JP2001089273A - Fertilizer, soil conditioner, wafer quality reforming material and deodorant utilizing carbonized rice bran as well as rust preventive method - Google Patents

Fertilizer, soil conditioner, wafer quality reforming material and deodorant utilizing carbonized rice bran as well as rust preventive method

Info

Publication number
JP2001089273A
JP2001089273A JP30283799A JP30283799A JP2001089273A JP 2001089273 A JP2001089273 A JP 2001089273A JP 30283799 A JP30283799 A JP 30283799A JP 30283799 A JP30283799 A JP 30283799A JP 2001089273 A JP2001089273 A JP 2001089273A
Authority
JP
Japan
Prior art keywords
rice bran
charcoal
fertilizer
water
carbonizing
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Pending
Application number
JP30283799A
Other languages
Japanese (ja)
Inventor
Kazuaki Nishimura
和明 西村
Nagaaki Kataoka
長昭 片岡
Takayuki Maruyama
隆之 丸山
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
AARU DAKKU KK
NICHIBAKU KK
YAMASHO KK
Original Assignee
AARU DAKKU KK
NICHIBAKU KK
YAMASHO KK
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by AARU DAKKU KK, NICHIBAKU KK, YAMASHO KK filed Critical AARU DAKKU KK
Priority to JP30283799A priority Critical patent/JP2001089273A/en
Publication of JP2001089273A publication Critical patent/JP2001089273A/en
Pending legal-status Critical Current

Links

Classifications

    • CCHEMISTRY; METALLURGY
    • C05FERTILISERS; MANUFACTURE THEREOF
    • C05FORGANIC FERTILISERS NOT COVERED BY SUBCLASSES C05B, C05C, e.g. FERTILISERS FROM WASTE OR REFUSE
    • C05F5/00Fertilisers from distillery wastes, molasses, vinasses, sugar plant or similar wastes or residues, e.g. from waste originating from industrial processing of raw material of agricultural origin or derived products thereof
    • 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 effectively utilize rice bran produced in a large amount. SOLUTION: The carbonized product obtained by carbonizing the rice bran or rice bran lees is utilized as a fertilizer, soil conditioner, water quality reforming material, deodorant, etc.

Description

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

【0001】[0001]

【発明の属する技術分野】本発明は、米糠(米糠絞り粕
を含む。)の炭化物を利用する肥料・土壌改良材・水質
改良材・消臭材・防錆方法に関するものである。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a fertilizer, a soil improving material, a water quality improving material, a deodorant, and a rust prevention method using charcoal of rice bran (including rice bran cake).

【0002】[0002]

【従来の技術】炭が透水性・保水性・保肥性・微生物相
改善力・水質浄化力を持つことは周知であり、炭は土壌
改良・水質改良等に使われている。やし殻炭・木炭・竹
炭・もみ殻炭・稲わら炭・バカス炭・おがくず炭を使う
のが一般的である。ただし、炭の効用が認知されている
とはいえ、農業等への普及はまだ十分でない。普及が進
まない理由の一つに環境問題がある。炭化時に出る排ガ
スの無害化処理が大変難しい。また、炭化に経費が掛か
って炭化物が高価になってしまうといった問題点もあ
る。
2. Description of the Related Art It is well known that charcoal has water permeability, water retention, fertilizer retention, microbial flora improvement, and water purification, and charcoal is used for soil improvement, water quality improvement, and the like. It is common to use coconut charcoal, charcoal, bamboo charcoal, rice husk charcoal, rice straw charcoal, bacas charcoal, sawdust charcoal. However, although the utility of charcoal is recognized, its widespread use in agriculture, etc. is not yet sufficient. One of the reasons for the lack of diffusion is environmental problems. It is very difficult to detoxify the exhaust gas generated during carbonization. In addition, there is also a problem that the carbonization is expensive and the carbide is expensive.

【0003】[0003]

【発明が解決しようとする課題】本発明が解決しようと
する課題は、多量に排出する米糠を炭化して利用するこ
とで安価に得ることができる優れた肥料・土壌改良材・
水質改良材・消臭材・防錆方法を提供する点にある。
An object of the present invention is to provide an excellent fertilizer / soil improving material which can be obtained at low cost by carbonizing and using rice bran discharged in large quantities.
An object of the present invention is to provide a water quality improving material, a deodorant, and a rust prevention method.

