JP2009126776A - Manufacturing method of fermented fertilizer and fermented fertilizer - Google Patents

Manufacturing method of fermented fertilizer and fermented fertilizer Download PDF

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JP2009126776A
JP2009126776A JP2007331027A JP2007331027A JP2009126776A JP 2009126776 A JP2009126776 A JP 2009126776A JP 2007331027 A JP2007331027 A JP 2007331027A JP 2007331027 A JP2007331027 A JP 2007331027A JP 2009126776 A JP2009126776 A JP 2009126776A
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Hiromichi Hara
弘道 原
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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
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W10/00Technologies for wastewater treatment
    • Y02W10/20Sludge processing
    • 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
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W30/00Technologies for solid waste management
    • Y02W30/50Reuse, recycling or recovery technologies
    • Y02W30/78Recycling of wood or furniture waste

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Abstract

<P>PROBLEM TO BE SOLVED: To provide a manufacturing method of an organic fertilizer capable of quickly fermenting and decomposing hardly decomposable organic resources such as grassy species. <P>SOLUTION: A silicic acid layer of a chaff is solubilized and an outer wall is made weak by an enzyme liquid obtained by subjecting a sewage disposal water to an enzyme/yeast treatment. Then fermentation and decomposition are promoted by placing under an aerobic condition by adding a rice bran and an enzyme/yeast mixture. A crushed product of the grassy species such as a straw, a heart of a maize and a bamboo can be similarly fermented and decomposed. A fermented chaff can be used as an effective fermentation/decomposition-treating agent for circulating organic resources such as a garbage containing fish, meat etc and a livestock wastesince fungi live in the fermented chaff and various enzymes also remain. <P>COPYRIGHT: (C)2009,JPO&INPIT

Description

本発明は、下水処理施設から排出される下水処理水を加工することによって、難分解性の有機資源、とくにイネ科植物を迅速に発酵・分解する技術である。  The present invention is a technique for rapidly fermenting and decomposing persistent organic resources, particularly gramineous plants, by processing sewage treated water discharged from a sewage treatment facility.

また本発明は、発酵分解されたイネ科植物によって、生ゴミや畜糞等の未利用有機資源を迅速に処理する技術である  In addition, the present invention is a technique for rapidly treating unused organic resources such as raw garbage and livestock excreta by fermented and decomposed gramineous plants.

さらに本発明は、水溶性ケイ酸含量の多い有機発酵肥料の製造方法である。  Furthermore, this invention is a manufacturing method of the organic fermented fertilizer with much water-soluble silicic acid content.

イネ科植物はその生長過程でケイ酸を多量に吸収するためにケイ酸植物とも呼称され,根から吸収されたケイ酸は表皮細胞の外壁にケイ酸層(図1)として集積し、もみ殻のケイ酸含有率は20.3%に達する。
イネのもみ殻は収穫した子実から食用とする玄米をのぞいた残渣であり、開花時における内穎と外穎に由来する。内外穎の厚壁組織は強くリグニン化するとともに、外表皮には多量のケイ酸が蓄積し、さらにこれらをクチクラ膜が覆って強固な外壁を形成している(図1)ために土壌中の微生物に分解され難く、堆肥として利用するためには1〜2年を要する。
一方、もみ殻に含まれるケイ酸は植物の細胞壁を強化する作用があり、イネ以外の作物においてもケイ酸質肥料の施用によって「うどん粉病」などの病害発生を抑制することが知られている(図2)。
日本の米生産量は年間約1000万トンであり、精米時には約200万トンのもみ殻が排出される。そして、そのうちの35%にあたる約70万トンが未利用のまま焼却処分されているとされている(平成16年:農林水産省生産局農産振興課)(図3)
もみ殻の焼却は煤煙による周囲環境へ影響を与えるばかりか、地球温暖化へつながる愚かな行為であり、もみ殻の持つ機能を生かす利用法の開発が期待されている。地球規模では1億2千万トンのもみ殻が排出されており、本発明の技術は日本国内にとどまらず、世界的にも注目されるだろう。
Gramineae plants are also called silicate plants because they absorb a large amount of silicic acid during their growth process, and the silicic acid absorbed from the roots accumulates as a silicic acid layer (Fig. 1) on the outer wall of the epidermis cells, The silicic acid content of this reaches 20.3%.
Rice husk is a residue obtained by removing edible brown rice from harvested grains, and is derived from inner and outer pods at the time of flowering. The thick wall tissue of the inner and outer tubules is strongly lignined, and a large amount of silicic acid accumulates in the outer epidermis, which is further covered with a cuticle membrane to form a strong outer wall (Fig. 1). It is difficult to be decomposed by microorganisms, and it takes 1 to 2 years to use it as compost.
On the other hand, silicic acid contained in rice husk has an effect of strengthening the cell wall of plants, and it is known that siliceous fertilizer is applied to crops other than rice to suppress the occurrence of diseases such as powdery mildew. (FIG. 2).
Japan's rice production is about 10 million tons per year, and about 2 million tons of rice husks are discharged during milling. And about 700,000 tons, or 35% of them, are said to be incinerated without being used (2004: Ministry of Agriculture, Forestry and Fisheries, Production Bureau, Agriculture Promotion Division) (Figure 3)
Incineration of rice husk not only affects the surrounding environment due to soot, but is also a foolish act that leads to global warming, and the development of a method for utilizing the functions of rice husk is expected. On a global scale, 120 million tons of rice husks have been discharged, and the technology of the present invention will not be limited to Japan, but will be noted worldwide.

