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JP6007446B2 - Method for producing iron fulvic acid containing soluble silica - Google Patents
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JP6007446B2 - Method for producing iron fulvic acid containing soluble silica - Google Patents

Method for producing iron fulvic acid containing soluble silica Download PDF

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JP6007446B2
JP6007446B2 JP2014534392A JP2014534392A JP6007446B2 JP 6007446 B2 JP6007446 B2 JP 6007446B2 JP 2014534392 A JP2014534392 A JP 2014534392A JP 2014534392 A JP2014534392 A JP 2014534392A JP 6007446 B2 JP6007446 B2 JP 6007446B2
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fulvic acid
silica
soluble silica
sludge
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大貴 古賀
大貴 古賀
義明 古賀
義明 古賀
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    • CCHEMISTRY; METALLURGY
    • C05FERTILISERS; MANUFACTURE THEREOF
    • C05FORGANIC FERTILISERS NOT COVERED BY SUBCLASSES C05B, C05C, e.g. FERTILISERS FROM WASTE OR REFUSE
    • C05F11/00Other organic fertilisers
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B09DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
    • B09BDISPOSAL OF SOLID WASTE NOT OTHERWISE PROVIDED FOR
    • B09B3/00Destroying solid waste or transforming solid waste into something useful or harmless
    • B09B3/60Biochemical treatment, e.g. by using enzymes
    • B09B3/65Anaerobic treatment
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B09DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
    • B09BDISPOSAL OF SOLID WASTE NOT OTHERWISE PROVIDED FOR
    • B09B3/00Destroying solid waste or transforming solid waste into something useful or harmless
    • B09B3/70Chemical treatment, e.g. pH adjustment or oxidation
    • CCHEMISTRY; METALLURGY
    • C05FERTILISERS; MANUFACTURE THEREOF
    • C05DINORGANIC FERTILISERS NOT COVERED BY SUBCLASSES C05B, C05C; FERTILISERS PRODUCING CARBON DIOXIDE
    • C05D9/00Other inorganic fertilisers
    • C05D9/02Other inorganic fertilisers containing trace elements
    • 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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  • Treatment Of Sludge (AREA)
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  • Fertilizers (AREA)

Description

本発明は、可溶性シリカを含んだフルボ酸鉄含有物の製造方法に関し、特に、海、河川、干潟、養殖場、池・湖沼などの水域及び土壌又は砂漠へフルボ酸鉄を供給し、藻場の再生と河口や干潟の堆積物の分解による砂地化、養殖場、池、湖沼の水質浄化を改善したり、土壌及び砂漠へ混合使用することで土壌改良及び植物の生育の促進及び砂漠を緑化したりすることが可能な可溶性シリカを含んだフルボ酸鉄含有物の製造方法に関する。 The present invention relates to a method for producing an iron-containing fulvic acid-containing material containing soluble silica, and in particular, supplies iron fulvic acid to water areas such as seas, rivers, tidal flats, farms, ponds and lakes, and soils or deserts. Rehabilitation of sand and landslides by decomposition of sediments in estuaries and tidal flats, water purification of farms, ponds, lakes and marshes is improved, and mixed use with soil and desert promotes soil improvement and plant growth, and desert greening The present invention relates to a method for producing an iron fulvic acid-containing material containing soluble silica.

フルボ酸鉄は自然界では植物の葉や茎の部分が腐植してできた腐植物質中にフルボ酸ができ、これが土中の無酸素状態の中で水に溶けている鉄とキレート作用により、結びついてフルボ酸鉄が生成する(特許文献1、2参照)。このフルボ酸鉄は河川により海へ運ばれ、植物プランクトンや海藻の生育に寄与する。最近ではこのフルボ酸鉄は海の磯焼けを防止し、海底の堆積物を分解し、河川を浄化することが報告されている。 In the natural world, iron fulvic acid forms fulvic acid in the humic substance formed by humming the leaves and stems of the plant, and this is combined with iron dissolved in water in the oxygen-free state of the soil and chelated. Thus, fulvic acid iron is generated (see Patent Documents 1 and 2) . This iron fulvic acid is transported to the sea by rivers and contributes to the growth of phytoplankton and seaweed. Recently, it has been reported that this fulvic acid iron prevents the burning of the sea, decomposes the sediment on the seabed, and purifies the river.