【0004】[0004]

【課題を解決するための手段】請求項1に係る肥料を植
物に施肥して使用するとき、または水に混ぜて水耕栽培
をするとき、米糠炭化物からリン・カルシウム・カリ・
マグネシウム等のイオンが溶け出し、肥料の作用を発揮
する。請求項2に係る土壌改良材を土壌に混ぜて使用す
るとき、土壌がアルカリ性になって改良される。また、
微生物の代謝活動が活発となって、同じく土壌が改良さ
れる。請求項3に係る水質改良材を使用するとき、汚水
が浄化される。亜硝酸イオン・硝酸イオンも除去され
る。請求項4に係る消臭材を使用するとき、消臭材が臭
いを吸収する。請求項5に係る防錆方法を実施すると
き、機器・装置等に使用する水はアルカリ性であるか
ら、機器・装置等は全く錆びないか又は極めて錆びにく
い。
Means for Solving the Problems When the fertilizer according to claim 1 is used by fertilizing a plant, or when mixed with water for hydroponic cultivation, phosphorus, calcium, potassium, and phosphorus are converted from carbonized rice bran.
Ions such as magnesium dissolve and exert the effect of fertilizer. When the soil improving material according to claim 2 is mixed with soil and used, the soil becomes alkaline and is improved. Also,
The metabolic activity of microorganisms becomes active, and the soil is also improved. When the water quality improving material according to claim 3 is used, sewage is purified. Nitrite and nitrate ions are also removed. When the deodorant according to claim 4 is used, the deodorant absorbs odor. When the rust prevention method according to claim 5 is carried out, the water used for the equipment / apparatus and the like is alkaline, so that the equipment / apparatus and the like are not rusted at all or extremely rust-resistant.

【0005】[0005]

【発明の実施の形態】玄米を精米する段階で米糠は約1
0%も発生する。米糠の用途は主として油用・飼料・食
品加工用であるが、それらの用途に使用される量は限ら
れている。また、米糠は通常環境下で保存すると腐敗す
るため、必要になった時点で必要な量を確保しようとし
ても大変難しい。したがって、燃料としても利用しにく
い。農業においてもボガシ肥を作る場合に米糠が使われ
るが、極めて少ない量に過ぎない。また、米糠は15〜
20%の油脂を含み、分解が遅い。無機化率が50%に
達するに要する日数も長くなり、米糠自体が肥料として
使われることは少ない。米糠が実際に利用される量は以
上のように大したものでなく、多くは産業廃棄物として
処分されている。
DETAILED DESCRIPTION OF THE INVENTION At the stage of browning rice, rice bran is reduced to about 1
0% also occurs. The use of rice bran is mainly for oil, feed and food processing, but the amount used for those uses is limited. In addition, rice bran is spoiled when stored in a normal environment, so it is very difficult to secure the required amount when it is needed. Therefore, it is difficult to use it as fuel. Rice bran is also used in agriculture to make bogashi manure, but only in very small quantities. In addition, rice bran is 15 ~
It contains 20% fats and oils and decomposes slowly. The number of days required for the mineralization rate to reach 50% becomes longer, and rice bran itself is rarely used as fertilizer. The amount of rice bran that is actually used is not so significant, and many are disposed of as industrial waste.

【0006】本発明の発明者は、処分に困っている米糠
を有効に活用できないかと鋭意検討を重ねた。米糠や米
糠の絞り粕を炭化物にすることを思い付き、その炭化物
の活用面について研究した。そして、従来のもみ殻・稲
わら等の炭化物には無い性能を有することを発見した。
米糠・米糠絞り粕の炭化物は安価に製造できる点も確認
し、本発明を完成することができた。
[0006] The inventor of the present invention has intensively studied whether rice bran, which is difficult to dispose of, can be effectively used. We came up with the idea of converting rice bran and rice bran cake into charcoal, and studied the application of charcoal. And they discovered that they had performance not found in conventional charcoal such as rice hulls and rice straw.
It was also confirmed that the charcoal of rice bran and rice bran cake could be produced at low cost, and the present invention was completed.

【0007】まず、本出願の出願人が試みた米糠炭化方
法の1例を紹介する。取扱いをし易くするため及び炭化
効率を上げるため、米糠をあらかじめ造粒する。造粒機
にて50kgf/cmで加圧成型し、直径8mm×長
さ10〜15mmの円柱状に造粒した。造粒したもの
を、図1・2・3に示す炭化装置で炭化した。その炭化
装置を図1・2・3に基づいて説明する。
First, an example of a method of carbonizing rice bran attempted by the applicant of the present application will be introduced. Rice bran is granulated in advance to facilitate handling and increase carbonization efficiency. It was press-molded with a granulator at 50 kgf / cm 2 and granulated into a column having a diameter of 8 mm and a length of 10 to 15 mm. The granulated product was carbonized by a carbonization device shown in FIGS. The carbonization device will be described with reference to FIGS.

