JPS5934260A - Activation of plant rot mud - Google Patents

Activation of plant rot mud

Info

Publication number
JPS5934260A
JPS5934260A JP57144615A JP14461582A JPS5934260A JP S5934260 A JPS5934260 A JP S5934260A JP 57144615 A JP57144615 A JP 57144615A JP 14461582 A JP14461582 A JP 14461582A JP S5934260 A JPS5934260 A JP S5934260A
Authority
JP
Japan
Prior art keywords
mud
activation
crushing
humus
degree
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.)
Granted
Application number
JP57144615A
Other languages
Japanese (ja)
Other versions
JPS6237003B2 (en
Inventor
森下 惟雄
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.)
Individual
Original Assignee
Individual
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 Individual filed Critical Individual
Priority to JP57144615A priority Critical patent/JPS5934260A/en
Publication of JPS5934260A publication Critical patent/JPS5934260A/en
Publication of JPS6237003B2 publication Critical patent/JPS6237003B2/ja
Granted legal-status Critical Current

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  • Solid-Sorbent Or Filter-Aiding Compositions (AREA)
  • Agricultural Chemicals And Associated Chemicals (AREA)
  • Compounds Of Unknown Constitution (AREA)
  • Disinfection, Sterilisation Or Deodorisation Of Air (AREA)
  • Treatment Of Sludge (AREA)

Abstract

(57)【要約】本公報は電子出願前の出願データであるた
め要約のデータは記録されません。
(57) [Summary] This bulletin contains application data before electronic filing, so abstract data is not recorded.

Description

【発明の詳細な説明】 本発明は植物性腐植泥の活性化方法に関する。[Detailed description of the invention] The present invention relates to a method for activating vegetable humus mud.

稙11勿姓腐植泥とは、現在、又は嘗て長い年月の間海
底、湖底等の水中に堆積していた植物質の醗酵物質であ
る。
11. Humic mud is a fermented plant material that is currently or has been deposited in water such as the seabed and lakebed for many years.

本出願人は先K IF!j願昭55−94563号に上
って植物性腐植泥を強制酸化し、乾燥してイ1られるガ
ス職種性消臭殺菌組成物に関して特許出願したが、更罠
強力な殺菌力、消臭性ガス吸着性を持った組成物を得る
ことを目的として研究を続けて来た。その結果本発明の
活性化方法を見出すに至りた。そもそも、植物性腐植泥
がある程度、 it’4臭作用全作用ことはか々り以前
から知られていたが。
The applicant is the first KIF! J Application No. 55-94563, he filed a patent application for a gas-based deodorizing and sterilizing composition in which vegetable humus mud is forcibly oxidized and dried, but it has even stronger sterilizing and deodorizing properties. We have continued our research with the aim of obtaining a composition with gas adsorption properties. As a result, the activation method of the present invention was discovered. In the first place, it has been known for a long time that vegetable humus mud has all the 4 odor effects to some extent.

堀り上げた腐植泥はそのま\では消臭力のバラツキが大
きく、殆んど消臭効果のないものがジい。
The deodorizing power of the dug humus mud as it is varies widely, and it is often found that it has almost no deodorizing effect.

従来性なわれて来た方法を」堀り上げた含水[4(J泥
を単に自然乾燥させて粉砕する方法であるが。
This is a method of simply drying and pulverizing the water-containing mud [4], which is a conventional method.

之だけでは消臭力の増強は殆んど見られない。This alone hardly increases the deodorizing power.

野積みして数ケ月にわたって天日乾燥させたものはかな
り消臭力が認められるがそれも表面の極〈一部分に過ぎ
ない。
Items that have been piled up in the open and dried in the sun for several months are known to have considerable deodorizing power, but this is only a small part of the surface.

