JP2016044088A - Method of producing compost in short period, method of transforming abandoned cultivation land into farmland in short period, and method of utilizing contaminated soil for farmland - Google Patents

Method of producing compost in short period, method of transforming abandoned cultivation land into farmland in short period, and method of utilizing contaminated soil for farmland Download PDF

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JP2016044088A
JP2016044088A JP2014168322A JP2014168322A JP2016044088A JP 2016044088 A JP2016044088 A JP 2016044088A JP 2014168322 A JP2014168322 A JP 2014168322A JP 2014168322 A JP2014168322 A JP 2014168322A JP 2016044088 A JP2016044088 A JP 2016044088A
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JP6427823B2 (en
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関 浩一
Koichi Seki
浩一 関
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Kukizaki Kanko Noen kk
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    • 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
    • Y02EREDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
    • Y02E50/00Technologies for the production of fuel of non-fossil origin
    • Y02E50/30Fuel from waste, e.g. synthetic alcohol or diesel

Abstract

PROBLEM TO BE SOLVED: To provide a method of producing compost in a short period in which livestock excreta is transformed into organic fertilizer and compost even faster comparing to conventional methods.SOLUTION: A method of producing compost on a roofed concrete floor in a short period comprises: a pretreatment process of heaping a mixture formed by mixing livestock excreta and an additive containing rice malt at the thickness of 20 to 30 cm; a primary fermentation process of agitating the mixture to aerobically ferment every day or every other day for 5 to 8 days; and a secondary fermentation process of adding rice bran and soybean cake to a primary fermented product and agitating it to aerobically ferment every day or every other day for 5 to 8 days.SELECTED DRAWING: Figure 1

Description

本発明は、本発明は、牛、豚、鶏、馬など家畜の糞尿(以下、単に「畜産糞尿」という)、人糞尿、青刈り作物、さらに食品残渣(これらを含めてここでは畜産糞尿とする)、特に牛の糞尿(以下、単に「牛糞」ともいう)を主原料とする、堆肥の短期製造方法、さらに耕作放棄地の短期農地化方法、加えて汚染土壌の農地利用方法に関する。   The present invention relates to the excrement of livestock such as cattle, pigs, chickens and horses (hereinafter simply referred to as “livestock excrement”), human excrement, green crops, and food residues (including these, In particular, the present invention relates to a method for producing compost in a short period of time using cow manure (hereinafter also simply referred to as “cow manure”), a method for converting abandoned farmland into a short-term farmland, and a method for using contaminated soil in farmland.

(堆肥化時間の短縮問題)
伝統的な畜産糞尿を主原料にして作られる堆肥は、畜産糞尿と稲藁などの副材料を混合して、野積みにして、長時間かけてゆっくり堆肥化して得られる。現在では、法規制、悪臭問題などもあり、畜産糞尿を、屋根がある土壌に浸透しない床の上に山積みにし、発酵が進み所定温度に到達したことを目安に、切り返し(反転)を繰り返し、悪臭を除きながら、完熟させて作られている。そして、畜産糞尿、特に、牛糞の完熟堆肥を得るには、おおよそ120日〜150日間必要とされている。そのため、家畜牛糞は、焼却処理などされ、処理費用、環境負荷を高めている。
(Problem shortening composting time)
Compost made from traditional livestock manure is made by mixing livestock manure and sub-materials such as rice straw, putting them in fields and slowly composting them over a long period of time. At present, due to legal regulations, bad odor problems, etc., livestock manure is piled up on a floor that does not penetrate the soil where the roof is located, and repeated turnover (reversal) with the progress of fermentation and reaching the predetermined temperature as a guideline, It is made by ripeness while eliminating bad smell. And in order to obtain livestock manure, in particular, fully-ripened compost of cow dung, approximately 120 to 150 days are required. For this reason, livestock cow dung is incinerated, which increases processing costs and environmental burden.

昨今では、特許文献1〜3などに開示されているように、種々の畜産糞尿を用いた有機肥料、有機肥料の製造方法が提案されている。しかしながら、いずれも早期堆肥化においては満足できるものではない。   In recent years, as disclosed in Patent Documents 1 to 3 and the like, organic fertilizers using various livestock manure and methods for producing organic fertilizers have been proposed. However, none are satisfactory in early composting.

そこで、発明者は、すでに特許文献4に開示のように、畜産糞尿の従来にない肥料成分を高めた早期有機肥料化を実現する有機肥料及び有機肥料の製造方法を開発している。その後、鋭意研究した結果、さらに、早期に堆肥化できることを見出し、本件発明を完成させるに至った。   Thus, as disclosed in Patent Document 4, the inventor has already developed an organic fertilizer and an organic fertilizer manufacturing method for realizing early organic fertilization by increasing an unprecedented fertilizer component of livestock manure. After that, as a result of earnest research, it was found that composting was possible at an early stage, and the present invention was completed.

特許文献4に開示の発明は、主に畜産糞尿、特に牛糞を主原料として、早期堆肥化でき、製造工程中の悪臭を低減した、リン高含有率の肥料、かつ連作障害を防ぎ、植物に耐病性を付与し、作物の収穫量増大、大きな花及び果実を栽培することを可能にする有機肥料及びその製造方法であって、糞尿に植物質原料を混合し糞尿の硬さを調節する糞尿前処理工程と、前記糞尿前処理工程後の糞尿を山積みし部分分解・発酵させる一次発酵工程と、前記一次発酵工程後の糞尿に米糠及び微生物培養液を添加して発酵を促進させる二次発酵工程と、前記二次発酵工程後の糞尿に微生物分解物を添加して追加発酵させる三次発酵工程とからなることを特徴とする。   The invention disclosed in Patent Document 4 mainly uses livestock manure, particularly cow dung, as a main raw material, can be composted at an early stage, reduces malodor during the manufacturing process, prevents fertilizer with a high phosphorus content, prevents continuous cropping trouble, An organic fertilizer that imparts disease resistance, increases crop yield, enables cultivation of large flowers and fruits, and a method for producing the same, wherein manure is mixed with plant material to adjust the hardness of manure A pre-treatment step, a primary fermentation step in which manure after the manure pretreatment step is piled up and partially decomposed and fermented, and a secondary fermentation in which rice bran and a microorganism culture solution are added to the manure after the primary fermentation step to promote fermentation And a tertiary fermentation process in which a microbial decomposition product is added to the manure after the secondary fermentation process to perform additional fermentation.

(耕作放棄地の問題)
他方、農業人口の減少、高齢化に伴い、耕作を放棄し農地(耕作放棄地(農地としての未開拓地も含む。また短期間放置され雑草が生い茂った圃場も含む。))が散見されるようになり、その対応が農村地域、その自治体において大きな問題となりつつある。企業の農業事業が認められるものの、耕作放棄地は、雑草に覆われ、簡単に農地として復元することはできず、また復元後も短期に農作物の栽培を開始することができない。
(Problems with abandoned farmland)
On the other hand, with the decline in the agricultural population and aging, farmland is abandoned and farmland (including abandoned farmland (including uncultivated land as farmland, and fields that have been left for a short period of time and overgrown with weeds)) is seen. This has become a big problem in rural areas and local governments. Although a company's agricultural business is permitted, the abandoned farmland is covered with weeds and cannot be easily restored as farmland, and cultivation of crops cannot be started in a short period after restoration.

したがって、農地への復元、作物栽培による収入が得られるまで、多大な時間と費用が必要になり、企業の農業事業が認められたとしても、耕作放棄地の問題は簡単に解決されるものではない。他方、農業者でなかった者が途中から農業に就業しようとしても、個人で広大な耕作放棄地を農地化することは現実的には不可能であると言わざるを得ないのが現状である。したがって、耕作放棄地の早期農地化、早期作物栽培による収入が可能な技術の開発が期待されている。   Therefore, it takes a lot of time and money to recover to farmland and to obtain income from crop cultivation. Even if a company's agricultural business is approved, the problem of abandoned farmland cannot be solved easily. Absent. On the other hand, even if a person who is not a farmer tries to start farming from the middle, it must be said that it is practically impossible to convert a large abandoned farmland into farmland. . Therefore, it is expected to develop a technology that enables early abandonment of farmland and income from early crop cultivation.

(汚染土壌の栽培制限問題)
他方、汚染物質の検出により、作物栽培が制限されている農地がある。原発事故による放射性物質による汚染地域、重金属による汚染地域などであり、栽培作物への汚染物質の移動、残留が深刻な問題である。これらの地域では、除染、土壌の入れ替え、汚染物質の不動化など様々な対策が取られているが、耕作開始の目途が立たず、農業による収入がないのが現状である。
(Culture restriction problem of contaminated soil)
On the other hand, there are farmlands where crop cultivation is restricted by the detection of pollutants. There are areas contaminated with radioactive materials caused by the nuclear accident, areas contaminated with heavy metals, and the transfer and residual of pollutants to cultivated crops are serious problems. In these areas, various measures such as decontamination, soil replacement, and immobilization of pollutants have been taken, but the current situation is that there is no prospect of starting cultivation and no income from agriculture.