【0008】図1は炭化装置の全体を示す正面図、図2
は炭化装置のうち炭化炉を示す縦断面図、図3は図2の
A−A断面図である。1は炭化炉の炉体を示している。
炉体1には、ほぼ水平に貫いて内筒2を配置している。
内筒2は、左側から右側へ行くに従い少しずつ低くなる
ようにやや傾けている。炉体1の両端壁と内筒2との間
にシール材3を取り付けている。内筒2には内部中央か
ら外方へと直角に折れ曲がる排ガス管4の幾つかを、9
0度ずつ位置をずらせながら等間隔で設けている。炉体
1の外部にある部分において内筒2の左端付近及び右端
付近の外周にギヤ5をそれぞれ取り付けている。ギヤ5
は駆動モータ6で回転させる。炉体1の外壁には温度測
定用の熱電対7を幾つか取り付けている。また、炉体1
内の下部にはバーナ8を等間隔で幾つか設けている。炉
体1の下方には炉体1内の右端に通じる排煙路9を設
け、排煙路9内に二次燃焼バーナ10を設けている。
FIG. 1 is a front view showing the entire carbonizing apparatus, and FIG.
3 is a longitudinal sectional view showing a carbonizing furnace in the carbonizing apparatus, and FIG. 3 is a sectional view taken along line AA of FIG. Reference numeral 1 denotes a furnace body of a carbonization furnace.
The inner cylinder 2 is disposed in the furnace body 1 so as to extend substantially horizontally.
The inner cylinder 2 is slightly inclined so as to gradually decrease as going from the left side to the right side. A sealing material 3 is attached between both end walls of the furnace body 1 and the inner cylinder 2. In the inner cylinder 2, some of the exhaust gas pipes 4, which are bent at right angles from the inner center to the outer side, are provided with 9.
It is provided at equal intervals while shifting the position by 0 degrees. Gears 5 are attached to the outer periphery near the left end and near the right end of the inner cylinder 2 in a portion outside the furnace body 1, respectively. Gear 5
Is rotated by the drive motor 6. Several thermocouples 7 for temperature measurement are attached to the outer wall of the furnace body 1. Furnace body 1
Several burners 8 are provided at equal intervals in the lower part inside. Below the furnace body 1, a flue gas passage 9 communicating with the right end in the furnace body 1 is provided, and a secondary combustion burner 10 is provided in the flue gas passage 9.

【0009】内筒2の左側から内筒2内へとフィーダ1
1を挿入している。フィーダ11内にスクリュー12を
設け、外部に取り付けたギヤ13を駆動モータで回転さ
せてスクリュー12を回転させるようにしている。フィ
ーダ11にはホッパー14の下端を取り付けている。ホ
ッパー14の上方に原料ホッパー15を設けている。内
筒2内の右端から下方へと炭化物排出管16を取り付け
ている。内筒2の右側から内筒2内へと高温ガス管17
を挿入している。高温ガス管17はブロワ18を介して
燃焼装置19へ連結している。
The feeder 1 is inserted into the inner cylinder 2 from the left side of the inner cylinder 2.
1 is inserted. A screw 12 is provided in the feeder 11, and a screw 13 is rotated by rotating a gear 13 attached to the outside with a drive motor. The lower end of the hopper 14 is attached to the feeder 11. A raw material hopper 15 is provided above the hopper 14. A carbide discharge pipe 16 is attached downward from the right end in the inner cylinder 2. From the right side of the inner cylinder 2, the hot gas pipe 17
Is inserted. The hot gas pipe 17 is connected to a combustion device 19 via a blower 18.

【0010】内筒2は例えば3rpm程度の低速で回転
させる。燃焼装置19で発生させた高温ガス(850〜
910度)をブロワ18によって高温ガス管17から内
筒2内へ送り込む。米糠造粒物は原料ホッパー15から
ホッパー14へ落とし、スクリュー12によって内筒2
内へ連続的に供給する。スクリュー12の回転数を3.
22rpmとしたとき、造粒物供給量は50kg/hと
なる。スクリュー12の回転数を1.94rpmとした
ときは造粒物供給量は15kg/hとなる。
The inner cylinder 2 is rotated at a low speed of, for example, about 3 rpm. High-temperature gas (850 to 850) generated in the combustion device 19
910 °) is sent from the high-temperature gas pipe 17 into the inner cylinder 2 by the blower 18. The rice bran granules are dropped from the raw material hopper 15 to the hopper 14,
Supply continuously into the inside. 2. The number of rotations of the screw 12
When the rotation speed is 22 rpm, the supply amount of the granulated material is 50 kg / h. When the rotation speed of the screw 12 is 1.94 rpm, the supply amount of the granulated material is 15 kg / h.

【0011】高温ガス管17から内筒2内に流入した高
温ガスは、フィーダ11から供給される造粒物を次第に
炭化させていく。造粒物が内筒2内に滞留する炭化時間
は10〜12分である。炭化温度は300〜800度で
ある。800度を越えると炭化物自体が軟化し、炉壁に
付着して炭化物収率が低下したり炉内からの排出が困難
になったりする。もちろんこの現象は炉内滞留時間によ
って異なる。
The high-temperature gas flowing from the high-temperature gas pipe 17 into the inner cylinder 2 gradually carbonizes the granules supplied from the feeder 11. The carbonization time during which the granules stay in the inner cylinder 2 is 10 to 12 minutes. The carbonization temperature is 300-800 degrees. If the temperature exceeds 800 ° C., the carbide itself softens and adheres to the furnace wall to lower the carbide yield or make it difficult to discharge from the furnace. Of course, this phenomenon depends on the residence time in the furnace.