本発明者は腐植泥の消臭作用につい−(: 4’+If
々(iJ)究を重ねた結果、腐414泥を強制酸化する
ことによって消臭力が増強され、同時にガス吸着性、静
菌作用も強化されることを見出して前述の特願昭55−
94563号を出願中m/it、たものであるが、その
際、酸化の方法として単に空気にさらす程度では酸化不
充分で効果が少ないことを実験的に確認した。
Regarding the deodorizing effect of humus mud, the present inventor has determined that -(: 4'+If
As a result of repeated research, it was discovered that by forcibly oxidizing Fu414 mud, the deodorizing power was enhanced, and at the same time, the gas adsorption and bacteriostatic effects were also strengthened.
No. 94563 is pending, and at that time, it was experimentally confirmed that simply exposing the material to air as an oxidation method was insufficient and had little effect.

以後HX、4ti泥の消臭作用、ガス吸着性及び静菌作
用の強化等を綜合して腐植泥の活性化と呼ぶことにする
。腐植泥の活性化の機構については、腐植泥そのものの
組成が複雑で、長年多くの研究者により研究がなされて
いるが、まだ定説はない。
Hereinafter, the deodorizing action, gas adsorption, and bacteriostatic action enhancement of HX and 4ti mud will be collectively referred to as activation of humus mud. Regarding the mechanism of activation of humic mud, the composition of humic mud itself is complex, and although many researchers have conducted research for many years, there is still no established theory.

更に1本発明者は腐植泥が空気酸化によシ活性化される
のは湿潤状態においCだけであり、乾燥状態では活性化
の進行が停滞することも実験的に見出した。
Furthermore, the present inventor has experimentally found that only C is activated by air oxidation in humic mud in a wet state, and that the progress of activation is stagnant in a dry state.

それらの実験的事実から本発明者tま、腐植泥の活性化
には空気中の酸素による酸化作用と共に。
Based on these experimental facts, the present inventors believe that the activation of humus mud involves the oxidation effect of oxygen in the air.

微生物、特に好気性菌の作用も併せて関与していると推
定するに至った。
We have come to the conclusion that microorganisms, especially aerobic bacteria, are also involved.

すなわち腐植泥を水切りして水分70〜80俤程度のも
のをハンマーミル型粉砕機にかけて破砕し、空気と充分
に接触する状態になしたる後、ビニールハウス内につみ
上げて数日間静首する。
That is, after draining the humus mud and crushing it with a water content of about 70 to 80 yen using a hammer mill-type crusher to bring it into sufficient contact with air, it is pumped up in a plastic greenhouse and left to stand for several days. .

之を熟成と呼ぶ。この間、適当な水分の存在下でro・
!生物による各種の反応が行なわれていると考えられる
This is called maturing. During this time, ro・
! It is thought that various reactions are carried out by living organisms.

すなわち破砕により表面積を拡大して、空気との接触面
積を大にすることによって酸素の供給を充分にすること
と、適度の水分を保持しながら。
In other words, crushing expands the surface area and increases the contact area with air, thereby ensuring a sufficient supply of oxygen and retaining an appropriate amount of moisture.

微生物反応が進行するに充分な時間を与えることが腐植
泥活性化のポイントである。
The key to activating humus mud is to provide sufficient time for microbial reactions to proceed.

更に破砕によって腐植泥がかきまV−られ、活性のバラ
ツキが均質化されることも重要なポイントである。
Another important point is that the humus sludge is stirred by crushing and the variation in activity is homogenized.

従って破砕工程を省いては酸素の供給が円滑に行なわれ
ないし2本来1品質のバラツキが大きい腐植泥の均質化
も行なわれない。
Therefore, if the crushing step is omitted, the supply of oxygen will not be carried out smoothly, and the humus mud, which inherently has large variations in quality, will not be homogenized.

また、水分Vl敬生物反応に不可欠で、少なくとも50
チ以上が望ましいが、一方、水分が多過ぎると(例えば
90チ以上では)腐植泥はペースト状になって、酸素の
供給が不充分になるので好ましくない。
In addition, water Vl is essential for biological reactions, with at least 50%
On the other hand, if the water content is too high (for example, 90 cm or more), the humic mud becomes pasty and oxygen supply becomes insufficient, which is not preferable.