もみ殻の利用についての特許は少なく、もみ殻を好気性の雰囲気下で発酵させて肥料とする幾つかの方法が提案されてきている。その一例は、糞尿排泄物(鶏糞、牛糞、豚糞等)に、粉砕したもみ殻(平均35メッシュ)を混合して培地を調製し、この混合培地を1日一回攪拌しながら好気性条件下での発酵および熟成を経て有機発酵肥料とする方法である(例えば、特許文献1参照)。この方法によると、11日目以後臭気が消失し、ほぼ一カ月程度で無臭化された有機発酵肥料となり、これを配合肥料として施肥すると、通常の肥料で栽培したものに比べて3倍の大きさの胡瓜が収穫されたと報告されている。  There are few patents on the use of rice husk, and several methods have been proposed for fermenting rice husk in an aerobic atmosphere. An example of this is a medium prepared by mixing crushed rice husks (average 35 mesh) with manure excrement (chicken dung, cow dung, pig dung, etc.), and aerobic conditions while stirring this mixed medium once a day This is a method for producing an organic fermented fertilizer through fermentation and aging below (see, for example, Patent Document 1). According to this method, the odor disappears after the 11th day, and it becomes an organic fermented fertilizer that has not been brominated in about one month. When this is applied as a fertilizer, it is three times larger than that cultivated with ordinary fertilizer. It is reported that Sano pepper was harvested.

また、加水しながら粉砕したもみ殻を加熱膨軟化したものに、雑草あるいは雑木を混合したものを高温発酵菌によって1次発酵し、これに、セルロースとアミロースを分解する放線菌、リグニン等を分解する白色腐朽菌等によって2次発酵を行った後、熟成及び土壌中で植物に有効な作用をするVA菌根菌と根粒菌を加えたもみ殻堆肥が提案されている(例えば、特許文献2参照)。  In addition, a mixture of weeds and weeds mixed with rice that has been crushed with water and heated and softened, is first fermented with high-temperature fermenting bacteria, and then decomposes actinomycetes that decompose cellulose and amylose, lignin, etc. Rice husk compost has been proposed in which VA mycorrhizal fungi and rhizobial fungi that have an effective action on plants in aging and soil are added after secondary fermentation with white rot fungi or the like (for example, Patent Document 2) reference).