また、魚場ではシリカ欠損、濁水流入、鉄欠損等が水産資源に与える影響も指摘されている(非特許文献1〜4参照)In addition, the effects of silica deficiency, muddy water inflow, iron deficiency, etc. on fishery resources have been pointed out in fish fields (see Non-Patent Documents 1 to 4) .

特開2005−34140号公報JP 2005-34140 A 特許第4710036号公報Japanese Patent No. 4710036

畠山重篤,森は海の恋人Satoshi Hatakeyama, forest is a lover of the sea 福島正巳,有害化学物質の化学形態変化に及ぼす腐植物質の影響 NIRE ニュース 2000年9月Masatsugu Fukushima, Influence of Humic Substances on Changes in Chemical Forms of Hazardous Chemicals NIRE News September 2000 村岡浩爾他,運輸省第三港湾建設局室内実験結果 底質浄化工法検討調査報告書Muraoka Hiroaki et al., Ministry of Transport, 3rd Port Construction Bureau Laboratory Experiment Results Bottom Soil Purification Method Investigation Survey Report 社団法人 海と渚環境美化推進機構,平成22年度 魚場環境・生物多様性保全にかかる植樹活動等森づくり調査報告書Japan Sea and Sea Breeding Environment Beautification Promotion Organization, FY 2010 Survey report on forestation, such as tree planting activities related to fishery environment and biodiversity conservation

自然界においては、フルボ酸と鉄との出会いは偶然性に支配され、また、特許文献1,2の方法では、フルボ酸鉄の生成量も不明で、その生成量をコントロールすることは困難で、フルボ酸鉄含有物質を安定して供給できず、製造コストも高く、シリカ欠損の問題も解決できないという課題がある。   In nature, the encounter between fulvic acid and iron is governed by chance, and in the methods of Patent Documents 1 and 2, the amount of fulvic acid iron is unknown, and it is difficult to control the amount of fulvic acid. There are problems that iron-acid-containing substances cannot be stably supplied, the production cost is high, and the problem of silica deficiency cannot be solved.

また、バチルス菌も水質浄化及び海底の底質浄化にも効果があることがいわれている。しかし、これ単独では効果にバラツキが有り、フルボ酸鉄との併用が必要とされていた。 Bacillus bacteria are also said to be effective for water purification and bottom sediment purification. However, this alone had a variation in effect, and it was necessary to use it together with iron fulvic acid.

そこで、本発明は、可溶性シリカを含んだフルボ酸鉄含有物を安定的に、安価に製造する方法を提供するものである。 Therefore, the present invention provides a method for stably and inexpensively producing an iron fulvic acid-containing material containing soluble silica.

本願請求項1の発明は、製紙スラッジ若しくは竹粉の発酵・殺菌処理によりフルボ酸が生成した発酵処理物又は木屑を使用した汚泥発酵肥料へシリカ鉄からなる液体物質を混合して、熟成することを特徴とする可溶性シリカを含んだフルボ酸鉄含有物の製造方法である。 The invention of claim 1 of the present invention is to mix and mature a liquid substance made of silica iron into a fermented product produced by fulvic acid by fermentation and sterilization of papermaking sludge or bamboo powder or sludge fertilizer using wood chips. Is a method for producing an iron fulvic acid-containing material containing soluble silica.