【0012】炭化中に乾留ガスが発生するが、乾留ガス
は排ガス管4から外へ出て、炉体1内でバーナ8によっ
て着火し燃える。そして、排煙路9から排出していくと
き、乾留ガス中の未燃焼物は二次燃焼バーナ10によっ
て燃焼し、奇麗になった排ガスが外部へ出ていく。炭化
した造粒物は炭化物排出管16から排出される。
A carbonization gas is generated during carbonization. The carbonization gas goes out of the exhaust gas pipe 4 and is ignited by the burner 8 in the furnace body 1 and burns. When exhausted from the flue gas passage 9, unburned substances in the carbonized gas are burned by the secondary combustion burner 10, and the clean exhaust gas goes out. The carbonized granules are discharged from the carbide discharge pipe 16.

【0013】生の米糠は油脂を多量に含んで可燃ガスを
大量に発生するため、点火時から初期段階だけを除い
て、消費する燃料はほとんど必要としない。この可燃ガ
スをメタンガスと仮定すると、米糠処理量50kg/h
で約47Nm/h、15kg/hで約14Nmの乾
留ガスが発生し、自燃する。外部から供給する燃料は
1.5kg/h以下で済む。この点は米糠を炭化する場
合の大きな特徴である。
Since raw rice bran contains a large amount of fats and oils and generates a large amount of combustible gas, little fuel is consumed except for the initial stage from the time of ignition. Assuming that this combustible gas is methane gas, the rice bran processing rate is 50 kg / h.
At about 47 Nm 3 / h and at 15 kg / h about 14 Nm 3 of carbonized gas and self-burn. The fuel supplied from outside can be 1.5 kg / h or less. This is a major feature when carbonizing rice bran.

【0014】このやり方を更に前進させると、米糠を併
用し、可燃ガス発生量の少ないいろいろな有機物を炭化
することができる。例えば農業で排出するもみ殻・枯れ
草・稲わら・サトウキビの絞り粕・農業用フィルム等を
米糠と共に炭化することで燃料を少なくし、環境汚染も
避けることができる。このとき、用途によって市販の微
生物資材を混ぜたり、ゼオライト・蛎殻等の一般に使用
される無機質資材を混ぜたりしてもよい。炭化工程で発
生する排熱は冷暖房等に有効活用してもよい。
If this method is further advanced, rice bran can be used in combination to carbonize various organic substances that generate a small amount of combustible gas. For example, carbonization of rice husks, hay, rice straw, sugarcane pulp, agricultural film, and the like discharged from agriculture together with rice bran can reduce fuel consumption and avoid environmental pollution. At this time, a commercially available microbial material or a commonly used inorganic material such as zeolite or oyster hull may be mixed depending on the use. The exhaust heat generated in the carbonization step may be effectively used for cooling and heating.

【0015】このようにして製造した米糠炭化物の性状
は次のとおりである。 嵩比重:0.26〜0.28 可燃分:49〜58% 灰 分:41〜50% 炭化物の成分:炭素・カリ・リン・カルシウム・マグネ
シウム・シリカ 水分吸着能:300%以上(炭化物を水中に入れて取り
出した後の重さ) PH:7.3〜8.5(水に5〜15重量%の炭化物を
浸漬したとき) 気孔の大きさ:SEM写真からミクロ孔〜マクロ孔の存
在が観察できる。
The properties of the rice bran charcoal thus produced are as follows. Bulk specific gravity: 0.26 to 0.28 Combustible content: 49 to 58% Ash content: 41 to 50% Carbide component: carbon, potassium, phosphorus, calcium, magnesium, silica Water adsorption capacity: 300% or more (carbonized water PH: 7.3 to 8.5 (when 5 to 15% by weight of a carbide is immersed in water) Pore size: Micropores to macropores are found from the SEM photograph. Observable.

【0016】まず、製造した米糠炭化物の肥料としての
利用面に関する次の試験をした。米糠炭化物・備長炭・
竹炭・やし殻活性炭・もみ殻炭を用意し、それらを各別
の水に5%ずつ添加したものを用意した。それらを使
い、ガーデンクレソン・貝割れ大根・ミニトマトの種を
まいて室内で水耕栽培をした。この結果、いずれの栽培
においても米糠炭化物を浸漬した水を使った栽培で成育
が最も早く、根や茎の太さも最も大きくなった。また、
水が無くなってから枯れるまでの時間も、米糠炭化物添
加水で栽培したものが他のものより10〜20日も長か
った。米糠炭化物を水に入れるとリン・カルシウム・カ
リ・マグネシウム等のイオンが溶け出す。このことは米
糠炭化物が肥料になることを示唆している。米糠炭化物
を加えれば他の肥料の量を少なくすることもできる。
First, the following test was conducted on the utilization of the produced rice bran carbide as a fertilizer. Rice bran charcoal, Bincho charcoal,
Bamboo charcoal, coconut shell activated charcoal, and rice husk charcoal were prepared, and those obtained by adding 5% of each to water were prepared. Using these, garden watercress, cracked radish and mini tomato were sown and hydroponically cultivated indoors. As a result, in any of the cultivations, the cultivation using water impregnated with charcoal of rice bran was the fastest growing, and the roots and stems were also the thickest. Also,
The time from the disappearance of water to the death of the rice bran was 10 to 20 days longer when cultivated with the rice bran-carburized water than with the others. Ions such as phosphorus, calcium, potassium, and magnesium are dissolved when the rice bran carbide is put into water. This suggests that charcoal of rice bran becomes a fertilizer. The addition of charcoal rice bran can reduce the amount of other fertilizers.