しかしながら、上記、特許文献1および特許文献2に記載された有機発酵肥料(もみ殻堆肥)は、いずれも細かく粉砕したもみ殻を使用しているが、もみ殻はケイ酸層に加えて強くリグニン化された厚壁細胞とクチクラ層を持つ表皮組織であり、その粉砕は容易ではない。(図2)
また、特許文献1の製造法では、糞尿排泄物を使用しており、7日程度で無臭になるとはいうものの臭気の発生は避けられず、環境衛生的にも問題がある。
さらに、特許文献2のもみ殻堆肥は、糞尿排泄物等を用いない方法ではあるが、もみ殻の粉砕が容易でないことに加えて、加熱後膨軟化処理という手間のかかる前処理を必要としている。すなわち、1次発酵から2次、3次発酵に加えて、石灰乳、栄養剤あるいは、VA菌根菌及び根粒菌を混合するという複雑な工程によっている。このために経済性の点で実用化には問題があり、前記特許文献1および特許文献2に記載の技術は実用化されるまでには至っていない。
However, the organic fermented fertilizer (rice husk compost) described in Patent Document 1 and Patent Document 2 uses finely ground rice husk, but the rice husk is strongly lignin in addition to the silicic acid layer. It is an epidermal tissue with thickened thick cell and cuticle layer, and its pulverization is not easy. (Figure 2)
Moreover, in the manufacturing method of patent document 1, although excrement of manure is used, although it becomes odorless in about 7 days, generation | occurrence | production of an odor cannot be avoided, and there also exists a problem also in environmental hygiene.
Furthermore, although the rice husk compost of patent document 2 is a method which does not use manure excretion etc., in addition to not being easy to grind a rice husk, it requires the time-consuming pre-processing of a swelling softening process after a heating. . That is, in addition to primary fermentation to secondary and tertiary fermentation, lime milk, nutrients, VA mycorrhizal fungi and rhizobia are mixed. For this reason, there is a problem in practical use in terms of economy, and the techniques described in Patent Document 1 and Patent Document 2 have not yet been put into practical use.

また、もみ殻を粉砕することなく、曝気した屎尿に浸漬することによって極めて短時間でもみ殻を分解したものが、有機発酵肥料として商品化(商品名「もみがら物語」)されている。(非特許文献1参照)。この方法は、曝気処理した屎尿槽に袋詰したもみ殻を漬け込んだ後に、もみ殻を取り出し、米糠、酵素および酵母菌を加えて発酵させ、ほぼ一ヶ月程度で有機発酵肥料とするものである  In addition, a rice husk decomposed by immersing it in aerated manure without crushing the rice husk has been commercialized as an organic fermented fertilizer (trade name “Momogara Monogatari”). (Refer nonpatent literature 1). This method is to immerse the packed rice husk in the aerated urine tank, take out the rice husk, ferment with rice bran, enzyme and yeast, and make it an organic fermented fertilizer in about one month

特開昭60−137888号公報JP-A-60-137888 特開平9−268088号公報Japanese Patent Laid-Open No. 9-268088 現代農業 84巻11月号、P96〜103(2005)(参考資料1)Modern agriculture 84 volume November issue, P96-103 (2005) (reference materials 1)

本発明は農業分野で効果が期待されながら、難分解性であるために利用が限られていたもみ殻を迅速に発酵・分解させる技術の開発である。従来の堆肥化技術では複雑な工程、不十分な臭気対策、衛生面での対策等の問題があり、簡便な技術の開発が望まれていた。The present invention is the development of a technique for rapidly fermenting and decomposing rice husks, which are expected to be effective in the agricultural field, but have been limited in use due to their indegradability. Conventional composting techniques have problems such as complicated processes, insufficient odor countermeasures, and hygiene countermeasures, and the development of simple techniques has been desired.

本発明者は、下水処理施設での処理工程で使用されている活性汚泥法に着目し、処理後塩素殺菌されて排出される下水処理水にもみ殻を浸漬したところ、2〜3ヶ月の間に緩慢ではあるが徐々にもみ殻外壁が脆くなっていることを走査電子顕微鏡によって確認した。(図4)
そこで、処理水を曝気しながら各種の酵素と酵母を添加した酵素液を製造し、この酵素液にもみ殻を浸漬または/および噴霧することによってケイ酸層を可溶化し、外壁を脆くして発酵分解を促進することに成功した。(図5)
The present inventor paid attention to the activated sludge method used in the treatment process at a sewage treatment facility, and immersed rice husk in sewage treated water discharged after chlorination after treatment, for 2 to 3 months. It was confirmed by a scanning electron microscope that the outer wall of the rice husk gradually became brittle although it was slow. (Fig. 4)
Therefore, an enzyme solution in which various enzymes and yeast are added while aeration of the treated water is produced, and the silicate layer is solubilized by immersing or / and spraying rice husks in this enzyme solution to make the outer wall brittle. Succeeded in promoting fermentation degradation. (Fig. 5)

酵素液に浸漬したもみ殻を引き上げて水分を50〜60%に調整し、米糠と酵素・酵母混合物を添加して好気条件で数時間撹拌すると、もみ殻は50〜60℃に達する。    When the rice husk immersed in the enzyme solution is pulled up to adjust the water content to 50-60%, and the rice bran and enzyme / yeast mixture are added and stirred for several hours under aerobic conditions, the rice husk reaches 50-60 ° C.