削除   Delete

本願請求項の発明は、製紙スラッジ若しくは竹粉の発酵・殺菌処理によりフルボ酸が生成した発酵処理物又は木屑を使用した汚泥発酵肥料1kgに対して、シリカ鉄からなる液体物質を50mg〜7000mgの範囲で混合して、熟成することを特徴とする請求項1に記載の可溶性シリカを含んだフルボ酸鉄含有物の製造方法である。 The invention of claim 2 of this application is that 50 mg to 7000 mg of a liquid substance composed of silica iron is used for 1 kg of sludge fertilizer using fermented product or wood waste produced by fulvic acid by fermentation and sterilization treatment of paper sludge or bamboo powder. The method for producing an iron-containing fulvic acid-containing material containing soluble silica according to claim 1, wherein the aging is carried out by mixing within a range of 5%.

本願請求項の発明は、請求項1又は2に記載の可溶性シリカを含んだフルボ酸鉄含有物の製造方法で製造された可溶性シリカを含んだフルボ酸鉄含有物へバチルス菌を混合することを特徴とするバイオ・フルボ酸鉄含有物の製造方法である。 Invention of Claim 3 of this application mixes a Bacillus bacterium to the iron fulvic acid containing material containing the soluble silica manufactured by the manufacturing method of the iron fulvic acid containing material containing the soluble silica of Claim 1 or 2. This is a method for producing a bio-fulvic acid iron-containing material.

本発明では、有機廃棄物を発酵・殺菌処理したものにシリカ鉄から成る液体物質を混合し、熟成処理中に有機廃棄物の発酵・殺菌過程で生成するフルボ酸とシリカ鉄の鉄成分がキレート反応することで、可溶性シリカを含んだフルボ酸鉄含有物を安定的に、安価に製造する。 In the present invention, a liquid substance composed of silica iron is mixed with fermented and sterilized organic waste, and the fulvic acid produced in the fermentation and sterilization process of organic waste during the aging process and the iron component of silica iron are chelated. By reacting, an iron fulvic acid-containing material containing soluble silica is stably and inexpensively produced.

本発明の有機廃棄物の発酵・殺菌処理品とは、コンポスト製造時に木屑又は竹粉を原料にした市販の製品を利用出来、又は、製紙排水処理工程で、シリカ鉄系凝集剤を利用して製造される製紙スラッジをキノコの廃培地を発酵促進剤として混合し、発酵処理したものが有効に利用できる。発酵処理工程で、有害微生物を殺したりあるいは不活性にしたりするには、発酵温度と暴露時間が大切であり、例えば、55℃以上、3日間以上曝すことでコンポストが製造される。   The organic waste fermented and sterilized product of the present invention can be a commercially available product made from wood chips or bamboo powder during compost manufacture, or can be used in a paper wastewater treatment process using a silica iron-based flocculant. It is possible to effectively use a papermaking sludge produced by mixing a mushroom waste medium as a fermentation accelerator and performing a fermentation treatment. In order to kill or inactivate harmful microorganisms in the fermentation process, fermentation temperature and exposure time are important. For example, compost is produced by exposure to 55 ° C. or more for 3 days or more.

シリカ鉄からなる液体物質は市販されている、鉄とシリカを主成分としたシリカ鉄凝集剤(商品名:PSI)を使用することで、可溶性のシリカ及び鉄を供給して容易に水中及び土壌中に、可溶性シリカ及びフルボ酸鉄を溶出し、海、河川の環境改善効果と植物の生育効果に有効に働くことになる。   The liquid substance consisting of silica iron is commercially available. By using a silica iron flocculant (trade name: PSI) based on iron and silica, soluble silica and iron can be easily supplied to the water and soil. Soluble silica and iron fulvic acid are eluted in it, and it works effectively for the environmental improvement effect of the sea and rivers and the growth effect of plants.