好適な水分量は50チないし80嗟である。The preferred amount of water is 50 inches to 80 degrees.

熟成工程は室温で行なうが熟成時間は゛数日好ましくは
50以上が必髪である。
The aging process is carried out at room temperature, and the aging time should preferably be several days, preferably 50 days or more.

温度を上げると熟成反応は幾分促進されるが。Raising the temperature will somewhat accelerate the ripening reaction.

水分の蒸発も多くなって、水分50条を下まわると熟成
反応が停滞してし寸うので、結局活性化が不完全になり
易い。但しその場合でも水を適当に噴霧するなどして、
水分が常に50%を切らないように配慮すれば活性化の
停T′ftFを防ぐことはできる。
The evaporation of moisture also increases, and if the moisture content falls below 50 degrees, the ripening reaction is likely to stagnate, resulting in incomplete activation. However, even in that case, by spraying water appropriately,
If care is taken to ensure that the moisture content does not always fall below 50%, activation termination T'ftF can be prevented.

破砕工程と熟成工程における腐植泥の性状変化を見ると
、PHが低下し、  Brlx度が高くなることがrl
HEiされる。すなわちPHは破砕前は中性CPH=6
.5〜7.0)であるが、破砕−熟成工程を経て次第に
低下し、PH:JQを切るに至る。
Looking at the changes in the properties of humus mud during the crushing process and aging process, it can be seen that the pH decreases and the Brlx degree increases.
HEi will be done. In other words, the pH is neutral CPH = 6 before crushing
.. 5 to 7.0), but gradually decreases through the crushing-ripening process, reaching PH:JQ.

Brlx度は破砕前は0.1前後のものが0.7〜1.
0穆度まで上昇する。
The Brlx degree is around 0.1 before crushing, but it is 0.7 to 1.
It rises to 0 degrees.

(A表参照)之に伴って腐植泥の消臭力、ガス吸着性及
び静菌作用等が強化きれ、すなわち活性化が進行する。
(See Table A) As a result, the deodorizing power, gas adsorption, bacteriostatic action, etc. of humus mud are strengthened, that is, activation progresses.

腐植泥の活性度の指標としてPHとBrlx度を採用す
る所以である。
This is the reason why PH and Brlx degree are used as indicators of the activity of humus mud.

A表 破砕、熟成共に常温で行なっているが、熟成中の試料温
度V130〜X56℃であった。
Table A: Both crushing and ripening were carried out at room temperature, but the sample temperature during ripening was V130 to X56°C.

PHの測定は試料(乾重量で’)  20J’rを常温
でイメン交換水を加えて2001rとし、30分間浸漬
攪拌し、V出液をPH計(電気化学計器(株)MO−フ
型)で測った。
To measure the pH, 20J'r of the sample (dry weight) was added to 2001r at room temperature with Imen-exchanged water, immersed and stirred for 30 minutes, and the V solution was measured using a PH meter (Denki Kagaku Keiki Co., Ltd. MO-F type). It was measured with

Brlx度は上記浸出液をrタボ屈折計N−IQを用い
j水道水を使って、零点調整を行なった後)測定した。
The degree of Brlx was measured using a Tabo refractometer N-IQ (after zero point adjustment) using tap water.

比較のために破砕工程を省いた熟成工程のみの場合のP
HBrlx度の変化を見るとB表のようになる。
For comparison, P in the case of only the aging process without the crushing process
Table B shows the change in HBrlx degree.

P H= 3.□ Brlx度=0.4を標準活性度と
しているが、破砕工程を省いた熟成工程のみの場合は3
0日間程度では標準活性度に達しないことが分る。。
PH=3. □ The standard activity is Brlx degree = 0.4, but in the case of only the aging process without the crushing process, it is 3
It can be seen that the standard activity is not reached in about 0 days. .