その後、撹拌を停止して円錐形に堆積すると発酵が始まり60〜70℃以上に発熱するので、適宜切り返しを行えば14日間程度で耕地へ施用できる程度まで分解を進めることができる。(図6)  Thereafter, when the stirring is stopped and the cone is deposited, fermentation starts and heat is generated at 60 to 70 ° C. or higher. Therefore, decomposition can be advanced to the extent that it can be applied to cultivated land in about 14 days if it is appropriately turned over. (Fig. 6)

本発明はもみ殻の迅速な発酵・分解を目的として見いだされたものであるが、付随的にいくつかの新発見を見いだした。
(1)酵素液を使用してケイ酸層の破壊と可溶化を図った結果、発酵もみ殻に含まれる可溶性ケイ酸を増加させることが出来る。(図7)
ケイ酸肥料の効果はすでに知られていることも多いが、発酵もみ殻に含まれる可溶性ケイ酸は植物であるもみ殻に由来するものであり、仮に過剰施用が行われても安全性に問題がない。
ケイ酸の吸収が速やかに行われ、表皮細胞を強化することによって、作物栽培、とくにイチゴやトマト、キウリなどの果菜類、イモ類、ブドウなどの果樹類ではうどんこ病や線虫、果面汚点症などの被害を軽減することが出来る。また、ホウレンソウやレタスでは糖度上昇効果が認められた。(図2)
(2)発酵もみ殻には各種酵素や酵母、菌類が残存しており、水分を与えることによって再度発酵・分解を進めることが出来る。
発酵による発熱はもみ殻の水分を蒸発させ、その含量が30%以下になると発酵は緩慢となり温度も低下して、各種の微生物は乾燥菌体となって残存する現象は一般に知られていることである。
このため、イネ科の草本類に限らず、水分を調整することによって生ゴミ、各種汚泥等の未利用有機資源の発酵・分解の処理剤として応用できる。
(3)もみ殻は最も発酵・分解の困難な有機質資源として知られており、酵素液への浸漬に始まる、もみ殻の発酵・分解工程は竹や木材などの長大な有機物などでも、粉砕処理をすることによって発酵・分解を進めることができる。
(4)酵素液はもみ殻の浸漬を続けている間に発酵を続けながら酸化されて濃い茶褐色となり、可溶性ケイ酸濃度も増加する。この液は液肥として利用できるので、有害な排出物は生じない。
Although the present invention has been found for the purpose of rapid fermentation and decomposition of rice husk, several new discoveries have been found incidentally.
(1) As a result of the destruction and solubilization of the silicate layer using the enzyme solution, the soluble silicate contained in the fermentation rice husk can be increased. (Fig. 7)
The effects of silicate fertilizers are often known, but the soluble silicic acid contained in fermented rice husks is derived from the plant rice husks, so there is a problem with safety even if excessive application is performed. There is no.
By absorbing silicic acid quickly and strengthening epidermal cells, crop cultivation, especially fruits and vegetables such as strawberries, tomatoes and cucumbers, fruit trees such as potatoes and grapes, powdery mildew, nematodes and fruit surfaces Damages such as blotches can be reduced. Also, spinach and lettuce were found to increase sugar content. (Figure 2)
(2) Various enzymes, yeasts, and fungi remain in the fermented rice husk and can be fermented and decomposed again by applying moisture.
The heat generated by fermentation evaporates the water content of the rice husk, and when the content falls below 30%, the fermentation slows down and the temperature decreases, and it is generally known that various microorganisms remain dry cells. It is.
For this reason, it can be applied not only to grasses of grasses but also as a treatment for fermentation / decomposition of unused organic resources such as garbage and various sludges by adjusting the water content.
(3) Rice husk is known as an organic resource that is the most difficult to ferment and decompose, and the fermentation and decomposition process of rice husk begins with immersion in an enzyme solution. Fermentation and decomposition can be promoted by doing.
(4) The enzyme solution is oxidized while continuing the soaking of the rice husks to become dark brown and the soluble silicic acid concentration increases. Since this liquid can be used as liquid fertilizer, no harmful emissions are generated.