有機廃棄物の発酵・殺菌処理品へのシリカ鉄からなる液体物質の添加量は、有機廃棄物の質量(kg)当り、50mg/kgから7000mg/kgの範囲で添加し、最適には500mg/kgから5000mg/kg添加する。   The amount of liquid substance composed of silica iron to fermented and sterilized processed organic waste is 50 mg / kg to 7000 mg / kg per mass (kg) of organic waste, and optimally 500 mg / kg. Add from kg to 5000 mg / kg.

添加量が50mg/kg未満の場合は、可溶性鉄の量が不足し、水質浄化効果が劣る。また、7000mg/kgを超えて添加すると、フルボ酸鉄・シリカ含有物のpH値が低下し、植物への生育にも影響し、コストも高くなる。 When the addition amount is less than 50 mg / kg, the amount of soluble iron is insufficient and the water purification effect is inferior. Moreover, when it adds exceeding 7000 mg / kg, the pH value of a fulvic acid iron and a silica containing material will fall, it will affect the growth to a plant, and cost will also become high.

このフルボ酸鉄・シリカ含有物はフルボ酸と鉄の含有割合は鉄/フルボ酸の成分比率が質量比で1〜5%でフルボ酸がリッチな状態である。そこで、持続性を持たせるために、市販の鉄分を混合してもよい。 In this fulvic acid- silica-containing material, the content ratio of fulvic acid and iron is 1 to 5% by mass of the component ratio of iron / fulvic acid, and fulvic acid is rich. Then, in order to give sustainability, you may mix commercially available iron.

また、バチルス菌を併用する場合、フルボ酸鉄とハイブリットにするバチルス菌は、Bacillus subtilis・Bacillus amyloliquefaciens・Bacillus pumilus・Baciillus licheniformis・Bacillus thuringiensis 等を使用することができ、バチルス菌の有機物分解能力やセルロース分解能力とフルボ酸鉄の光フェントン反応を利用した相乗効果が発揮できる。   In addition, when used in combination with Bacillus, Bacillus hybridized with iron fulvic acid can be used to decompose Bacillus subtilis, Bacillus amyloliquefaciens, Bacillus pumilus, Bacillus licheniformis, Bacillus thulienis, etc. A synergistic effect using the decomposition ability and the photo-Fenton reaction of iron fulvic acid can be exhibited.

フルボ酸鉄の光フェントン反応は、非特許文献2に記載されているように、まずフルボ酸が光反応により、水中の溶存している酸素と光反応し、過酸化水素を生成し、この過酸化水素とフルボ酸鉄中の2価鉄イオンとで光フェントン反応を起こし、ヒドロパーオキシドラジカルが生成する。このヒドロパーオキシドラジカルが強力な酸化作用のために、硫化物等を含む有機化合物を酸化分解する。このために海底の堆積物のヘドロ等が分解し、砂地化して行く。   As described in Non-Patent Document 2, the photo-Fenton reaction of iron fulvic acid is first performed by photoreaction of fulvic acid with oxygen dissolved in water to produce hydrogen peroxide. Photo-Fenton reaction occurs between hydrogen oxide and divalent iron ions in iron fulvicate, and hydroperoxide radicals are generated. This hydroperoxide radical oxidizes and decomposes organic compounds including sulfides and the like because of its strong oxidizing action. For this reason, sludge etc. of sediments on the sea floor decomposes and turn into sand.

この時に、2価鉄イオンは3価鉄イオンになるが、フルボ酸と光エネルギーにより、還元され、2価鉄イオンに戻り、これが水中で繰り返し起こり、硫化物有機化合物を分解して、水質及び底質の浄化をして行く。 At this time, bivalent iron ions becomes the trivalent iron ions, the fulvic acid and light energy, is reduced, back to divalent iron ions, which stiffness Shi caused repeatedly in water, to decompose the sulfide organic compound , Purify water and bottom quality.

本発明によれば、水中に可溶性シリカ及びフルボ酸鉄を良好に供給することで、水質及び海底の底質の浄化や藻場の再生を促進し、水質環境を改善することができる。   ADVANTAGE OF THE INVENTION According to this invention, purification | cleaning of water quality and the bottom sediment of a seabed and regeneration of a seaweed bed can be accelerated | stimulated by supplying soluble silica and fulvic acid iron well in water, and water quality environment can be improved.