結局、破砕工程では空気との接触面積を増大して酸素の
取入れを充分にし、且つ原料をよく混合して均質化させ
1次いで熟成工程では適度の水分を保持することによっ
て腐植泥の活性化を進行させ、熟成時間を充分に与える
ことによって活性化が完成する。
After all, in the crushing process, the contact area with air is increased to ensure sufficient oxygen intake, and the raw materials are thoroughly mixed and homogenized.Then, in the ripening process, the humus mud is activated by retaining an appropriate amount of moisture. Activation is completed by allowing sufficient aging time.

破砕工程を省くと、空気との接触面積が少ないので酸素
の取入れが不充分になり、又、乾燥が速すぎると熟成時
間不足となり、何れも活性化が不完全になる。破砕−熟
成の組合せを本命とする所以である。
If the crushing step is omitted, the contact area with air will be small, resulting in insufficient oxygen uptake, and if drying is too rapid, aging time will be insufficient, resulting in incomplete activation. This is why the combination of crushing and ripening is the favorite.

破砕工程と熟成工程を経たものを再度破砕工程にかけ1
次いで熟成工程にかけると腐植泥の活性化に1更に進む
。腐植泥の水分が50饅以上であれtir破砕−熟成の
組合せの繰返しに依り、腐植泥の活性度は(の都度向上
するが、実用上から云えば3回が限度である。
After passing through the crushing process and aging process, the product is subjected to the crushing process again.1
Then, when it is subjected to a maturing process, the humus mud is further activated. Even if the water content of the humus mud is 50 ml or more, the activity of the humus mud will improve each time the combination of tir crushing and ripening is repeated, but from a practical standpoint, the limit is three times.

之以上4回、5回と繰返し又も手間をかける割には活性
度の向上はそれ程大きくない。
Although repeating this process four or five times takes effort, the improvement in activity is not that great.

以下実施例によって説明することは、破砕工程及び熟成
工程の組合せによって腐植泥の活性化がどのようVC進
行するか、−!た。破砕工程を行なわずに、ただ放置し
て自然乾燥させた場合、活性化の進行が如何に遅く且つ
不完全に終るかを示す。
The following examples will explain how VC progresses in the activation of humic mud by the combination of the crushing process and the aging process. Ta. This shows how slowly and incompletely the activation progresses if the material is left to air dry without a crushing step.

活性化度の指徘としてはPH及びBrlx度を以てする
The degree of activation is determined by PH and Brlx degree.

ここで云う活性度とは腐植泥の消臭力、ガス吸着性、静
菌作用等を綜合した性能で数字を以て表革q、すること
は出来ないが、  PHが低い程、  Brlx度が高
い程活性度が高いことが確認さtlており。
The activity referred to here refers to the performance that combines the deodorizing power, gas adsorption, bacteriostatic action, etc. of humus mud, and cannot be expressed in numbers, but the lower the pH, the higher the degree of Brx. It has been confirmed that the activity is high.

実用上の標準品としては、  PH= 3.Q Br1
x度=0.4と決めたものである。
As a practical standard product, PH=3. Q Br1
It was decided that x degrees = 0.4.

〔実施例1〕 水分80饅の腐植泥をハンマーミル型粉砕機にかけて破
砕し1次に之をビニルノ・ウス内に山積みして熟成5 
E+、 lo日zoE]/&のPH、Brlx度及び水
分を示すと表1のようになる。
[Example 1] Humus mud with a moisture content of 80 ml was crushed using a hammer mill type crusher, and the first layer was piled up in a vinyl container and aged 5.
Table 1 shows the PH, Brlx degree, and moisture content of E+, lo day zoE]/&.

表1 〔実施例2〕 実施例1と同じロットの腐植泥を破砕工程を省略して山
ワ1(みしたt烏合の50,10日、20日。
Table 1 [Example 2] The same lot of humus mud as in Example 1 was used on the 50th, 10th, and 20th days of Yamawa 1 (Mishita T) without the crushing step.