【0017】つぎに、米糠炭化物の土壌改良作用につい
て説明する。前記のとおり、米糠炭化物はアルカリ性で
ある。土壌に混ぜると、土壌がアルカリに傾いて改良さ
れる。また、土壌中の微生物が活発に代謝活動をすると
土壌が改良されるが、米糠炭化物は微生物の代謝活動を
促進する機能を有する。この機能の点を説明する。
Next, the soil improving effect of the rice bran carbide will be described. As mentioned above, the rice bran carbide is alkaline. When mixed with soil, the soil tends to be alkaline and improved. In addition, soil is improved when microorganisms in the soil actively metabolize, but charcoal of rice bran has a function of promoting the metabolic activity of microorganisms. The point of this function will be described.

【0018】次の試験をした。まず、米糠炭化物のほか
に市販の活性炭・備長炭・竹炭を超純水にそれぞれ6重
量%ずつ添加したものを96時間常温で静置した後に蔗
糖を20%ずつ溶解した蔗糖水溶液試料を用意した。別
に超純水に20%の蔗糖を溶解した蔗糖水溶液試料も用
意し、全部で5種類の蔗糖水溶液試料とした。それらの
30ミリリットルずつに5000ミリグラムずつのイー
スト菌系を混ぜた。そして、27度で90分保管する間
の累計ガス発生量の経時変化を調べたら、図4のように
なった。ガスは微生物の代謝活動によって発生する炭酸
ガスである。米糠炭化物を添加したものは、備長炭・竹
炭を添加したものや超純水だけのものよりガス発生時点
が10分以上も早い。90分後の累計ガス発生量も他の
ものよりかなり多い。米糠炭化物が微生物の代謝活動を
促進することを示唆している。
The following tests were performed. First, in addition to charcoal rice bran, commercially available activated carbon, bincho charcoal, and bamboo charcoal were added to ultrapure water at 6% by weight each, and the mixture was allowed to stand at room temperature for 96 hours. . Separately, a sucrose aqueous solution sample in which 20% sucrose was dissolved in ultrapure water was also prepared, and five kinds of sucrose aqueous solution samples were used in total. Each 30 milliliters was mixed with 5000 milligrams of yeast strain. FIG. 4 shows the change with time in the cumulative gas generation during storage at 27 degrees for 90 minutes. Gas is carbon dioxide gas generated by metabolic activity of microorganisms. In the case of adding rice bran charcoal, the gas generation time is earlier than that of the case of adding bincho charcoal / bamboo charcoal or ultrapure water only by 10 minutes or more. The cumulative gas generation after 90 minutes is also significantly higher than the others. It suggests that charcoal of rice bran promotes the metabolic activity of microorganisms.

【0019】つぎに、次の試験をした。米糠炭化物を体
積比でそれぞれ10%・30%・50%添加してよく混
合した土と庭の土とをガラス製広口瓶にそれぞれ入れ、
紙片と木綿生地片もそれぞれ混入して室内に放置した。
観察結果を表1に示す。米糠炭化物がセルロース分解菌
の活性を高めるものと考えられる。
Next, the following test was conducted. The rice bran charcoal is added in a volume ratio of 10%, 30% and 50%, respectively, and the well-mixed soil and garden soil are placed in glass jars, respectively.
A piece of paper and a piece of cotton fabric were also mixed and left indoors.
Table 1 shows the observation results. It is considered that charred rice bran enhances the activity of cellulolytic bacteria.

【0020】[0020]

【表1】 [Table 1]

【0021】つぎに、米糠炭化物による水質改良の点を
説明する。まず、汚水に米糠炭化物を添加処理した場合
にCODがどのように変化するかを見てみた。結果は図
5の上図に示すとおりとなった。すなわち、米糠炭化物
で処理しない場合は10日間でCODはほとんど減らな
いのに対し、米糠炭化物で処理した場合は7日間で大き
く減っている。また、NH ・NO ・PO 3−
についても経時変化を測定して見たら、図5の下図に示
すとおりとなった。米糠炭化物を添加しない場合はNH
・PO 3−はゆっくり減少していくのに対し、米
糠炭化物を添加した場合はそれらのイオンは急激に減少
していく。汚水に米糠炭化物を投入するとリン酸イオン
(PO 3−)がリン酸カルシウム等に変化して凝集沈
澱し、リン酸イオンが除去される。
Next, the point of improvement of water quality by charcoal of rice bran will be described. First, it was examined how COD changes when charcoal of rice bran is added to sewage. The result was as shown in the upper diagram of FIG. That is, when not treated with charcoal rice bran, COD is hardly reduced in 10 days, whereas when treated with charcoal rice bran, it is greatly reduced in 7 days. Moreover, NH 4 + · NO 2 - · PO 4 3-
As for, the change over time was measured, and the results were as shown in the lower diagram of FIG. If rice bran char is not added, NH
While 4 + .PO 4 3- decreases slowly, when carbonized rice bran is added, those ions rapidly decrease. When turning on the rice bran carbide sewage phosphate ions (PO 4 3-) are agglomerated precipitated changed to calcium phosphate, phosphoric acid ions are removed.