また、有機廃棄物の発酵・殺菌処理物を使用することで、土壌へ使用した場合は、フルボ酸鉄、シリカ、窒素、リンを供給でき、植物の生育促進に効果がある。   In addition, when fermented and sterilized organic waste is used, when used for soil, iron fulvic acid, silica, nitrogen, and phosphorus can be supplied, which is effective in promoting the growth of plants.

実施例1におけるヘドロ分解の評価の様子を示す。The state of evaluation of sludge decomposition in Example 1 is shown.

以下、本発明の実施形態について説明する。なお、フルボ酸鉄の分析は株式会社 日本食品機能分析研究所へ依頼して分析した。また、フルボ酸鉄・シリカ含有物からの溶出成分は、株式会社久留米リサーチパークのICP−MS分析装置を使用して分析した。 Hereinafter, embodiments of the present invention will be described. The analysis of iron fulvic acid was carried out by requesting the Japan Food Function Analysis Laboratory. Moreover, the elution component from a fulvic acid iron and a silica containing material was analyzed using the ICP-MS analyzer of Kurume Research Park.

[実施例1]
有限会社土壌微生物研究所で市販されている木屑を使用した汚泥発酵肥料10トンに シリカ鉄からなる液体物質(タイキ薬品工業株式会社製のPSI−025)を5kg噴霧混合し、20日間倉庫で熟成した。
[Example 1]
5 kg of liquid material (PSI-025 manufactured by Taiki Yakuhin Kogyo Co., Ltd.) made of silica iron is spray-mixed with 10 tons of sludge fertilizer using wood chips marketed by Soil Microbiology Research Institute, Inc., and aged in a warehouse for 20 days did.

得られたフルボ酸鉄・シリカ含有物をPETボトルへ入れ、混合物濃度50(g/100ml)の濃度で光の当るところで、常温で20日間放置した後の上澄み液を5Aの濾紙で濾過したものを 株式会社 日本食品機能分析研究所でフルボ酸と可溶性鉄を分析した。また、上澄み液中の可溶性シリカはICP−MS分析装置にて分析した。その結果を表1に示す。この結果、フルボ酸2400(mg/L)、可溶性鉄39(mg/L)、可溶性シリカ105(mg/L)を生成していることが解った。 The obtained fulvic acid-silica-containing material was put into a PET bottle, and the supernatant was filtered through a 5A filter paper after being left at room temperature for 20 days in a place where the mixture was exposed to light at a concentration of 50 (g / 100 ml). Fulvic acid and soluble iron were analyzed at Japan Food Functional Analysis Laboratory. The soluble silica in the supernatant was analyzed with an ICP-MS analyzer. The results are shown in Table 1. As a result, it was found that fulvic acid 2400 (mg / L), soluble iron 39 (mg / L), and soluble silica 105 (mg / L) were produced.