下水処理施設で処理され、環境基準(図8)を満たして排出される安全な処理水を原料にすることによって、悪臭のない作業環境が可能になるとともに、周辺の環境に悪影響を与えることなく、イネ科植物から植物性ケイ酸を含む有機発酵肥料を短期間で大量に生産することが可能になった。本発明によって大量に発生するもみ殻を焼却などの廃棄処分にする必要がなくなり、加えて畜糞、生ゴミ、竹や樹木のチップ、汚泥などが有効に利用されうるので、環境問題の解消のみならず、農業生産に寄与する効果は極めて大である。  By using safe treated water that is treated at a sewage treatment facility and discharged to meet environmental standards (Figure 8) as a raw material, a work environment without odor is possible and without adversely affecting the surrounding environment. It has become possible to produce a large amount of organic fermented fertilizer containing plant silicic acid in a short period of time from gramineous plants. The present invention eliminates the need to dispose of a large amount of rice husk generated by incineration, etc. In addition, livestock excrement, raw garbage, bamboo and tree chips, sludge, etc. can be used effectively. Therefore, the effect contributing to agricultural production is extremely large.

以下、本発明の意義と方法について詳細に説明する。
本発明において、酵素液とは下水処理施設において活性汚泥処理を経て塩素殺菌され、河川の環境基準(図8)を満たした下水処理水に、セルロース、デンプン、脂質およびタンパク質を分解する酵素と有機物を餌とする酵母や菌類を配合して曝気処理したものであり、汚泥や下水のにおいは殆ど感じない。
塩素殺菌された下水処理水にもみ殻のケイ酸層を分解し脆くする働き(図5,6)があることや塩素殺菌されたものに漬け込んだ有機物が発酵することはこれまで想像し得なかったことである。
Hereinafter, the significance and method of the present invention will be described in detail.
In the present invention, the enzyme solution is an enzyme and an organic substance that decomposes cellulose, starch, lipids, and proteins into sewage treated water that has been chlorinated by activated sludge treatment in a sewage treatment facility and that satisfies the river environmental standards (FIG. 8). It is aerated by mixing yeast and fungi that feed on it, and hardly smells sludge or sewage.
Until now, it has been impossible to imagine that chlorinated sewage treated water has a function to decompose and weaken the silicate layer of rice husks (Figs. 5 and 6) and that fermented organic matter immersed in chlorinated sterilized water. That is.

本発明において処理の対象となる植物と未利用有機資源は、イネ科のセルロースあるいはリグニン等を構成成分としているもみ殻、わら、あるいは竹チップ等と、デンプンや糖質、脂質、タンパク質を蓄積している茎や根、果実、子実、動物の肉や魚など、殆どの有機物が含まれる。
特に、もみ殻は農業用に堆肥化するためには1年以上の歳月を必要とすることはよく知られていることであり、本発明によって短時間で分解し、かつ、臭気の少ない方法が見出されたことは、有機資源の循環と環境に優しい農業育成のためにきわめて重要な意味を持つ。
Plants and unused organic resources to be treated in the present invention accumulate starch, carbohydrates, lipids, and proteins, as well as rice husks, straws, bamboo chips, etc., which are composed of cellulose or lignin of the grass family. Most organic substances such as stalks, roots, fruits, grains, animal meat and fish are included.
In particular, it is well known that rice husk requires more than a year to be composted for agriculture, and is a method that decomposes in a short time and has low odor according to the present invention. The discovery of this is extremely important for organic resource recycling and environmentally friendly agriculture.

本発明の製造方法において使用する酵素はアミラーゼ、セルラーゼ、プロテアーゼ、リパーゼ等という、きわめて一般的な酵素であり、菌類はキノコ菌床由来の木材腐朽菌、酵母菌は米ぬかに由来するものである。
添加量は、もみ殻100に対して酵素・酵母混合物5%、米糠30%である。米糠が不足すると発酵温度の上昇が緩慢となる。
Enzymes used in the production method of the present invention are very general enzymes such as amylase, cellulase, protease, lipase, etc., fungi are wood-rotting fungi derived from mushroom fungi, and yeasts are derived from rice bran.
The addition amount is 5% of enzyme / yeast mixture and 30% of rice bran with respect to rice husk 100. When the rice bran is insufficient, the fermentation temperature rises slowly.