また、耕作制限地域では、結果的に、耕作放棄地と同様に、農地が雑草に覆われ、耕作が再開できるとなったとしても、農地化への時間、費用面の負担が懸念される。すでに、耕作放棄地と化しており、農地に復元したとしても、再度農地化を防ぐため、作物栽培しない場合には雑草の刈り込みを継続する必要があり、作物栽培を継続する場合には、収入にならない作物の栽培を継続する必要がある、極めて負担が大きい。耕作制限地域において、継続的な作物生産と、収入とを両立する新たな農業生産システムの構築が望まれている。   As a result, in the restricted farming area, as in the case of the abandoned farming area, even if the farmland is covered with weeds and the farming can be resumed, there is a concern about the time and cost burden for farming. Even if it has already been turned into abandoned cultivated land and it has been restored to farmland, it is necessary to continue pruning weeds when crop cultivation is not carried out to prevent the return to farmland. It is necessary to continue the cultivation of crops that do not become large, and it is extremely burdensome. In areas where cultivation is restricted, it is desired to construct a new agricultural production system that balances continuous crop production and income.

特開2005−320181号公報JP-A-2005-320181 特開2005−060210号公報Japanese Patent Laid-Open No. 2005-060210 特開2004−131356号公報JP 2004-131356 A 特開2010−208893号公報JP 2010-208893 A

そこで、本発明は、畜産糞尿を、従来に比べ一層早期に有機肥料・堆肥化する、堆肥の短期製造方法、さらに耕作放棄地の短期農地化方法、また汚染土壌の農地利用方法を提供することを目的とする。   Therefore, the present invention provides a short-term production method for compost, a short-term farmland production method for abandoned farmland, and a method for using contaminated soil in farmland, in which livestock manure is converted to organic fertilizer / compost earlier than conventional methods. With the goal.

上記課題を解決するために、本発明は、
(1)
屋根付きコンクリート床で堆肥を短期に製造する方法であって、
畜産糞尿と麹を含む添加物を混合した混合物を厚さ20−30cmで積む前処理工程と、
前記混合物を5−8日間毎日或いは1日おきに撹拌し好気発酵させる一次発酵工程と、
一次発酵物に米糠及び大豆かすを追加して5−8日間毎日或いは1日おきに撹拌し好気発酵させる二次発酵工程と、
からなることを特徴とする堆肥の短期製造方法。

(2)
圃場で堆肥を短期に製造する方法であって、
畜産糞尿と麹を含む添加物と土壌を混合した混合物を厚さ20−30cmで積む前処理工程と、
前記混合物の水分調整をしながら5−8日間毎日或いは1日おきに撹拌し好気発酵させる一次発酵工程と、
一次発酵物に米糠及び大豆かすを追加して5−8日間毎日或いは1日おきに撹拌し好気発酵させる二次発酵工程と、
からなることを特徴とする堆肥の短期製造方法。

(3)
前記添加物に、カキ殻が含まれることを特徴とする(1)又は(2)に記載の堆肥の短期製造方法。

(4)
前記添加物が、
畜産糞尿2トン当たり、
米糠 100〜300kg
大豆かす 50〜100kg
カキ殻 30〜 80kg
ケイ素源 10〜 30kg
カニ殻 30〜 50kg
麹 50〜200kg
であることを特徴とする(1)又は(2)に記載の堆肥の短期製造方法。

(5)
前記麹が、種麹を増殖させた残渣であることを特徴とする(1)〜(3)の何れかに記載の堆肥の短期製造方法。

(6)
前記ケイ素源が、笹又は竹であることを特徴とする(4)に記載の堆肥の短期製造方法。

(7)
地上部が3kg/mより少ない密度で雑草が生い茂った耕作放棄地の農地化方法であって、
雑草を粉砕する雑草粉砕工程と、
圃場10アール当たり、以下の添加物を0.2〜0.5トン投入する添加物散布工程と、
米糠 100〜300kg
大豆かす 50〜100kg
カキ殻 30〜 80kg
ケイ素源 10〜 30kg
カニ殻 30〜 50kg
麹 50〜200kg
粉砕した雑草と添加物と土壌を混合し、3週間放置する荒耕し工程と、
圃場10アール当たり、以下の微生物酵素を散布、混合し、2週間放置する微生物酵素混合工程と、
圃場表層をロータリで均す表層仕上げ工程と、
からなり、
表層仕上げ工程後、直ちに、作物の播種・苗植えを可能とした耕作放棄地の農地化方法。

(8)
地上部が3kg以上/mの密度で雑草が生い茂った耕作放棄地の農地化方法であって、
雑草を粉砕する雑草粉砕工程と、
微生物酵素を散布する工程と、
粉砕した雑草と散布した微生物酵素と土壌を混合する混合工程と、
圃場表層をロータリで均す表層仕上げ工程と、
からなり、
前記雑草粉砕工程〜表層仕上げ工程まで1日で行い、表層仕上げ工程後、直ちに、作物の播種・苗植えを可能とした耕作放棄地の農地化方法。

(9)
前記微生物酵素が、醤油の種麹を増殖させた小麦麹の残渣又は/及び味噌の種麹を増殖させた大麦麹の残渣(圃場10アール当たり50〜150kg)、であることを特徴とする(7)又は(8)に記載の耕作放棄地の農地化方法。

(10)
汚染土壌に、バイオ燃料の原料となる作物を栽培し、得られたバイオマスからバイオ燃料を生成することを特徴とする汚染土壌の農地利用方法。

(11)
前記汚染土壌を、(7)〜(9)の何れかに記載の耕作放棄地の短期農地化方法によって、整地、圃場化した後に、前記作物の栽培を開始することを特徴とする(10)に記載の汚染土壌の農地利用方法。

(12)
前記バイオエタノールの生成に伴い、前記汚染物質を濃縮、回収し、汚染土壌の汚染物質濃度を低下させることを特徴とする(10)又は(11)に記載の汚染土壌の農地利用方法。

(13)
(10)又は(11)に記載の方法によって、得られたことを特徴とするバイオ燃料。
とした。

(14)
(1)〜(6)の何れかに記載の堆肥の短期製造方法で得られたことを特徴とする堆肥。

(15)
(14)に記載の堆肥と、粘土質を多く含む建設残土を混合したことを特徴とする土壌改良材。
In order to solve the above problems, the present invention provides:
(1)
A method of manufacturing compost on a covered concrete floor in a short time,
A pretreatment step of laminating a mixture of livestock manure and additives containing sputum at a thickness of 20-30 cm;
A primary fermentation step in which the mixture is aerobically fermented by stirring for 5-8 days every day or every other day;
A secondary fermentation process in which rice bran and soybean meal are added to the primary fermented product and stirred for 5 to 8 days every day or every other day for aerobic fermentation;
A method for the short-term production of compost characterized by comprising:

(2)
A method for producing compost in the field in a short time,
A pre-treatment step of stacking a mixture of an additive containing livestock manure and straw and soil in a thickness of 20-30 cm;
A primary fermentation step of aerobic fermentation by stirring daily or every other day for 5-8 days while adjusting the water content of the mixture;
A secondary fermentation process in which rice bran and soybean meal are added to the primary fermented product and stirred for 5 to 8 days every day or every other day for aerobic fermentation;
A method for the short-term production of compost characterized by comprising:

(3)
The short-term production method of compost according to (1) or (2), wherein the additive contains oyster shells.

(4)
The additive is
Per 2 tons of livestock manure,
100-300kg of rice bran
Soy meal 50-100kg
Oyster shell 30-80 kg
Silicon source 10-30kg
Crab shell 30-50kg
〜 50-200kg
(1) Or the short-term manufacturing method of compost as described in (2) characterized by the above-mentioned.

(5)
The method for producing a compost for a short time according to any one of (1) to (3), wherein the koji is a residue obtained by growing seed koji.

(6)
The method for producing a compost for a short time according to (4), wherein the silicon source is straw or bamboo.

(7)
A method for converting abandoned cultivated land where the above-ground part has a density of less than 3 kg / m 2 and overgrown with weeds,
A weed crushing process for crushing weeds;
An additive spraying process in which 0.2 to 0.5 tons of the following additives are added per 10 ares of a field,
100-300kg of rice bran
Soy meal 50-100kg
Oyster shell 30-80 kg
Silicon source 10-30kg
Crab shell 30-50kg
〜 50-200kg
A rough tilling process in which ground weeds, additives and soil are mixed and left for 3 weeks,
A microbial enzyme mixing process in which the following microbial enzymes are sprayed, mixed, and allowed to stand for 2 weeks per 10 ares of field:
A surface finishing process to level the field surface with a rotary,
Consists of
A method for converting abandoned cultivated land into farmland that enables seeding and seedling planting of crops immediately after the surface finishing process.

(8)
A method for converting abandoned cultivated land where the above-ground part has a density of 3 kg / m 2 or more and overgrown with weeds,
A weed crushing process for crushing weeds;
Spraying microbial enzymes;
A mixing step of mixing the crushed weeds and the sprayed microbial enzyme with the soil;
A surface finishing process to level the field surface with a rotary,
Consists of
A method for converting abandoned cultivated land into a farmland, which is performed in one day from the weed pulverization step to the surface finishing step, and immediately after the surface finishing step, it is possible to sow and plant seedlings.

(9)
The microbial enzyme is a residue of wheat straw or soy sauce seed cake grown with soy sauce seed meal (and 50 to 150 kg per 10 ares of field). 7) or the farm land conversion method of abandoned cultivation land as described in (8).