このフルボ酸鉄・シリカ含有物を生分解性袋(ユニチカ製 テラマック土嚢袋)に15kg(フルボ酸鉄・シリカ含有物7.5kg,海砂7.5kg)入れ、伊万里湾の海底堆積物(ヘドロ)がある場所へ設置面積100m2に5m間隔で、5個 設置したところ、3ヶ月後にはヘドロが分解し、低質土の高さが10cmから20cm低下し、砂地化出来ることが解った。具体的には図1に示すように、本件フルボ酸鉄・シリカ含有物設置時はヘドロが厚く、長靴だけでは歩けず、補助箱を使わないと歩行できない状況であったが、設置3ケ月経過後にはヘドロが減少し、砂地化して長靴だけで歩行可能となった。このヘドロの分解の評価は、福岡大学工学部社会デザイン学科が平成24年度3月の土木学会西部支部研究発表会(フルボ酸鉄を用いたヘドロ浄化に関する実証研究〜カブトガニ再生に向けた伊万里湾での取組み〜福岡大学工学部 坂田早、山崎惟義、渡辺亮一、伊豫岡宏樹、三光株式会社 古賀義明)で発表した。ヘドロの分解はフルボ酸鉄による光フェントン反応で分解され、浮泥化し、潮の満ち引きにより、浮泥が流されて、少しずつ標高が低下して行ったものと考えている。 Put 15 kg of this fulvic acid-silica-containing material into a biodegradable bag (Terramac sandbag bag made by Unitika), 7.5 kg of fulvic acid-silica-containing material, and 7.5 kg of sea sand. ) When 5 pieces were installed at an installation area of 100 m2 at intervals of 5 m, the sludge decomposed after 3 months, and the height of the low-quality soil was reduced from 10 cm to 20 cm. Specifically, as shown in Fig. 1, when the fulvic acid-silica-containing material was installed, the sludge was thick, it was impossible to walk with boots alone, and it was impossible to walk without using an auxiliary box, but 3 months have passed since installation Later, the sludge decreased, it became sandy and it became possible to walk with only boots. The evaluation of the decomposition of sludge was conducted by the Department of Social Design, Faculty of Engineering, Fukuoka University, in March 2012. The Western Society of Civil Engineering Research Presentation (Empirical study on sludge purification using iron fulvic acid-in Imari Bay for the recovery of horseshoe crab Efforts ~ Fukuoka University Faculty of Engineering Sayaka Sakata, Yasuyoshi Yamazaki, Ryoichi Watanabe, Hiroki Iokaoka, Sanko Co., Ltd. Yoshiaki Koga) The sludge was decomposed by the optical Fenton reaction with iron fulvic acid, and it was floated, and it was thought that the altitude gradually decreased due to the floating mud being washed away by the tide.

[実施例2]
シリカ鉄からなる液体物質を12.5kg噴霧した以外は、実施例1と同様にして製造した。このフルボ酸鉄・シリカ含有物を固形分濃度20(g/100mL)にした以外は同様にして、上澄み液を作成した。その分析結果を表1に示す。フルボ酸980(mg/L)、可溶性鉄32(mg/L)、可溶性シリカ78(mg/L)であった。このフルボ酸・シリカ鉄含有物を麻袋に10kg入れ、伊万里湾の海底堆積物(ヘドロ)がある場所へ設置したところ、3ヶ月後にはヘドロが分解し、砂地化できることが解った。
[Example 2]
It was produced in the same manner as in Example 1 except that 12.5 kg of a liquid substance composed of silica iron was sprayed. A supernatant was prepared in the same manner except that the iron-silica fulvic acid content was changed to a solid content concentration of 20 (g / 100 mL). The analysis results are shown in Table 1. They were fulvic acid 980 (mg / L), soluble iron 32 (mg / L), and soluble silica 78 (mg / L). When 10 kg of this fulvic acid / silica iron-containing material was put in a hemp sack and installed in a place where Imari Bay's seabed sediment (sludge) was found, it was found that sludge decomposed and became sandy in 3 months.

[実施例3]
シリカ鉄からなる液体物質を25kg使用した以外は 実施例1と同様に製造した。得られたフルボ酸鉄・シリカ含有物は実施例2と同様な濃度で、上澄み液を作成した。その分析結果を表1に示す。フルボ酸990(mg/L)、可溶性鉄45(mg/L)、可溶性シリカ84(mg/L)であった。このフルボ酸鉄含有物を麻袋に10kg入れ、伊万里湾の海底堆積物(ヘドロ)がある場所へ設置したところ、3ヶ月後にはヘドロが分解し、砂地化できることが解った。
[Example 3]
It was produced in the same manner as in Example 1 except that 25 kg of a liquid substance made of silica iron was used. The obtained fulvic acid-silica-containing material was prepared in the same concentration as in Example 2 to prepare a supernatant. The analysis results are shown in Table 1. They were fulvic acid 990 (mg / L), soluble iron 45 (mg / L), and soluble silica 84 (mg / L). When 10 kg of this fulvic acid-containing material was put in a hemp sack and installed in a place where there was an underwater sediment (sludge) in Imari Bay, it was found that the sludge decomposed and became sandy after 3 months.