混合撹拌して堆積した後の切り返しは、中心部温度が70℃程度の時に行うと全体に均質な発酵もみ殻を製造することが出来る。また、高さが3mを超えるような大きな堆積を行うと腐敗が生じやすく、悪臭が発生することがあるので、小型の円錐形に堆積することが望ましいが、やむを得ない場合には温度低下に留意しながら空気の導入を行わなければならない。  If the turning after mixing and agitation is performed when the center temperature is about 70 ° C., a fermentation husk that is homogeneous throughout can be produced. In addition, it is desirable to deposit in a small conical shape, because it is easy to cause spoilage and bad odor may be generated if a large deposition exceeding 3 m in height is performed. However, air must be introduced.

また、本発明技術で製造した発酵もみ殻は、畜糞や汚泥、あるいは生ゴミ等に添加することによって、堆肥化や減量化を図ることが出来る。その添加量は、もみ殻100に対して、20〜50%程度が適当である。  Moreover, the fermented rice husk produced by the technology of the present invention can be composted or reduced in weight by adding it to livestock dung, sludge, raw garbage or the like. The addition amount is appropriately about 20 to 50% with respect to rice husk 100.

以上説明したように、本技術は環境に優しい農業を振興させるためにきわめて重要、画期的な技術である。これまで利用困難であったもみ殻や藁、トウモロコシの芯、あるいは竹や有機物等を耕地へ戻すことによって、地域における資源循環システムを支え、有機農業の推進にも寄与することが出来る。
また、生ゴミ等の未利用有機資源の処理にも適用できるので、各地の行政府が苦慮している有機資源(バイオマス)の有効利用や自然再生、環境保護技術等による循環型社会の構築にも寄与できる。(図9)
As explained above, this technology is extremely important and groundbreaking for promoting environmentally friendly agriculture. By returning rice husks, straw, corn cores, bamboo, organic matter, etc., which have been difficult to use, to the arable land, it can support the resource recycling system in the region and contribute to the promotion of organic agriculture.
It can also be applied to the treatment of unused organic resources such as raw garbage, so it can be used for the effective utilization of organic resources (biomass), natural regeneration, environmental protection technologies, etc. Can also contribute. (Fig. 9)

もみ殻の断面図(3図)Cross section of rice husk (Fig. 3) ケイ酸効果の一例An example of silicic acid effect もみ殻の利用Use of rice husk 下水道処理水で処理し、多湿状態で3ヶ月経過後のもみ殻表面組織Rice hull surface texture after 3 months of treatment with sewage treated water 酵素液に24時間浸漬して2週間発酵させたもみ殻表面組織Surface texture of rice husks immersed in enzyme solution for 24 hours and fermented for 2 weeks 堆積時の発酵温度の時系列変化Time series change of fermentation temperature during deposition 無処理もみ殻、処理液散布処理後の発酵もみ殻、および酵素液浸漬処理後の発酵もみ殻におけるケイ酸含有量の相違Difference in silicic acid content between untreated rice husk, fermented rice husk after spraying treatment liquid, and fermented rice husk after enzyme solution immersion treatment 下水処理施設の排出基準例(茨城県土木部ホームページより引用)Example of discharge standards for sewage treatment facilities (quoted from Ibaraki Prefecture Civil Engineering Department website) 有機質資材の資源循環活用(関東農政局バイオマス・ニッポンホームページより引用)Resource recycling of organic materials (quoted from Kanto Agricultural Administration Bureau Biomass Nippon website)

参考資料1.現代農業,第84巻11月号,p94〜103,2005(農文協)
参考資料2.「発酵もみがら」による栽培試験結果,「株式会社アイオム」ホームページより引用
Reference material 1. Modern Agriculture, Vol.84, November, p94-103, 2005 (Agricultural Bunka Kyo)
Reference material2. Cultivation test results from “Fermented Momigara”, quoted from “IOM Co., Ltd.” website

Claims (6)