(10)
A method for using contaminated soil in farmland, comprising cultivating a crop as a raw material for biofuel on contaminated soil and generating biofuel from the obtained biomass.

(11)
(10) The cultivation of the crop is started after the contaminated soil is leveled and fielded by the short-term farmland conversion method of the abandoned farmland according to any one of (7) to (9). Use of contaminated soil in farmland

(12)
The method for using contaminated soil in agricultural land according to (10) or (11), wherein the pollutant is concentrated and recovered as the bioethanol is produced, and the pollutant concentration in the contaminated soil is reduced.

(13)
A biofuel obtained by the method according to (10) or (11).
It was.

(14)
A compost obtained by the short-term production method for compost according to any one of (1) to (6).

(15)
A soil conditioner characterized by mixing the compost according to (14) and construction residual soil containing a large amount of clay.

本発明は、上記構成であるので、堆肥の熟成期間が極めて短い。加えて、リン成分が高く、栽培作物の病害虫に対する抵抗性が高く、作物品質も高い。   Since this invention is the said structure, the maturation period of compost is very short. In addition, the phosphorus component is high, the cultivated crop is highly resistant to pests, and the crop quality is also high.

また、耕作放棄地であっても、農地復元、整地化後、短期或いは直ちに、播種、苗植え等が可能で、短期間で作物の栽培を可能にし、農業収入を短期間で得られる。   Even in abandoned cultivated land, seeding, seedling planting, etc. can be performed in a short period of time or immediately after restoration of farmland and leveling, enabling cultivation of crops in a short period of time and agricultural income in a short period of time.

汚染土壌が、耕作放棄地状態であっても、本発明である耕作放棄地の短期農地化方法によって、作物の栽培が早期に可能で、バイオエタノールなどを生成可能なバイオ燃料源となる作物を選択、栽培することで、汚染土壌においても農作物を栽培し、収入を得ることができる。加えて、汚染土壌の汚染物質が作物に吸収、濃縮され、作物栽培を繰り返すことで、土壌中の汚染物質の濃度が低減し、人が摂取可能な作物の栽培可能になる年数を大幅に短縮することができる。   Even if the contaminated soil is in an abandoned cultivated land state, it is possible to cultivate the crop at an early stage by using the short-term farmland method of the abandoned cultivated land according to the present invention. By selecting and cultivating, it is possible to cultivate crops and obtain income even in contaminated soil. In addition, pollutants in contaminated soil are absorbed and concentrated in crops, and repeated crop cultivation reduces the concentration of pollutants in the soil, greatly reducing the number of years that crops that can be ingested by humans can be grown. can do.

本発明である堆肥の短期製造方法の第一の実施形態の製造フロー図である。It is a manufacturing flow figure of a first embodiment of a short-term manufacturing method of compost which is the present invention. 短期製造方法の第一の実施形態に用いられる添加物の組成例である。It is an example of a composition of the additive used for 1st embodiment of a short-term manufacturing method. 本発明である堆肥の短期製造方法の第二の実施形態の製造フロー図である。It is a manufacturing flow figure of 2nd embodiment of the short-term manufacturing method of compost which is the present invention. 本発明である耕作放棄地の短期農地化方法(雑草が少ない場合)の工程図である。It is process drawing of the short-term farmlandization method (when there are few weeds) of cultivation abandonment land which is this invention. 本発明である耕作放棄地の短期農地化方法(雑草が多い場合)の工程図である。It is process drawing of the short-term farmlandization method (when there are many weeds) of cultivation abandonment land which is this invention. 本発明である耕作放棄地の短期農地化方法(雑草が多い場合)の作業風景である。It is the working scenery of the short-term farmland conversion method (when there are many weeds) of cultivation abandonment land which is this invention. 本発明である雑草が多い茂った土地の短期農地化方法で、整備した農地に、直ちに、ラッカセイの種を播種したときの生育の様子(播種から10日後)を写した写真である。対象では、発芽はほとんど確認できない。It is the photograph which copied the mode of growth (10 days after sowing) when seeds of peanut were immediately sown on the farmland improved by the method for short-term farming of the land with a lot of weeds according to the present invention. The subject hardly sees germination. 本発明である汚染土壌の農地利用方法の工程図である。It is process drawing of the farmland utilization method of the contaminated soil which is this invention.

次に、以下に、添付図面に基づいて、本発明についてより詳細に説明する。なお、本発明は下記実施例に限定されるものではない。   Next, the present invention will be described in more detail with reference to the accompanying drawings. In addition, this invention is not limited to the following Example.

堆肥の短期製造方法1/屋内(コンクリート床のストックヤード)での堆肥化
(1)本発明である堆肥の短期製造方法1は、図1に示すように、前処理工程2と、一次発酵工程3と、二次発酵工程4と、三次発酵工程5とからなり、堆肥6を極めて早期に製造することができる。
Compost short-term manufacturing method 1 / Composting indoors (concrete floor stockyard) (1) As shown in FIG. 1, compost short-term manufacturing method 1 includes a pretreatment step 2 and a primary fermentation step. 3, a secondary fermentation process 4, and a tertiary fermentation process 5, and the compost 6 can be manufactured very quickly.

(2)前処理工程2
前処理工程2は、畜産糞尿と、アルカリ資材を含む添加物と混合し、混合物を屋根付きコンクリート床上に厚さ20−30cmに積む工程である。従来の堆肥の製造方法と異なり、畜産糞尿を堆く山積みすることなく
(2) Pretreatment process 2
Pretreatment step 2 is a step of mixing livestock manure and an additive containing an alkaline material, and stacking the mixture to a thickness of 20 to 30 cm on a concrete floor with a roof. Unlike conventional compost production methods, without piles of livestock manure

畜産糞尿は、糞尿としては、主に牛、さらに豚、鶏、馬などの家畜の単一又は複合糞尿(畜産糞尿)、人糞が採用でき、それらに加え、食品残渣、植物も畜産糞尿に混合して利用できる。何れの糞尿等であってもよいが、元肥、追肥としての堆肥の栄養素(N、P、K)のバランスを考慮すると、牛糞4重量部、豚糞4重量部、鶏糞2重量部が好ましい。なお、畜産糞尿には、敷き藁、米の籾殻なども含まれてもよい。   Livestock manure is mainly cattle, livestock manure such as cattle, pigs, chickens, and horses (livestock manure) and human feces. In addition to these, food residues and plants can also be used for livestock manure. Can be used as a mixture. Any feces and urine may be used, but considering the balance of nutrients (N, P, K) of compost as raw manure and additional fertilizer, 4 parts by weight of cow dung, 4 parts by weight of swine dung, and 2 parts by weight of chicken dung are preferable. The livestock manure may also include bedding straw, rice husk and the like.

添加物は、図2に示すように、圃場10アールに施肥される堆肥量に対応する畜産糞尿2〜5トンに対し、米糠、大豆かす、カキ殻、ケイ素源、カニ殻、麹を図2に示す量を目安に調整する。   As shown in FIG. 2, the additives are rice bran, soybean meal, oyster shell, silicon source, crab shell, and straw for 2 to 5 tons of livestock manure corresponding to the amount of compost applied to the field 10 are. Adjust the amount shown in.

米糠・大豆かすは、主に、畜産糞尿の水分(粘度)調整に用い、さらに、米糠は乳酸菌源ともなり、リン成分を高める効果がある。大豆かすは発酵時のアミノ酸源となる。   Rice bran and soybean meal are mainly used to adjust the water content (viscosity) of livestock manure, and rice bran is also a source of lactic acid bacteria and has the effect of increasing the phosphorus component. Soybean meal becomes a source of amino acids during fermentation.

カキ殻は、アルカリ資材であり、畜産糞尿のpHを高め、アルカリ発酵を促し、酸敗微生物等の生育を抑制するなど、発酵微生物を選別するとともに、微生物酵素の生産、活性化に必要な亜鉛(Zn)、マグネシウム(Mg)の供給源ともなる。   Oyster shells are an alkaline material that increases the pH of livestock manure, promotes alkaline fermentation, suppresses the growth of spoilage microorganisms, etc. It is also a supply source of Zn) and magnesium (Mg).

亜鉛、マグネシウムを増強することで、酵素生産、活性が高まるが、カギ殻を多量に投入すると、畜産糞尿のpHが高くなりすぎる。畜産糞尿の高pH化を防止しつつ、Zn、Mgを増強する場合には、にがりを添加するとよい。また、カキ殻に換え、アルカリ鉱物である医王石の粉末などを使用することもできる。   Enhancing zinc and magnesium increases enzyme production and activity, but if a large amount of key shell is added, the pH of livestock manure becomes too high. In order to increase Zn and Mg while preventing the increase in pH of livestock manure, bittern is preferably added. Further, instead of oyster shells, powder of Ioishi, which is an alkali mineral, can be used.