[実施例4]
竹を粉砕処理した後、常温で20日間熟成した竹粉10kgにシリカ鉄からなる液体物質(タイキ薬品工業製PSI−025)を50g混合(5000ppm)し、ポリ袋に入れ、30日間常温熟成発酵してフルボ酸鉄・シリカ含有物含有物を製造した。得られたフルボ酸鉄・シリカ含有物中のフルボ酸、鉄を日本食品機能分析研究所で測定した結果、フルボ酸59(g/kg),可溶性鉄410(mg/kg)が生成していることが解った。可溶性シリカは得られたフルボ酸鉄・シリカ含有物20gを水道水200mlに16日間、常温で浸漬させ、抽出した液をICP−MS分析装置でシリカ濃度を測定した。その結果、可溶性シリカ濃度は22(mg/L)であった。測定結果を表2に示す。河川水で、アオコが発生した水10Lへ、フルボ酸鉄・シリカを含有したサンプル100gを生分解性の袋へ入れ、流れの中に沈めたら、水の濁度が20から10以下に低下し、アオコの発生も見られなくなった。
[Example 4]
After pulverizing bamboo, liquid material consisting of shea silica iron bamboo powder 10kg it was aged at room temperature for 20 days (Taikiyakuhinkogyo manufactured PSI-025) were 50g mixed (5000 ppm), placed in a plastic bag, cold aged for 30 days Fermentation was carried out to produce a substance containing iron fulvic acid and silica . As a result of measuring fulvic acid and iron in the obtained fulvic acid -silica-containing material at Japan Food Functional Analysis Laboratory, fulvic acid 59 (g / kg) and soluble iron 410 (mg / kg) are produced. I understood that. Soluble silica was obtained by immersing 20 g of the obtained fulvic acid-silica-containing material in 200 ml of tap water for 16 days at room temperature, and measuring the silica concentration of the extracted solution with an ICP- MS analyzer. As a result, the soluble silica concentration was 22 (mg / L). The measurement results are shown in Table 2. 100 g of sample containing fulvic acid iron / silica is put into a biodegradable bag in 10 L of water that is generated by aquatic river water. When submerged in the flow, the turbidity of the water drops from 20 to 10 or less. The occurrence of blue sea bream is no longer seen.

[実施例5]
実施例4と同様に製造したフルボ酸鉄・シリカ含有物に既出3種のバチルス菌(1×10cfu/g)濃度の芽胞菌を均等混合し、1gを添加して、ポリ袋に入れて、30日間常温熟成した。得られたフルボ酸鉄・シリカ含有物の中のフルボ酸、鉄及びシリカ濃度を測定した結果、フルボ酸58(g/kg),可溶性鉄360(mg/kg)が生成していることが解った。また、可溶性シリカは20(mg/L)であった。測定結果を表2に示す。河川水での効果は実施例4と同じであった。
[Example 5]
Three types of Bacillus bacteria (1 × 10 8 cfu / g) spore bacteria previously mixed with the iron-containing fulvic acid / silica-containing material produced in the same manner as in Example 4, 1 g was added, and the mixture was placed in a plastic bag. For 30 days. As a result of measuring the concentration of fulvic acid, iron and silica in the obtained fulvic acid -silica-containing material, it was found that fulvic acid 58 (g / kg) and soluble iron 360 (mg / kg) were produced. It was. Moreover, the soluble silica was 20 (mg / L). The measurement results are shown in Table 2. The effect on river water was the same as in Example 4.