【0022】肥料を過剰投与した場合、硝酸性窒素から
出る亜硝酸イオン・硝酸イオンのうち農作物に吸収され
ない分が地中に浸透する。それを人間が取り込むと健康
障害を引き起こすのではないかと懸念されている。特に
亜硝酸イオンを含む水を飲むと、ひどい場合には酸素を
運ぶヘモグロビンが亜硝酸イオンの作用によって酸素を
運ばなくなる。呼吸をしているのに酸素不足で窒息する
という状況に陥る可能性があると言われている。そこ
で、米糠炭化物が硝酸性窒素を除去する能力について試
験をしてみた。土壌500gに米糠炭化物を5%又は1
5%添加して混合し、45mg/リットルの硝酸イオン
を含む汚水1リットル及び1mg/リットルの亜硝酸イ
オンを含む汚水1リットルにそれぞれ投入した。そし
て、硝酸イオン・亜硝酸イオンの濃度の経時変化を見る
ことで除去能力を評価した。結果を表2に示す。
When the fertilizer is over-administered, nitrite ions and nitrate ions from nitrate nitrogen that are not absorbed by the crops penetrate into the ground. It has been feared that humans could cause health problems if taken in. In particular, when drinking water containing nitrite ions, in severe cases, hemoglobin carrying oxygen stops carrying oxygen due to the action of nitrite ions. It is said that you may fall into a situation of suffocation due to lack of oxygen while breathing. Therefore, a test was conducted on the ability of charcoal rice bran to remove nitrate nitrogen. 5% or 1 char of rice bran in 500g of soil
5% was added and mixed, and the mixture was added to 1 liter of wastewater containing 45 mg / liter nitrate ions and 1 liter of wastewater containing 1 mg / liter nitrite ions. Then, the removal ability was evaluated by observing the change over time in the concentrations of nitrate ion and nitrite ion. Table 2 shows the results.

【0023】[0023]

【表2】 [Table 2]

【0024】なお、米糠炭化物を添加した場合、更に黒
糖1〜5%水溶液やアルコール1ミリリットル(0.1
%)を添加すると、硝酸イオン・亜硝酸イオンとも10
日後にはゼロになった。以上から、米糠炭化物が硝酸性
窒素の除去効果を有することが明らかである。黒糖水溶
液やアルコールを併用すると、更に効果的である。
When charcoal rice bran is added, a 1-5% aqueous solution of brown sugar or 1 ml of alcohol (0.1 ml) is added.
%), 10% for both nitrate and nitrite ions
It became zero after a day. From the above, it is clear that the rice bran carbide has a nitrate nitrogen removing effect. It is more effective to use an aqueous solution of brown sugar or alcohol in combination.

【0025】つぎに、消臭能力に関する試験をした。ま
ず、硫化水素水に空気を吹き込んで発生した硫化水素ガ
スを1リットルのフラスコで捕集し、検知管式気体測定
器(ガステック製GV−100S)で硫化水素ガス濃度
を直ちに測定した。そして、直後に同じフラスコに米糠
炭化物粉末(10〜20μ網粒)10gを投入したもの
及び投入しないままのものの2種類について30分後に
硫化水素ガス濃度を再び測定した。アンモニアについて
も同様の試験をした。すなわち、アンモニア水に送気し
て発生したアンモニアをフラスコで捕集し、濃度を測定
した。そして、米糠炭化物を直後に投入したもの及び投
入しないままのものについて30分後に再び測定した。
結果は表3のとおりである。検知管としては、硫化水素
の場合はガステック製No.4Mを使用し、アンモニア
の場合はNo.3Lを使用した。
Next, a test regarding the deodorizing ability was conducted. First, hydrogen sulfide gas generated by blowing air into hydrogen sulfide water was collected in a 1-liter flask, and the concentration of the hydrogen sulfide gas was immediately measured with a detection tube type gas meter (GV-100S manufactured by Gastech). Then, immediately after 30 minutes, the hydrogen sulfide gas concentration was measured again for two types, one in which 10 g of rice bran carbide powder (10 to 20 μ mesh) was charged and the other without charging, in the same flask. A similar test was performed for ammonia. That is, ammonia generated by feeding into ammonia water was collected in a flask, and the concentration was measured. Then, 30 minutes later, the measurement was again performed for the rice bran charcoal which had been charged immediately and the rice bran charcoal which had not been charged.
Table 3 shows the results. As a detection tube, in the case of hydrogen sulfide, No. No. 4M was used. 3L was used.