ケイ素源は、ガラス質を多く含む植物などであり、笹、竹、籾殻などが例示できる。ガラス質が豊富であると、作物の葉が丈夫になり、病害虫への抵抗性が高まる。また、笹、竹、籾殻などは、従来から肥料成分として有効といわれているが、堆肥化に時間がかかり、堆肥としての利用実績は多くなく、焼却処分として、処分費用、環境負荷が高まっている。本発明において、堆肥の材料とすることで、作物の病害中への抵抗性を高める他に、環境負荷の低減も図れる効果がある。   The silicon source is a plant containing a large amount of glass, and examples thereof include straw, bamboo, and rice husks. Abundant glassy material makes the crops more durable and more resistant to pests. In addition, firewood, bamboo, rice husks, etc. are traditionally said to be effective as fertilizer components, but it takes time to compost and has not been used as a compost, resulting in increased disposal costs and environmental impact as incineration disposal. Yes. In the present invention, the use of compost material has the effect of reducing the environmental burden in addition to increasing resistance to crop diseases.

カニ殻は、L−キトサン源で、発酵微生物の増殖を助ける。   Crab shell is a source of L-chitosan and helps the growth of fermenting microorganisms.

麹は、麹の増殖に伴って分泌される澱粉成分の加水分解させるアミラーゼ、タンパク質のアミノ酸化するプロテアーゼ、脂質のエステル結合を加水分解するリパーゼによって、畜産糞尿の分解(低分子化)を促す。さらに、抗生物質、ビタミン類も生成し、発酵菌相を好適に整える。また、セルラーゼ、セミセルラーゼを生成し、畜産糞尿、ケイ素源を効果的に分解し、ガラス質(ケイ素)豊富な堆肥の製造を可能にする。   Koji promotes degradation (low molecular weight) of livestock manure by amylase that hydrolyzes starch components secreted with the growth of koji, protease that converts amino acid into protein, and lipase that hydrolyzes ester bond of lipid. Furthermore, antibiotics and vitamins are also produced, and the fermenting bacterial flora is suitably arranged. It also produces cellulase and semicellulase, effectively decomposes livestock manure and silicon source, making it possible to produce compost rich in vitreous (silicon).

麹源として、日本酒、味噌、醤油用の黄麹、焼酎の白、黒麹、泡盛用の黒麹などがある。特に、種麹を増殖させた残渣を用いるとよい。種麹は、栄養源である、蒸した小麦、大麦、大豆、米等の培養材で増殖させ、乾燥後、篩いで胞子を篩いおとし、粉末状或いは顆粒化して流通している。種麹メーカは、従来から、種麹の残渣を産業廃棄物として、その処理に費用を支払って、焼却処分しており、廃棄に多大なコストを掛けていた。種麹の残渣を本発明に用いることで、原料の短期肥料化を可能にし、焼却処分費用の低減も図れる。さらに、穀物飲料、例えば、麦茶の抽出残座(煮殻)に、麹菌(胞子粉末)、種麹、種麹の残渣を植え付け、必要に応じて他の栄養源を添加し、拡大培養した麹増殖物を用いてもよい。これによっても、食品残渣の低減に繋がる。麹菌の増殖床は、流通農産物、食品と競合しないことが望ましい。   Examples of koji sources include sake, miso, soy sauce yellow koji, shochu white, black koji, and awamori black koji. In particular, a residue obtained by growing seed pods may be used. Seed rice is grown in culture materials such as steamed wheat, barley, soybeans, and rice, which are nutrient sources, and after drying, the spores are sieved with a sieve and are distributed in the form of powder or granules. Conventionally, the seed maker has spent a great deal of cost on disposal because the seed residue is treated as industrial waste, paying for its disposal and incineration. By using the seed meal residue in the present invention, it is possible to make the raw material a short-term fertilizer and to reduce the incineration disposal cost. In addition, cereals such as barley tea extract residue (boiled husk) were planted with koji mold (spore powder), seed cake, and seed cake residue, and other nutrients were added if necessary, and expanded culture Proliferation may be used. This also leads to a reduction in food residues. It is desirable that the gonococcal growth bed does not compete with agricultural products and foods distributed.

麹の用途によって、培養材、種麹の種類はことなる。例えば、醤油用麹(小麦麹)であれば、全粒小麦粉砕物を培養材として培養される。味噌用麹であれば大麦が培養材として用いられる。特に、小麦麹の残渣は、麹の種類、ケイ素源(小麦ふすま)が豊富なことから好適である。   Depending on the use of the koji, the type of culture material and seed koji vary. For example, in the case of soy sauce koji (wheat koji), the whole wheat pulverized product is cultured as a culture material. Barley is used as a culture material for miso. In particular, the residue of wheat bran is preferable because of its rich variety of straw and silicon source (wheat bran).

種麹の残渣には、畜産糞尿の堆肥化に十分な麹菌が残存していること、また小麦麹の残渣にはふすまが含まれ、ケイ素源ともなる。大豆であればアミノ酸源となる。また、黒麹は、クエン酸を生産し、発酵微生物活性を高める。   The residue of the seed meal contains enough koji mold for composting of livestock manure, and the residue of wheat straw contains bran and becomes a silicon source. Soybean is a source of amino acids. Black potato also produces citric acid and enhances fermenting microbial activity.

(3)一次発酵工程3
一次発酵工程3は、図1に示すように、畜産糞尿と添加物の混合物を1〜2日に1回撹拌し、1週間ほど主に好気アルカリ発酵を促し、畜産糞尿を分解させる。一次発酵では混合物が70〜80℃まで達温し、そのころを一次発酵の終点とする。アルカリ性と高熱により、一次発酵の微生物菌相が選択され、堆肥化に好適な環境が整えられる。
(3) Primary fermentation process 3
As shown in FIG. 1, the primary fermentation step 3 stirs a mixture of livestock manure and additives once every 1-2 days, mainly promotes aerobic alkaline fermentation for about 1 week, and decomposes livestock manure. In the primary fermentation, the mixture reaches a temperature of 70 to 80 ° C., and that time is regarded as the end point of the primary fermentation. Due to the alkalinity and high heat, the microbial flora of primary fermentation is selected, and an environment suitable for composting is prepared.

(4)二次発酵工程4
二次発酵工程4は、図1、2に示すように、米糠、大豆かすを追加して、さらに、混合物を1〜2日に1回撹拌し、1週間ほど主に好気アルカリ発酵を促す。米糠、大豆かすの追加は、一次発酵で微生物増殖に消費された栄養素を補充し、施肥後の土壌微生物、作物の栄養源であるとともに、乳酸菌を混合物に補充するために行う。元肥として使用するのであれば、二次発酵物を圃場に施肥することができる。二次発酵中期以後後、混合物から、ほとんど悪臭はしない。
(4) Secondary fermentation process 4
In the secondary fermentation step 4, as shown in FIGS. 1 and 2, rice bran and soybean meal are added, and the mixture is stirred once every 1 to 2 days to promote mainly aerobic alkaline fermentation for about one week. . Rice bran and soybean meal are added to supplement the nutrients consumed for microbial growth in the primary fermentation, as well as to supply soil microorganisms and nutrients for the crop, and to supplement the mixture with lactic acid bacteria. If used as the original fertilizer, the secondary fermented product can be fertilized in the field. After the middle stage of secondary fermentation, there is almost no odor from the mixture.

(5)三次発酵工程5
三次発酵工程5は、追肥用として、作物に怖じて、さらに米糠、大豆かすを追加し、発酵させる工程である。これにより、堆肥の栄養価、特に、米糠の追加によりリン成分(P)が高まる。
(5) Tertiary fermentation process 5
The tertiary fermentation process 5 is a process for adding fermented rice bran and soybean meal and fermenting them as a fertilizer for fear of crops. Thereby, the nutrient value of compost, in particular, the phosphorus component (P) is increased by the addition of rice bran.

なお、各発酵工程に、黒糖蜜(1/100希釈程度)及び/又は微生物発酵酵素液を噴霧、添加すると、発酵速度が速まり、各発酵工程を短縮することができる。微生物発酵酵素液としては、バイオイオンバランス((有)アグリクリエイト製)を100倍に希釈した液、その他、所謂「ぼかし」液などが使用できる。実施例2においても同じ。   In addition, when brown molasses (about 1/100 dilution) and / or a microbial fermentation enzyme liquid are sprayed and added to each fermentation process, fermentation rate will increase and each fermentation process can be shortened. As the microbial fermentation enzyme solution, a solution obtained by diluting bioion balance (manufactured by Aggregate) 100 times, other so-called “blur” solution, and the like can be used. The same applies to Example 2.

(6)堆肥6
堆肥6は、畜産糞尿から約3週間の短期で製造することができる。元肥として使用する場合には、約2トンからできる二次発酵物を圃場10aに施肥すればよい。元肥であれば、畜産糞尿から約2週間で製造できる。また、熟成途中での悪臭の発生が極めて少ない。
(6) Compost 6
The compost 6 can be produced from livestock manure in a short period of about 3 weeks. In the case of using it as the original fertilizer, a secondary fermented product made from about 2 tons may be applied to the field 10a. If it is original fertilizer, it can be manufactured from livestock manure in about two weeks. Moreover, the generation of bad odor during aging is extremely small.

本発明である堆肥の短期製造方法1によって得られた堆肥は、肥料成分比率、特にリン含有率が従来の堆肥に比べ高い上、作物の連作障害防止、耐病性向上(特に葉の病気(うどん粉病、黒斑病、灰色カビ病)が極めて低減される)、収穫量向上、作物品質、特に糖度が向上し、農業分野において極めて有効である。   The compost obtained by the method 1 for short-term production of compost according to the present invention has a higher fertilizer component ratio, particularly phosphorus content, compared to conventional compost, and prevents crop cropping failures and improves disease resistance (especially leaf disease (emulsions) Disease, black spot disease, gray mold disease) is greatly reduced), yield is improved, crop quality, especially sugar content is improved, and it is extremely effective in the agricultural field.