[比較例1]
実施例1で使用した木屑使用発酵汚泥肥料を固形分濃度30(g/100mL)の濃度で上澄み液を作成し、分析した結果を表1に示す。この結果、フルボ酸は510(mg/L)生成していたが、可溶性鉄は1.6(mg/L)と汚泥から持ち込まれたものしか検出出来なかった。このフルボ酸鉄含有物を、麻袋に10kg入れ、伊万里湾の海底堆積物(ヘドロ)がある場所へ設置したが、ヘドロの分解は見られなかった。
[Comparative Example 1]
Table 1 shows the results of analyzing and analyzing the supernatant of the wood sludge fermented sludge fertilizer used in Example 1 at a solid content concentration of 30 (g / 100 mL). As a result, 510 (mg / L) fulvic acid was produced, but only 1.6 (mg / L) soluble iron brought in from sludge could be detected. Although 10 kg of this iron-containing fulvic acid was put in a hemp sack and installed in a place where there was a seabed deposit (sludge) in Imari Bay, the sludge was not decomposed.

[比較例2]
実施例4の竹粉だけを発酵熟成したものを日本食品機能分析研究所で分析した結果、フルボ酸が48(g/kg・dry),可溶性鉄が4(mg/kg・dry)であった。この竹粉だけを発酵処理したものを固形分濃度10(g/100ml)で16日間常温放置し、抽出した上澄み液中の可溶性シリカを分析した結果、23(mg/L)で有った。その結果を表2に示す。
[Comparative Example 2]
As a result of analyzing the fermented and matured bamboo powder of Example 4 at the Japan Food Functional Analysis Laboratory, fulvic acid was 48 (g / kg · dry) and soluble iron was 4 (mg / kg · dry). . The result of fermentation treatment of only this bamboo powder was allowed to stand at room temperature for 16 days at a solid content concentration of 10 (g / 100 ml), and as a result of analyzing the soluble silica in the extracted supernatant, it was 23 (mg / L). The results are shown in Table 2.

Claims (3)

製紙スラッジ若しくは竹粉の発酵・殺菌処理によりフルボ酸が生成した発酵処理物又は木屑を使用した汚泥発酵肥料へシリカ鉄からなる液体物質を混合して、熟成することを特徴とする可溶性シリカを含んだフルボ酸鉄含有物の製造方法。 Contains soluble silica characterized by mixing and aging liquid fermented fertilizer using fermented fermented fertilizer or wood sludge fermented fertilizer produced by fermenting and sterilizing paper sludge or bamboo powder. A method for producing iron-containing fulvic acid. 製紙スラッジ若しくは竹粉の発酵・殺菌処理によりフルボ酸が生成した発酵処理物又は木屑を使用した汚泥発酵肥料1kgに対して、シリカ鉄からなる液体物質を50mg〜7000mgの範囲で混合して、熟成することを特徴とする請求項1に記載の可溶性シリカを含んだフルボ酸鉄含有物の製造方法。 A liquid substance consisting of silica iron is mixed in a range of 50 mg to 7000 mg and aged for 1 kg of fermented fertilizer using sulphated fertilizer produced by fermentation and sterilization of paper sludge or bamboo powder, or wood waste. The manufacturing method of the iron fulvic acid containing material containing the soluble silica of Claim 1 characterized by the above-mentioned. 請求項1又は2に記載の可溶性シリカを含んだフルボ酸鉄含有物の製造方法で製造された可溶性シリカを含んだフルボ酸鉄含有物へバチルス菌を混合することを特徴とする可溶性シリカを含んだフルボ酸鉄含有物の製造方法。 Include soluble silica characterized by mixing bacillus to claim 1 or fulvic iron inclusions containing soluble silica produced by the production method of fulvic iron inclusions containing soluble silica described in 2 A method for producing iron-containing fulvic acid.
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