【0026】[0026]

【表3】 [Table 3]

【0027】米糠炭化物は腐らないので長期保存が可能
で、保管条件の制約もない。つまり米糠を炭化すること
で米糠が持っている分解の遅さ・保存性の悪さという欠
点を無くすことができる。しかも、米糠炭化物を保存し
ている場所の悪臭も吸着し空気も浄化する。米糠炭化物
は家畜舎の消臭にも積極的に利用することもできる。
Since the rice bran charcoal does not rot, it can be stored for a long time, and there are no restrictions on storage conditions. In other words, carbonizing rice bran can eliminate the disadvantages of rice bran such as slow decomposition and poor storage stability. In addition, it absorbs the bad odor of the place where the rice bran is stored and purifies the air. Rice bran charcoal can also be actively used for deodorizing livestock barns.

【0028】つぎに、米糠炭化物が防錆作用を発揮する
点に着目した。米糠炭化物を1%以上添加した水のPH
は7.3〜8.5である。硬度は50〜100で、水道
水と変わらない。弱アルカリであるが、米糠炭化物に含
まれるリン酸イオンとカルシウムイオンの作用による。
このため、防錆作用を発揮し、中に鉄を浸しても錆びる
ことがない。水中に米糠炭化物を投入すると白い浮遊物
(ハイドロオキシアパタイトと推定される。)が溶出し
てくるが、不織布・濾紙で除去できる。除去した水の中
でも鉄は錆びない。以上のように、米糠炭化物は防錆機
能を有するから、例えばボイラー等の熱交換機器の水循
環経路に、米糠炭化物を入れたタンクやカートリッジを
設置し、防錆システムとすることができる。
Next, attention was paid to the point that the rice bran carbide exerts a rust-preventive action. PH of water to which 1% or more of rice bran carbide is added
Is 7.3 to 8.5. Hardness is 50-100, which is the same as tap water. Although weakly alkaline, it is due to the action of phosphate ions and calcium ions contained in the rice bran carbide.
For this reason, it exhibits a rust-preventive effect and does not rust even if iron is immersed therein. When the rice bran carbide is put into water, white suspended matter (estimated as hydroxyapatite) elutes, but can be removed with a nonwoven fabric / filter paper. Iron does not rust in the water removed. As described above, since the rice bran carbide has a rust prevention function, for example, a tank or a cartridge containing the rice bran can be installed in a water circulation path of a heat exchange device such as a boiler to provide a rust prevention system.

【0029】以上のように、米糠炭化物は肥料・土壌改
良材・水質改良材・消臭材として利用でき、防錆作用も
発揮する。この米糠炭化物は、実際には次のような使い
方をする。黒糖溶液・木節・粘土等の粘結材で固めた成
型体にして使用してもよい。 ○米糠炭化物を農業用水路に浸漬する。 ○米糠炭化物を土壌に混ぜる。 ○土壌表面下50cm以下に米糠炭化物層を作る。 ○米糠炭化物を水田にまく。 ○水田・畑の周りに米糠炭化物の囲い・土手を作る。 ○家畜舎にまいたり充填物を置いたりする。
As described above, the rice bran carbide can be used as a fertilizer, a soil improving material, a water quality improving material, and a deodorant, and also exhibits a rust-preventive effect. This rice bran carbide is actually used as follows. It may be used as a molded product hardened with a binder such as brown sugar solution, kibushi, and clay. ○ Soak rice bran in agricultural irrigation canals. ○ Mix rice bran carbide into soil. ○ Make a rice bran carbide layer below 50 cm below the soil surface. ○ Sprinkle rice bran on rice fields. ○ Make rice bran fences and banks around paddy fields and fields. ○ Sowing in the livestock barn or filling.

【0030】[0030]

【発明の効果】本発明に係る肥料・土壌改良材・水質改
良材・消臭材・防錆方法は、安価に得られる米糠炭化物
を利用したものであり、極めて有効なものである。
The fertilizer, soil improver, water quality improver, deodorant, and rust preventive method according to the present invention utilize charcoal of rice bran obtained at a low cost and are extremely effective.

【図面の簡単な説明】[Brief description of the drawings]

【図1】炭化装置を示す正面図である。FIG. 1 is a front view showing a carbonizing device.

【図2】炭化装置の要部を示す縦断面図である。FIG. 2 is a longitudinal sectional view showing a main part of the carbonizing device.

【図3】図2のA−A断面図である。FIG. 3 is a sectional view taken along line AA of FIG. 2;

【図4】各種炭を用いた微生物代謝活動促進に関する試
験の結果を示す図である。
FIG. 4 is a view showing the results of a test on promoting microbial metabolic activity using various types of charcoal.

【図5】米糠炭化物を用いた場合及び用いない場合の汚
水浄化試験の結果を示す図である。
FIG. 5 is a view showing the results of a sewage purification test when charcoal rice bran is used and when it is not used.