さらに、堆肥6を培養土或いは土壌改良材とする場合には、使用される圃場に合わせて、各種土と混合すればよい。粘土質が少ない圃場、例えば水田の場合には、建築現場、整地工事等から廃棄される粘土質が多い建設残土を混合すればよい。そうすることで、建設残土の処理コストも抑制し、低コストの培養土、土壌改良材を提供することができる。各種土は、発酵前、発酵途中、発酵後に混合してもよい。   Furthermore, when compost 6 is used as culture soil or a soil improving material, it may be mixed with various types of soil according to the field used. In the case of farm fields with little clay, such as paddy fields, construction residual soil with much clay discarded from construction sites, leveling work, etc. may be mixed. By doing so, the processing cost of construction residual soil can also be suppressed and a low-cost culture soil and a soil improvement material can be provided. Various soils may be mixed before fermentation, during fermentation, or after fermentation.

堆肥の短期製造方法11/圃場での堆肥化
以下、10アール規模の圃場に施肥する堆肥の圃場での製造方法について具体的に説明する。
Short-term production method 11 for compost / composting in a field Hereinafter, a production method in a field for compost applied to a 10 are scale field will be described in detail.

(1)畜産糞尿:2トン/10アール
施肥される圃場の面積に応じて、上記畜産糞尿重量を比例的に増減させればよい。例えば、1ヘクタールの圃場には、畜産糞尿20トン使用する等。当該方法であれば、広大な圃場の堆肥をその圃場で短期間に製造することができ、堆肥の製造時間、化学費用の使用量、購入コストを押さえることができ、排出された畜産糞尿の処理も可能になり、処理費の抑制にも実現する。大規模農場、極めて経済的に経営することを可能にする。
(2)添加物:実施例1の添加物と同じものである。
(1) Livestock manure: 2 ton / 10 ares The above livestock manure weight may be proportionally increased or decreased according to the area of the field to be fertilized. For example, 20 tons of livestock manure is used in a 1 hectare field. With this method, compost from a vast field can be produced in the field in a short period of time, and the production time of compost, the amount of chemical costs used, and the purchase cost can be reduced, and the discharged livestock manure is treated. This also makes it possible to reduce processing costs. Large farms that make it extremely economical to operate.
(2) Additive: Same as the additive in Example 1.

(3)製造工程
1)堆肥の短期製造方法11は、前処理工程12と、一次発酵工程13と、二次発酵工程14とからなる。
(3) Manufacturing process 1) The compost short-term manufacturing method 11 includes a pretreatment process 12, a primary fermentation process 13, and a secondary fermentation process 14.

2)前処理工程12(畜産糞尿の圃場への搬入)
圃場に、畜産糞尿を搬入し、実施例1と同じ添加物を混合し、畜産糞尿が2トンであれば、縦横約3m×3m、厚さ約20−30cmに積む。
2) Pretreatment process 12 (carrying livestock manure into the field)
Livestock manure is carried into the field, the same additives as in Example 1 are mixed, and if the livestock manure is 2 tons, it is stacked in a length of about 3 m × 3 m and a thickness of about 20-30 cm.

3)一次発酵工程13
一次発酵13は、図3に示すように、畜産糞尿と添加物と土壌の混合物を1〜2日に1回撹拌し、1週間ほど主に好気アルカリ発酵を促し、畜産糞尿を分解させる。一次発酵では混合物が70〜80℃まで達温し、そのころを一次発酵の終点とする。アルカリ性と高熱により、一次発酵の微生物菌相が選択され、堆肥化に好適な環境が整えられる。一次発酵では、土壌上に載置され、大気中に水分も拡散しやすいことから、4日程度で、畜産糞尿はカラカラに乾燥する。そのため、発酵が進行する程度に、水分を噴霧する。その際、1重量%濃度の黒糖蜜液を噴霧すると発酵がより早く進む。また、微生物酵素液を加えてもよい。
3) Primary fermentation process 13
As shown in FIG. 3, the primary fermentation 13 stirs a mixture of livestock manure, additive, and soil once every 1 to 2 days, mainly promotes aerobic alkaline fermentation for about 1 week, and decomposes livestock manure. In the primary fermentation, the mixture reaches a temperature of 70 to 80 ° C., and that time is regarded as the end point of the primary fermentation. Due to the alkalinity and high heat, the microbial flora of primary fermentation is selected, and an environment suitable for composting is prepared. In primary fermentation, since it is placed on soil and moisture easily diffuses into the atmosphere, livestock excreta is dried in about 4 days. Therefore, water is sprayed to such an extent that fermentation proceeds. At that time, the fermentation proceeds faster when sprayed with 1% by weight brown molasses. Further, a microbial enzyme solution may be added.

4)二次発酵工程14
二次発酵工程14は、図3に示すように、米糠、大豆かすを追加して、さらに、混合物を土壌とともに1〜2日に1回撹拌し、1週間ほど主に好気アルカリ発酵を促す。米糠、大豆かすの追加は、一次発酵で微生物増殖に消費された栄養素を補充し、施肥後の土壌微生物、作物の栄養源であるとともに、乳酸菌を混合物に補充するために行う。二次発酵物は、堆肥16(元肥)となり、直接圃場に施肥することができる。二次発酵中期以後後、混合物から、ほとんど悪臭はしない。
4) Secondary fermentation process 14
As shown in FIG. 3, the secondary fermentation process 14 adds rice bran and soybean meal, and further stirs the mixture with the soil once every 1 to 2 days to promote mainly aerobic alkaline fermentation for about one week. . Rice bran and soybean meal are added to supplement the nutrients consumed for microbial growth in the primary fermentation, as well as to supply soil microorganisms and nutrients for the crop, and to supplement the mixture with lactic acid bacteria. The secondary fermented product becomes compost 16 (original fertilizer) and can be directly applied to the field. After the middle stage of secondary fermentation, there is almost no odor from the mixture.

5)堆肥16
圃場に10アールに、散布し、トラクターに牽引されるロータリで圃場に鋤込まれる。
5) Compost 16
It is sprayed on the field at 10 ares and is swallowed into the field by a rotary driven by a tractor.

耕作放棄地の短期農地化方法21(雑草少)
耕作放棄地といっても、雑草が生い茂り、そのままでは、農作物の栽培が直ちに行えない、圃場、未開拓地も含むものである。
Short-term farmland conversion method 21 (low weeds)
Abandoned cultivated land includes overgrown fields and uncultivated land where weeds grow overgrown and crops cannot be cultivated immediately.

(1)
そこで、本発明である耕作放棄地の短期農地化方法21は早期農地化を可能とすべく、雑草粉砕工程22と、添加物散布工程23と、荒耕し工程24と、微生物酵素混合工程25と、表層仕上げ工程26とからなり、その後、播種・苗植え工程27が可能になる。
(1)
Therefore, the short-term farmland conversion method 21 of the abandoned farmland according to the present invention enables the early farming, the weed grinding process 22, the additive spraying process 23, the roughing process 24, the microbial enzyme mixing process 25, And the surface finishing step 26, and then the sowing / seedling planting step 27 becomes possible.

(2)雑草粉砕工程22
雑草粉砕工程22は、ハンマーナイフで、耕作放棄地の雑草を切断、粉砕し、圃場表面に散乱させる工程である。粉砕された雑草は、土壌に混合し、発酵、分解させ、作物の肥料にする。
(2) Weed grinding step 22
The weed crushing step 22 is a step of cutting, crushing the weeds in the abandoned cultivated land with a hammer knife and scattering the weeds on the field surface. The ground weed is mixed with soil, fermented and decomposed into crop fertilizer.

(3)添加物散布工程23
添加物散布工程23は、実施例1の添加物を、実施例1同様に、10アール当たり、0.2〜0.5トン散布する工程である。
(3) Additive spraying step 23
The additive spraying step 23 is a step of spraying the additive of Example 1 in an amount of 0.2 to 0.5 ton per 10 ares as in Example 1.

(4)荒耕し工程24
荒耕し工程24は、トラクターで牽引されるプラウなどで、圃場土を30cm程度の深さで、耕起、反転する工程である。刃で土を切断した後、切り出された土をモールドボードに沿ってすり上げ、下層の土が地表にくるように反転させる。圃場土の上下が反転することによって、雑草粉砕物が土中に鋤込まれ埋まるとともに下層の有機物の分解が早める。耕起、反転の後、3週間放置する。この間に、雑草、添加物は、分解が進む。
(4) Roughing process 24
The rough plowing step 24 is a step of plowing and inverting the field soil at a depth of about 30 cm with a plow pulled by a tractor. After cutting the soil with a blade, the cut soil is lifted along the mold board and inverted so that the underlying soil is on the ground. By reversing the top and bottom of the field soil, the weed pulverized material is buried in the soil and buried, and the decomposition of the organic matter in the lower layer is accelerated. Leave for 3 weeks after plowing and turning. During this time, weeds and additives are decomposed.