下水道法に基づいて活性汚泥処理された下水処理水に、アミラーゼ、プロテアーゼ、セルラーゼおよびリパーゼなどの酵素・酵母混合物を添加して前記下水処理水を酵素液化させ、さらに連続曝気して生成する液体状の酵素液の製造方法。  A liquid state produced by adding an enzyme / yeast mixture such as amylase, protease, cellulase and lipase to the sewage treated water treated according to the sewerage law to liquefy the sewage treated water, and further by continuous aeration. A method for producing an enzyme solution. 請求項1に記載の製造方法によって得られた酵素液にもみ殻を浸漬または/および噴霧し、該もみ殻を発酵・分解させて生成するもみ殻の発酵肥料の製造方法。  A method for producing fermented fertilizer for rice husks produced by immersing or / and spraying rice husks in the enzyme solution obtained by the production method according to claim 1 and fermenting and decomposing the rice husks. 請求項2に記載の製造方法によって得られたもみ殻発酵肥料に米糠とアミラーゼ、プロテアーゼ、セルラーゼおよびリパーゼなどの酵素・酵母混合物を添加し、該もみ殻を発酵・分解させて生成するもみ殻の発酵肥料の製造方法。  A rice husk fermented by the production method according to claim 2, wherein rice bran and an enzyme / yeast mixture such as amylase, protease, cellulase and lipase are added, and the rice husk is fermented and decomposed to produce rice husk. A method for producing fertilizer. 竹、乾燥トウモロコシの芯、ふすま等のイネ科の植物を粉砕して粉砕物を形成し、該粉砕物を請求項1に記載の製造方法によって得られた酵素液に浸漬または/および噴霧処理した処理後の粉砕物に米糠とアミラーゼ、プロテアーゼ、セルラーゼおよびリパーゼなどの酵素・酵母混合物を添加し、前記粉砕物を発酵・分解させて生成するイネ科植物から成る粉砕物の発酵肥料の製造方法。  A gramineous plant such as bamboo, dried corn core, bran or the like is pulverized to form a pulverized product, and the pulverized product is immersed or / and sprayed in the enzyme solution obtained by the production method according to claim 1. A method for producing fermented fertilizer of a pulverized product comprising a gramineous plant produced by adding rice bran and an enzyme / yeast mixture such as amylase, protease, cellulase and lipase to the pulverized product after treatment, and fermenting and decomposing the pulverized product. 生ゴミなどの有機廃材または/および家畜糞尿に請求項3に記載の製造方法によって得られたもみ殻発酵肥料を添加して、発酵・分解させて生成する前記生ごみなどの発酵肥料または/および家畜糞尿を発酵肥料にする製造方法。  Fermented fertilizers such as garbage produced by adding fermented rice husk fertilizer obtained by the production method according to claim 3 to organic waste materials such as garbage or / and livestock manure, and / or fermented and decomposed, and / or A method for producing livestock manure as fertilizer. 請求項1ないし請求項5の製造方法により得られた発酵肥料  Fermented fertilizer obtained by the production method of claims 1 to 5
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KR101157821B1 (en) * 2010-06-16 2012-06-22 조승현 liquid fertilizer using rice of the method of manufacturing the same
KR101221530B1 (en) 2010-09-28 2013-01-11 한규흠 Manufacturing method of natural fertilizer using crop and the washing water of rice for plants
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JP2015086089A (en) * 2013-10-29 2015-05-07 俊規 鈴木 Method for producing organic fermentation fertilizer
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Publication number Priority date Publication date Assignee Title
KR101157821B1 (en) * 2010-06-16 2012-06-22 조승현 liquid fertilizer using rice of the method of manufacturing the same
KR101221530B1 (en) 2010-09-28 2013-01-11 한규흠 Manufacturing method of natural fertilizer using crop and the washing water of rice for plants
KR101377626B1 (en) 2012-10-02 2014-03-25 전라남도 Haulm pellet fertilizer and method for manufacturing thereof
CN103483024A (en) * 2013-06-26 2014-01-01 中国农业科学院草原研究所 Method used for preparing organic fertilizer from city domestic sludge
CN103382142A (en) * 2013-07-31 2013-11-06 常熟市常福有机复合肥有限公司 Microorganism fermented organic fertilizer
JP2015086089A (en) * 2013-10-29 2015-05-07 俊規 鈴木 Method for producing organic fermentation fertilizer
CN106746426A (en) * 2017-01-12 2017-05-31 哈尔滨工业大学 A kind of dehydration quantitative reduction method for storing sludge
CN107182845A (en) * 2017-07-11 2017-09-22 段青文 The method for removing medicine and antibiotic residue in Aquatic farming animals body
KR102258068B1 (en) * 2020-08-18 2021-05-28 주식회사 상우바이오푸드 Sludge reduction and the composting method using enzyme
CN112481138A (en) * 2020-12-07 2021-03-12 贵州大学 Preparation method for high-yield polysaccharide based on sweet potato wastewater submerged fermentation
WO2023190667A1 (en) * 2022-03-29 2023-10-05 ケイワート・サイエンス株式会社 Method for producing silicon compound aqueous solution

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