【符号の説明】[Explanation of symbols]

1 炉体 2 内筒 11 フィーダ 16 炭化物排出管 17 高温ガス管 DESCRIPTION OF SYMBOLS 1 Furnace body 2 Inner cylinder 11 Feeder 16 Carbide discharge pipe 17 Hot gas pipe

───────────────────────────────────────────────────── フロントページの続き (72)発明者 西村 和明 埼玉県久喜市中央3丁目2番18号 株式会 社アール・ダック内 (72)発明者 片岡 長昭 東京都墨田区緑4丁目25番2号 株式会社 ニチバク内 (72)発明者 丸山 隆之 東京都台東区東上野4丁目6番7号 株式 会社山商内 Fターム(参考) 4B023 LE08 4D004 AA04 BA02 BA03 BA04 CA14 CA26 CB04 DA02 DA06 4G046 CA00 CB08 HA01 HB02 4G066 AA04B AC39A CA02 CA28 CA41 CA43 DA03 DA07 FA18 FA23 4H061 AA01 CC42 KK08  ──────────────────────────────────────────────────続 き Continuing on the front page (72) Inventor Kazuaki Nishimura 3-2-1-18 Chuo, Kuki-shi, Saitama R-Duck Co., Ltd. (72) Inventor Nagaaki Kataoka 4-25 Midori, Sumida-ku, Tokyo No. 2 Nichibaku Corporation (72) Inventor Takayuki Maruyama 4-6-7 Higashi-Ueno, Taito-ku, Tokyo F-term (reference) 4B023 LE08 4D004 AA04 BA02 BA03 BA04 CA14 CA26 CB04 DA02 DA06 4G046 CA00 CB08 HA01 HB02 4G066 AA04B AC39A CA02 CA28 CA41 CA43 DA03 DA07 FA18 FA23 4H061 AA01 CC42 KK08

Claims (5)

【特許請求の範囲】[Claims] 【請求項1】 米糠又は米糠絞り粕を炭化して得られた
米糠炭化物からなる肥料。
1. A fertilizer comprising charcoalized rice bran obtained by carbonizing rice bran or rice bran cake.
【請求項2】 米糠又は米糠絞り粕を炭化して得られた
米糠炭化物からなる土壌改良材。
2. A soil improver comprising charcoalized rice bran obtained by carbonizing rice bran or rice bran cake.
【請求項3】 米糠又は米糠絞り粕を炭化して得られた
米糠炭化物からなる水質改良材。
3. A water quality improving material comprising a rice bran char obtained by carbonizing rice bran or rice bran cake.
【請求項4】 米糠又は米糠絞り粕を炭化して得られた
米糠炭化物からなる消臭材。
4. A deodorant comprising charcoalized rice bran obtained by carbonizing rice bran or rice bran cake.
【請求項5】 米糠又は米糠絞り粕を炭化して得られた
米糠炭化物で処理して得られたアルカリ水を、防錆を必
要とする機器・装置等に使用することを特徴とする防錆
方法。
5. Rust prevention characterized in that alkaline water obtained by treating rice bran or rice bran char obtained by carbonizing rice bran cake is used for equipment and devices that require rust prevention. Method.
JP30283799A 1999-09-17 1999-09-17 Fertilizer, soil conditioner, wafer quality reforming material and deodorant utilizing carbonized rice bran as well as rust preventive method Pending JP2001089273A (en)

Priority Applications (1)

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Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
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Publication Number Publication Date
JP2001089273A true JP2001089273A (en) 2001-04-03

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ID=17913703

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Country Link
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Cited By (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US6887288B2 (en) 2002-06-05 2005-05-03 Minebea Co., Ltd. Superfinishing grindstone
US7140778B2 (en) 2002-03-01 2006-11-28 Minebea Co., Ltd. Synthetic resin composites and bearings formed therefrom and method
US7160622B2 (en) 2003-01-07 2007-01-09 Minebea Co., Ltd. Oil repelling agent
JP2007326746A (en) * 2006-06-08 2007-12-20 Fujimi Kogyo Kk Organic fertilizer and its application method
EP2196443A1 (en) * 2008-12-03 2010-06-16 Marcello Lustri Incinerated husk
JP2012125667A (en) * 2010-12-13 2012-07-05 Miki Sato Method for preventing thickening and solidification of scum in sewage treatment tank

Cited By (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US7140778B2 (en) 2002-03-01 2006-11-28 Minebea Co., Ltd. Synthetic resin composites and bearings formed therefrom and method
US7144932B2 (en) * 2002-03-01 2006-12-05 Minebea Co., Ltd. Low-friction, high-dispersion synthetic resin composition containing fine particles of RB ceramic or CRB ceramic and a method for its preparation
US6887288B2 (en) 2002-06-05 2005-05-03 Minebea Co., Ltd. Superfinishing grindstone
US7160622B2 (en) 2003-01-07 2007-01-09 Minebea Co., Ltd. Oil repelling agent
JP2007326746A (en) * 2006-06-08 2007-12-20 Fujimi Kogyo Kk Organic fertilizer and its application method
EP2196443A1 (en) * 2008-12-03 2010-06-16 Marcello Lustri Incinerated husk
JP2012125667A (en) * 2010-12-13 2012-07-05 Miki Sato Method for preventing thickening and solidification of scum in sewage treatment tank

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