(5)微生物酵素混合工程25
微生物酵素混合工程25は、麹又は微生物酵素発酵液(微生物酵素)を散布し、表面を混合する工程であり、添加物とともに粉砕された雑草を発酵、分解させる。例えば、醤油の種麹を増殖させた小麦麹の残渣又は/及び味噌の種麹を増殖させた大麦麹の残渣を圃場10アール当たり50〜150kg投入する。麹に換え、或いは麹とともに、実施例1のバイオバランス、或いは/及びぼかしを散布してもよい。その後、プラウで耕耘された土は帯状または大きな土塊であるので、ロータリ等で圃場の表層10−20cm程度の土壌を砕き、表面を荒く均す。この後、約2週間放置する。この間に、雑草、添加物の分解を促進させる。
(5) Microbial enzyme mixing step 25
The microbial enzyme mixing step 25 is a step of spraying straw or a microbial enzyme fermentation liquid (microbial enzyme) and mixing the surface, fermenting and decomposing the weed pulverized with the additive. For example, 50 to 150 kg of wheat bran residue in which soy sauce seed meal is grown and / or barley koji residue in which miso seed meal is grown is introduced per 10 ares. The biobalance or / and blur of Example 1 may be sprayed instead of the cocoon or together with the cocoon. After that, since the soil cultivated with plow is a strip or a large lump of soil, the surface of the surface layer of about 10-20 cm is crushed with a rotary or the like to roughen the surface roughly. Then leave it for about 2 weeks. During this time, the decomposition of weeds and additives is promoted.

(6)表層仕上げ工程26
種子の播種、或いは苗の移植が容易になるように、圃場表面を均す工程である。これで、農地化は完了する。この後、播種、苗植えを行えば、作物栽培を開始することができる。当該方法であれば、約1ヶ月で、耕作放棄地(雑草が少ない場合、概ね雑草の地上部の重量が3kg/mより少ない場合である)を農地として利用できる。
(7)播種・苗植え工程27
基本的に、その土地で栽培可能な作物を栽培することができ、特別な種類、品種に限定されることはない。
(6) Surface finishing step 26
This is a step of leveling the field surface so that seed sowing or seedling transplantation is facilitated. This completes the farming. After this, if sowing and seedling planting are performed, crop cultivation can be started. If it is the said method, cultivation abandoned land (when there are few weeds, it is a case where the weight of the above-ground part of weeds is generally less than 3 kg / m < 2 >) can be utilized as farmland in about one month.
(7) Sowing / seedling planting process 27
Basically, crops that can be grown on the land can be cultivated and are not limited to special types and varieties.

耕作放棄地の短期農地化方法31(雑草多)
本発明である耕作放棄地の短期農地化方法31は、一層の早期農地化を可能とすべく、雑草粉砕工程22と、微生物酵素散布工程32と、混合工程35と、表層仕上げ工程26とからなり、その後、播種・苗植え工程27が可能になる。
Short-term farmland production method 31 (many weeds)
The short-term farmland conversion method 31 of the abandoned cultivated land according to the present invention includes a weed crushing step 22, a microbial enzyme spraying step 32, a mixing step 35, and a surface finishing step 26 in order to enable further early farming. After that, the sowing / seedling planting step 27 becomes possible.

なお、雑草粉砕工程22、表層仕上げ工程26、播種・苗植え工程27は、実施例3と同じである。   The weed grinding step 22, the surface finishing step 26, and the sowing / seedling planting step 27 are the same as in the third embodiment.

また、当該方法は、雑草多い場合、概ね雑草の地上部の重量が3kg以上/m以上の密度で生い茂った耕作放棄地に適用できる。雑草としては、イネ科植物(笹、竹も含む)が最適である。イネ科植物は、葉にガラス質(ケイ素源)を多く含み、栽培作物の葉を丈夫にし、病害虫への抵抗性を高める。 In addition, when there are many weeds, the method can be applied to abandoned cultivated land where the weight of the above-ground part of the weeds is overgrown with a density of 3 kg / m 2 or more. As the weeds, gramineous plants (including straw and bamboo) are the most suitable. Gramineae plants contain a lot of vitreous (silicon source) in their leaves, making the cultivated crops durable and increasing their resistance to pests.

微生物酵素散布工程32
微生物酵素散布工程32は、実施例3における微生物酵素混合工程25の麹又は微生物酵素発酵液を散布する工程である。これらが、種子の発芽、苗の生育を阻害することなく、同時に、粉砕された雑草を分解、肥料化させる。
Microbial enzyme spraying process 32
The microbial enzyme spraying step 32 is a step of spraying the straw of the microbial enzyme mixing step 25 in Example 3 or the microbial enzyme fermentation broth. These break down and fertilize the crushed weeds simultaneously without inhibiting seed germination and seedling growth.

混合工程33
混合工程33は、微生物酵素が散布された雑草粉砕物を土壌に鋤込む工程で、トラクターのロータリで土壌の表層10−20cmを撹拌する。鋤込まれた雑草粉砕物が、微生物酵素によって分解され、栽培作物の元肥となる。
Mixing step 33
The mixing step 33 is a step of pouring the weed pulverized material sprayed with microbial enzymes into the soil, and agitates the surface layer of 10-20 cm with the rotary of the tractor. The crushed weeds that have been incorporated are decomposed by microbial enzymes and become the basic fertilizer for cultivated crops.

このようにしてなる耕作放棄地の短期農地化方法31では、雑草粉砕工程22から播種・苗植え工程27を一日で行うことができる。これまでの常識では、雑草を圃場に鋤込んだ場合には、所定の期間、放置して雑草の分解、分解熱、作物にとって有害ガスが除かれた後、播種・苗植え工程をとるのが常識であった。   In the short-term farmland conversion method 31 of the abandoned cultivated land thus formed, the sowing and seedling planting steps 27 to 27 can be performed in one day. Conventional common sense is that when weeds are planted in the field, they are left to stand for a predetermined period of time, after which weed decomposition, heat of decomposition, and harmful gases for crops are removed, followed by sowing and seedling planting processes. It was common sense.

しかしながら、微生物酵素を雑草粉砕物に散布した後、土壌に鋤込むことで、直ちに、種子の播種・苗の移植が可能であることが確認された。雑草粉砕物は分解され、生命活動がある種子、苗は分解されず、生育可能になる。そのメカニズムはこれからの研究が待たれるが、微生物酵素、とりわけ、小麦麹を用いた場合、何らかの選択が働き、例えば、分解に伴う発熱を抑え、或いは有毒ガスを抑制或いは生成を回避させ、又は、それらの複合現象、或いは知られていない新たな現象によって、雑草分解物は分解され、種子、苗は分解されることなく或いは発芽を抑制させることなく、生育可能になっている。   However, it was confirmed that seeding of seeds and transplanting of seedlings were immediately possible by spraying microbial enzymes on ground weeds and then pouring them into the soil. The weed pulverized product is decomposed, and the seeds and seedlings having vital activities are not decomposed and become viable. The mechanism is awaiting further research, but when using microbial enzymes, especially wheat straw, some choices work, for example, suppressing the fever associated with decomposition, or suppressing or avoiding the generation of toxic gases, or By these complex phenomena or new unknown phenomena, weed decomposition products are decomposed, and seeds and seedlings can be grown without being decomposed or suppressing germination.

これにより、雑草の処理簡素化、肥料化、それに伴う肥料コストの削減、農地化までの待機時間の削減、それにともなる早期収入を可能にし、耕作放棄地の実現可能な問題解決手段を提供することができる。   This simplifies the processing of weeds, makes fertilizers, reduces the costs of fertilizer associated therewith, reduces the waiting time until farming, and provides early income, thereby providing a feasible solution to the problem of abandoned farmland be able to.

耕作放棄地の短期農地化方法31の様子撮影した写真を、図6に掲載した。(A)雑草が、生い茂った耕作放棄地の風景である。(B)は、荒耕し(30センチ深さで上下反転耕起)の風景である。ここでは、雑草粉砕工程後、微生物酵素散布前に、荒耕し工程を加えたが、荒耕し工程は必須ではない。(C)は、醤油用種麹(小麦麹)の残渣を散布している風景である。   A photograph taken during the short-term farmland conversion method 31 in abandoned farmland is shown in FIG. (A) A landscape of abandoned farmland where weeds are overgrown. (B) is a landscape of rough plowing (upside down plowing at a depth of 30 cm). Here, after the weed crushing process, but before the microbial enzyme application, a rough tilling process was added, but the rough tilling process is not essential. (C) is a landscape where the residue of soy sauce seed meal (wheat meal) is sprayed.

その後、圃場表面をロータリで、均し、ラッカセイの種を播種した。その後、実施例区では、4日後に発芽が確認できた。発芽率は、ほぼ100%であったの対して、比較例(微生物酵素散布工程32なし)では、4日目には発芽はまったく確認できなかった。   Then, the field surface was leveled with a rotary, and seeds of groundnut were sown. Thereafter, germination could be confirmed after 4 days in the example section. The germination rate was almost 100%, whereas no germination was confirmed on the fourth day in the comparative example (without the microbial enzyme spraying step 32).

雑草を利用した短期農地化方法
図7に、雑草が生い茂った圃場を整地し、直ちに、ラッカイセイの種子を播種し、その生育を観察した写真を掲載した。
Short-term farmlandization method using weeds Fig. 7 shows a field where weeds were cultivated and immediately seeded with seeds of sea oysters and their growth was observed.

