廃棄
物とを混合し、水分調整を兼ねると共に臭気等を吸着さ
せ、該混合物を好気性発酵させてなる混合発酵物に、石
灰質や珪酸等からなる各種ネクトン、プランクトン、藻
類、海藻等が埋没して堆積し腐植溶性を帯びた結晶体で
ある貝化石を混合してなることを特徴とするミネラル強
化肥料。
4. A mixed fermented product obtained by mixing soil not contaminated with pathogenic bacteria and organic waste, serving as a water regulator and adsorbing odors, and subjecting the mixture to aerobic fermentation. A mineral-enriched fertilizer comprising a mixture of shell fossils, which are humus-soluble crystalline bodies in which various nektons, planktons, algae, seaweeds and the like are embedded and deposited.
【請求項5】前記貝化石は、その小孔に含まれている結
晶水が加熱処理により除去されている請求項1、2、3
又は4記載のミネラル強化肥料。
5. The shell fossil according to claim 1, wherein water of crystallization contained in the pores is removed by heat treatment.
Or the mineral-enriched fertilizer according to 4.
JP11233079A 1999-07-15 1999-07-15 Mineral enriched fertilizer Pending JP2001026488A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP11233079A JP2001026488A (en) 1999-07-15 1999-07-15 Mineral enriched fertilizer

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP11233079A JP2001026488A (en) 1999-07-15 1999-07-15 Mineral enriched fertilizer

Publications (1)

Publication Number Publication Date
JP2001026488A true JP2001026488A (en) 2001-01-30

Family

ID=16949481

Family Applications (1)

Application Number Title Priority Date Filing Date
JP11233079A Pending JP2001026488A (en) 1999-07-15 1999-07-15 Mineral enriched fertilizer

Country Status (1)

Country Link
JP (1) JP2001026488A (en)

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2006076868A (en) * 2004-09-09 2006-03-23 Tadaaki Ono Method for manufacturing insect-proofing and insect-removing fertilizer and its product
KR100779758B1 (en) 2005-12-23 2007-11-28 조재영 Method for organic by-product fertilizer using seaweed by-product as bulking agent
CN102206121A (en) * 2011-04-01 2011-10-05 刘京花 Marine polysaccharide inorganic and organic composite controlled release fertilizer and process for producing the same
CN104030747A (en) * 2014-06-28 2014-09-10 云南思创格科技有限责任公司 Alkali organic fertilizer and preparation method thereof
KR101978615B1 (en) * 2018-12-24 2019-08-28 김정민 Method for manufacturing poultry waste fertilizer and the poultry waste fertilizer manufactured thereof

Cited By (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2006076868A (en) * 2004-09-09 2006-03-23 Tadaaki Ono Method for manufacturing insect-proofing and insect-removing fertilizer and its product
KR100779758B1 (en) 2005-12-23 2007-11-28 조재영 Method for organic by-product fertilizer using seaweed by-product as bulking agent
CN102206121A (en) * 2011-04-01 2011-10-05 刘京花 Marine polysaccharide inorganic and organic composite controlled release fertilizer and process for producing the same
CN102206121B (en) * 2011-04-01 2014-08-20 山东乐丰生物科技有限公司 Marine polysaccharide inorganic and organic composite controlled release fertilizer and process for producing the same
CN104030747A (en) * 2014-06-28 2014-09-10 云南思创格科技有限责任公司 Alkali organic fertilizer and preparation method thereof
CN104030747B (en) * 2014-06-28 2016-06-01 云南思创格科技有限责任公司 Alkalescent fertilizer and its preparation method
KR101978615B1 (en) * 2018-12-24 2019-08-28 김정민 Method for manufacturing poultry waste fertilizer and the poultry waste fertilizer manufactured thereof

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