図7に示すように、背丈ほど雑草が生い茂っている圃場(奥実施例区、手前比較例区)の雑草(1)を、ハンマーナイフ34で、切断し、試験区に放置し、その上に、実施例区では実施例3の微生物酵素と米糠を散布(5)し、耕耘、すなわち切断した雑草を土壌に鋤込んだ(3)。このとき、地上部の雑草重量は、6.56kg/mであった(2014年6月25日)。なお、比較例区では、微生物酵素と米糠を散布していない。 As shown in FIG. 7, the weed (1) in the field (the back example section, the front comparative example section) where weeds grow as much as the height is cut with a hammer knife 34 and left in the test section, In the Example section, the microbial enzyme and rice bran of Example 3 were sprayed (5), and plowed, that is, cut weeds were put into the soil (3). At this time, the weed weight of the above-ground part was 6.56 kg / m 2 (June 25, 2014). In the comparative example, microbial enzymes and rice bran are not sprayed.

その後、直ちに、実施例区及び比較例区において、ラッカセイ(おおまさり)の種子を播種した(4)。   Immediately thereafter, peanut seeds were sown in the example group and the comparative example group (4).

実施例区では播種から4日目に発芽(5)、比較例は播種から10日目にやっと発芽が確認できた(6)。写真(6)からわかるように、実施例区では雑草の生育も旺盛であるが、比較例区では雑草の生育も極めて少ない。この結果は、従来から知られている、雑草を鋤込んだ後の圃場では作物の生育が悪いことと一致した。   In the example group, germination was confirmed on the fourth day after sowing (5), and in the comparative example, germination was finally confirmed on the tenth day after sowing (6). As can be seen from the photograph (6), weed growth is strong in the example section, but weed growth is very small in the comparative section. This result was consistent with the conventionally known poor growth of crops in fields after weeds were introduced.

他方、微生物酵素(ここでは麹)を散布した実施例区では、生の雑草を鋤込んでも、切断された雑草は分解され、種子は分解されることなく発芽し、順調に成長した(7)。   On the other hand, in the example section where the microbial enzyme (here, cocoon) was sprayed, even if raw weeds were swallowed, the cut weeds were decomposed, the seeds were germinated without being decomposed, and grew smoothly (7) .

このことは、切断した雑草を栽培圃場に鋤込むことで、肥料として利用できる可能性を示唆している。したがって、雑草を十分成長させることで、光合成による有機物の蓄積量を増やし、肥料価値を高め、直ちに種子の播種、苗の移植を可能にする新たな農法が開拓されたと言える。
従来繁茂した雑草は、コストをかけ圃場から除去していたが、本発明では、除去コストがかからない上、肥料として利用でき、簡易かつ低コスト農法を可能にする。
This suggests the possibility of using the cut weeds as fertilizer by plowing them into the cultivation field. Therefore, it can be said that by fully growing weeds, a new farming method has been pioneered that increases the amount of organic matter accumulated by photosynthesis, increases the fertilizer value, and enables seed sowing and seedling transplantation immediately.
Conventionally weeds have been removed from the field at a high cost. However, in the present invention, the removal costs are not required, and they can be used as fertilizers, enabling a simple and low-cost farming method.

汚染土壌の農地利用方法41
本発明である汚染土壌の農地利用方法41は、図8に示すように、耕作放棄地の短期農地化方法21、31と、バイオ燃料用作物栽培42と、バイオマス43の収穫と、バイオ燃料製造44とからなり、バイオ燃料を得る。
How to use contaminated soil in farmland 41
As shown in FIG. 8, the contaminated soil farmland utilization method 41 according to the present invention includes short-term farmland production methods 21 and 31, biofuel crop cultivation 42, biomass 43 harvesting, and biofuel production as shown in FIG. 8. 44 to obtain biofuel.

汚染物質が基準を超えて検出される汚染土壌においては、耕作放棄地と同様に、雑草が生い茂り、直ちに、耕作地として使用できない。汚染物質としては、水銀、カドミウム、銅などの金属物質、放射性物質などが周知である。   In contaminated soil where pollutants are detected in excess of the standard, weeds overgrow, just like abandoned farmland, and cannot be used immediately as farmland. Known contaminants include mercury, cadmium, copper and other metallic materials, radioactive materials, and the like.

次に、圃場として整地できても、そこで栽培された作物は、人の摂取が許容される基準濃度を超えて汚染物質が検出するため、人が摂取する作物として流通、販売することができない。   Next, even if the ground can be leveled, the crops cultivated there cannot be distributed and sold as crops for human consumption because pollutants are detected in excess of a standard concentration that is acceptable for human consumption.

汚染土壌を耕作地として使用する場合、先ず、圃場に生い茂った雑草の除去、一定期間放置して農作物の栽培圃場とする必要があった。また、必要に応じて、従来は、土壌の入れ換えを行っていた。そして、この期間、作物栽培による収入が得られないことが問題であった。汚染土壌の農地化は、多大な費用と、時間を要し、ほとんど実施できないのが現状である。   When using contaminated soil as cultivated land, it was first necessary to remove the weeds that had grown in the field and leave it for a certain period of time to become a farming field for crops. Moreover, conventionally, the soil was replaced as needed. And it was a problem that the income from crop cultivation cannot be obtained during this period. The conversion of contaminated soil into agricultural land is very expensive and time consuming, and it can hardly be implemented.

そこで、本発明である耕作放棄地の短期農地化方法21、31によって、短期間で農地として整地し、短期或いは直ちに、播種・苗植え工程27を行い、作物栽培を開始する。その際、選択する作物は、人が摂取することを目的とせず、バイオ燃料45となり得る、澱粉、糖質の多い作物を選択し、バイオ燃料用作物栽培42をする。   Therefore, by the short-term farmland conversion methods 21 and 31 of the abandoned farmland according to the present invention, the farmland is leveled in a short period of time, and the sowing / seedling planting step 27 is performed in a short period or immediately to start crop cultivation. At that time, the crop to be selected is not intended to be ingested by humans but is selected from crops rich in starch and sugar that can become the biofuel 45, and the crop 42 for biofuel is grown.

収穫されたバイオマス43(果実由来の澱粉、糖質分等、葉、茎由来のセルロース分等)は、それぞれ、既知の化学的、微生物的発酵手法(バイオ燃料製造44)により、バイオエタノールなどのバイオ燃料45に変換する。   The harvested biomass 43 (such as fruit-derived starch, carbohydrates, leaves, stem-derived cellulose, etc.) is converted into bioethanol or the like by known chemical and microbial fermentation methods (biofuel production 44), respectively. Convert to biofuel 45.

これにより、短期農地化、作物栽培による短期の収入を可能にし、流通基準を超える汚染物質濃度により、作物栽培制限を受けている土地においても、農作物の栽培が可能になり、汚染土壌の農地利用を可能にするとともに、汚染土壌の耕作放棄地化を防止することが可能になる。   This enables short-term farmland and short-term income from crop cultivation, and enables the cultivation of crops even on land that is subject to crop cultivation restrictions due to the concentration of pollutants exceeding the distribution standards. It becomes possible to prevent abandoned cultivation of contaminated soil.

また、汚染物質が、バイオマスに濃縮され、回収することができるとともに、土壌を入れ換えることなく、汚染土壌において、汚染物質の濃度が低下し、人が摂取できる通常の農作物の栽培を短期に実現することもできるようになる。   In addition, the pollutants can be concentrated and recovered in biomass, and the concentration of pollutants in the contaminated soil can be reduced and the cultivation of ordinary crops that can be consumed by humans can be realized in a short time without replacing the soil. You can also do that.

1 堆肥の短期製造方法
2 前処理工程
3 一次発酵工程
4 二次発酵工程
5 三次発酵工程
6 堆肥
11 堆肥の短期製造方法
12 前処理工程
13 一次発酵工程
14 二次発酵工程
16 堆肥
21 耕作放棄地の短期農地化方法
22 雑草粉砕工程
23 添加物散布工程
24 荒耕し工程
25 微生物酵素混合工程
26 表層仕上げ工程
27 播種・苗植え工程
31 耕作放棄地の短期農地化方法
32 微生物酵素散布工程
33 混合工程
34 ハンマーナイフ
41 汚染土壌の農地利用方法
42 バイオ燃料用作物栽培
43 バイオマス
44 バイオ燃料製造
45 バイオ燃料
1 Compost short-term production method 2 Pretreatment process 3 Primary fermentation process 4 Secondary fermentation process 5 Tertiary fermentation process 6 Compost 11 Compost 11 Short-term production method 12 Pretreatment process 13 Primary fermentation process 14 Secondary fermentation process 16 Compost 21 Abandoned farmland Short-term farmland conversion method 22 Weed grinding process 23 Additive spraying process 24 Rough plowing process 25 Microbial enzyme mixing process 26 Surface layer finishing process 27 Seeding and seedling planting process 31 Short-term farming method of abandoned farmland 32 Microbial enzyme spraying process 33 Mixing process 34 Hammer knife 41 Agricultural land utilization method 42 Biofuel crop cultivation 43 Biomass 44 Biofuel production 45 Biofuel

Claims (15)

屋根付きコンクリート床で堆肥を短期に製造する方法であって、
畜産糞尿と麹を含む添加物を混合した混合物を厚さ20−30cmで積む前処理工程と、
前記混合物を5−8日間毎日或いは1日おきに撹拌し好気発酵させる一次発酵工程と、
一次発酵物に米糠及び大豆かすを追加して5−8日間毎日或いは1日おきに撹拌し好気発酵させる二次発酵工程と、
からなることを特徴とする堆肥の短期製造方法。
A method of manufacturing compost on a covered concrete floor in a short time,
A pretreatment step of laminating a mixture of livestock manure and additives containing sputum at a thickness of 20-30 cm;
A primary fermentation step in which the mixture is aerobically fermented by stirring for 5-8 days every day or every other day;
A secondary fermentation process in which rice bran and soybean meal are added to the primary fermented product and stirred for 5 to 8 days every day or every other day for aerobic fermentation;
A method for the short-term production of compost characterized by comprising:
圃場で堆肥を短期に製造する方法であって、
畜産糞尿と麹を含む添加物と土壌を混合した混合物を厚さ20−30cmで積む前処理工程と、
前記混合物の水分調整をしながら5−8日間毎日或いは1日おきに撹拌し好気発酵させる一次発酵工程と、
一次発酵物に米糠及び大豆かすを追加して5−8日間毎日或いは1日おきに撹拌し好気発酵させる二次発酵工程と、
からなることを特徴とする堆肥の短期製造方法。
A method for producing compost in the field in a short time,
A pre-treatment step of stacking a mixture of an additive containing livestock manure and straw and soil in a thickness of 20-30 cm;
A primary fermentation step of aerobic fermentation by stirring daily or every other day for 5-8 days while adjusting the water content of the mixture;
A secondary fermentation process in which rice bran and soybean meal are added to the primary fermented product and stirred for 5 to 8 days every day or every other day for aerobic fermentation;
A method for the short-term production of compost characterized by comprising:
前記添加物に、カキ殻が含まれることを特徴とする請求項1又は請求項2に記載の堆肥の短期製造方法。 The method for producing a compost for a short time according to claim 1 or 2, wherein the additive contains oyster shells. 前記添加物が、
畜産糞尿2トン当たり、
米糠 100〜300kg
大豆かす 50〜100kg
カキ殻 30〜 80kg
ケイ素源 10〜 30kg
カニ殻 30〜 50kg
麹 50〜200kg
であることを特徴とする請求項1又は請求項2に記載の堆肥の短期製造方法。
The additive is
Per 2 tons of livestock manure,
100-300kg of rice bran
Soy meal 50-100kg
Oyster shell 30-80 kg
Silicon source 10-30kg
Crab shell 30-50kg
〜 50-200kg
The method for short-term production of compost according to claim 1 or 2, wherein:
前記麹が、種麹を増殖させた残渣であることを特徴とする請求項1〜請求項3の何れか1項に記載の堆肥の短期製造方法。 The method for producing a compost for a short time according to any one of claims 1 to 3, wherein the cocoon is a residue obtained by growing seed pods. 前記ケイ素源が、笹又は竹であることを特徴とする請求項4に記載の堆肥の短期製造方法。 The method for producing a compost for a short time according to claim 4, wherein the silicon source is straw or bamboo. 地上部が3kg/mより少ない密度で雑草が生い茂った耕作放棄地の農地化方法であって、
雑草を粉砕する雑草粉砕工程と、
圃場10アール当たり、以下の添加物を0.2〜0.5トン投入する添加物散布工程と、
米糠 100〜300kg
大豆かす 50〜100kg
カキ殻 30〜 80kg
ケイ素源 10〜 30kg
カニ殻 30〜 50kg
麹 50〜200kg
粉砕した雑草と添加物と土壌を混合し、3週間放置する荒耕し工程と、
圃場10アール当たり、以下の微生物酵素を散布、混合し、2週間放置する微生物酵素混合工程と、
圃場表層をロータリで均す表層仕上げ工程と、
からなり、
表層仕上げ工程後、直ちに、作物の播種・苗植えを可能とした耕作放棄地の農地化方法。
A method for converting abandoned cultivated land where the above-ground part has a density of less than 3 kg / m 2 and overgrown with weeds,
A weed crushing process for crushing weeds;
An additive spraying process in which 0.2 to 0.5 tons of the following additives are added per 10 ares of a field,
100-300kg of rice bran
Soy meal 50-100kg
Oyster shell 30-80 kg
Silicon source 10-30kg
Crab shell 30-50kg
〜 50-200kg
A rough tilling process in which ground weeds, additives and soil are mixed and left for 3 weeks,
A microbial enzyme mixing process in which the following microbial enzymes are sprayed, mixed, and allowed to stand for 2 weeks per 10 ares of field:
A surface finishing process to level the field surface with a rotary,
Consists of
A method for converting abandoned cultivated land into farmland that enables seeding and seedling planting of crops immediately after the surface finishing process.
地上部が3kg以上/mの密度で雑草が生い茂った耕作放棄地の農地化方法であって、
雑草を粉砕する雑草粉砕工程と、
微生物酵素を散布する工程と、
粉砕した雑草と散布した微生物酵素と土壌を混合する混合工程と、
圃場表層をロータリで均す表層仕上げ工程と、
からなり、
前記雑草粉砕工程〜表層仕上げ工程まで1日で行い、表層仕上げ工程後、直ちに、作物の播種・苗植えを可能とした耕作放棄地の農地化方法。
A method for converting abandoned cultivated land where the above-ground part has a density of 3 kg / m 2 or more and overgrown with weeds,
A weed crushing process for crushing weeds;
Spraying microbial enzymes;
A mixing step of mixing the crushed weeds and the sprayed microbial enzyme with the soil;
A surface finishing process to level the field surface with a rotary,
Consists of
A method for converting abandoned cultivated land into a farmland, which is performed in one day from the weed pulverization step to the surface finishing step, and immediately after the surface finishing step, it is possible to sow and plant seedlings.
前記微生物酵素が、醤油の種麹を増殖させた小麦麹の残渣又は/及び味噌の種麹を増殖させた大麦麹の残渣(圃場10アール当たり50〜150kg)、であることを特徴とする請求項7又は請求項8に記載の耕作放棄地の農地化方法。 The microbial enzyme is a residue of wheat straw or soy sauce seed cake grown with soy sauce seed meal (and 50 to 150 kg per 10 ares of field). Item 7. The method for converting abandoned farmland into a farmland according to Item 7 or Claim 8. 汚染土壌に、バイオ燃料の原料となる作物を栽培し、得られたバイオマスからバイオ燃料を生成することを特徴とする汚染土壌の農地利用方法。 A method for using contaminated soil in farmland, comprising cultivating a crop as a raw material for biofuel on contaminated soil and generating biofuel from the obtained biomass. 前記汚染土壌を、請求項7〜請求項9の何れか1項に記載の耕作放棄地の短期農地化方法によって、整地、圃場化した後に、前記作物の栽培を開始することを特徴とする請求項10に記載の汚染土壌の農地利用方法。 The cultivation of the crop is started after the contaminated soil is leveled and fielded by the short-term farming method of abandoned farmland according to any one of claims 7 to 9. Item 10. A method for using contaminated soil in farmland. 前記バイオエタノールの生成に伴い、前記汚染物質を濃縮、回収し、汚染土壌の汚染物質濃度を低下させることを特徴とする請求項10又は請求項11に記載の汚染土壌の農地利用方法。 The method for using contaminated soil in farmland according to claim 10 or 11, wherein the pollutant is concentrated and collected as the bioethanol is produced to reduce the pollutant concentration in the contaminated soil. 請求項10又は請求項11に記載の方法によって、得られたことを特徴とするバイオ燃料。 A biofuel obtained by the method according to claim 10 or 11. 請求項1〜請求項6の何れか1項に記載の堆肥の短期製造方法で得られたことを特徴とする堆肥。 A compost obtained by the short-term production method for compost according to any one of claims 1 to 6. 請求項14に記載の堆肥と、粘土質を多く含む建設残土を混合したことを特徴とする土壌改良材。 A soil improver comprising the compost according to claim 14 mixed with construction residual soil containing a large amount of clay.
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CN107082535A (en) * 2017-05-31 2017-08-22 安徽永志环能科技有限公司 Livestock and poultry cultivation night soil biological treatment utilization process
JP2019109144A (en) * 2017-12-19 2019-07-04 株式会社ダイワ Decontamination reagent of radioactive contamination and production method thereof
JP2020153749A (en) * 2019-03-19 2020-09-24 高嶋 康豪 Soil modification method
JP2020184912A (en) * 2019-05-13 2020-11-19 石坂産業株式会社 Plant cultivation soil

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JP2005296835A (en) * 2004-04-13 2005-10-27 Hideo Hasegawa Method for treating animal feces and urine
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Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN107082535A (en) * 2017-05-31 2017-08-22 安徽永志环能科技有限公司 Livestock and poultry cultivation night soil biological treatment utilization process
JP2019109144A (en) * 2017-12-19 2019-07-04 株式会社ダイワ Decontamination reagent of radioactive contamination and production method thereof
JP2020153749A (en) * 2019-03-19 2020-09-24 高嶋 康豪 Soil modification method
JP2020184912A (en) * 2019-05-13 2020-11-19 石坂産業株式会社 Plant cultivation soil

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