30日後のPH、Brlx度及び水分を示すと表2の如
くなる。
Table 2 shows the PH, Brlx degree, and moisture content after 30 days.

表2 〔実施例3〕 実施例1と同じ腐植泥を破砕−熟成(5B )の組合せ
を経返し4回行なった場合の各回毎のPH。
Table 2 [Example 3] PH for each time when the same humus mud as in Example 1 was subjected to the crushing-ripening (5B) combination four times.

Brlx度及び水分を示す表−3の如くなる表−3 出願人 : 亜  下  惟  雄 代理人X弁理士佐々井弥太部  □ (ほか°I名)Table-3 as shown in Table-3 showing Brlx degree and moisture content Applicant: Akio Shimo Agent X Patent Attorney Yatabe Sasai □ (Other °I names)

Claims (1)

【特許請求の範囲】[Claims] 水分50〜80チの範囲の植物性腐植泥を破砕して、空
気と充分接触せしめる工程と1次にこの破砕物を静置し
、水分50〜80 %を保持しながら熟成させる工程と
を組合せることを特徴とする(p物PI:n<植泥を活
性化させる方法
This method combines the process of crushing vegetable humus mud with a water content of 50 to 80% and bringing it into sufficient contact with air, and the first step of allowing the crushed material to stand still and aging while retaining a moisture content of 50 to 80%. (method for activating p-product PI: n<
JP57144615A 1982-08-23 1982-08-23 Activation of plant rot mud Granted JPS5934260A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP57144615A JPS5934260A (en) 1982-08-23 1982-08-23 Activation of plant rot mud

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP57144615A JPS5934260A (en) 1982-08-23 1982-08-23 Activation of plant rot mud

Publications (2)

Publication Number Publication Date
JPS5934260A true JPS5934260A (en) 1984-02-24
JPS6237003B2 JPS6237003B2 (en) 1987-08-10

Family

ID=15366145

Family Applications (1)

Application Number Title Priority Date Filing Date
JP57144615A Granted JPS5934260A (en) 1982-08-23 1982-08-23 Activation of plant rot mud

Country Status (1)

Country Link
JP (1) JPS5934260A (en)

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS6414187A (en) * 1987-07-09 1989-01-18 Morishita Koreo Microbial activation for vegetable humud mud
JPH01153605A (en) * 1987-12-11 1989-06-15 Koreo Morishita Foliar application agent
JPH01168790A (en) * 1987-12-25 1989-07-04 Koreo Morishita Soil conditioning material
JP2006273734A (en) * 2005-03-29 2006-10-12 Enzyme Kk Humus, humus extract solution, moisturizing liquid, their manufacturing method and use

Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS4966447A (en) * 1972-10-26 1974-06-27
JPS5391121A (en) * 1977-01-22 1978-08-10 Tokyo Shiyokubutsu Kagaku Kenk Sterilizing agent and use thereof

Patent Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS4966447A (en) * 1972-10-26 1974-06-27
JPS5391121A (en) * 1977-01-22 1978-08-10 Tokyo Shiyokubutsu Kagaku Kenk Sterilizing agent and use thereof

Cited By (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS6414187A (en) * 1987-07-09 1989-01-18 Morishita Koreo Microbial activation for vegetable humud mud
JPH0571562B2 (en) * 1987-07-09 1993-10-07 Morishita Gijutsu Kenkyusho Kk
JPH01153605A (en) * 1987-12-11 1989-06-15 Koreo Morishita Foliar application agent
JPH01168790A (en) * 1987-12-25 1989-07-04 Koreo Morishita Soil conditioning material
JPH0353351B2 (en) * 1987-12-25 1991-08-14 Morishita Kijutsu Kenkyusho Kk
JP2006273734A (en) * 2005-03-29 2006-10-12 Enzyme Kk Humus, humus extract solution, moisturizing liquid, their manufacturing method and use

Also Published As

Publication number Publication date
JPS6237003B2 (en) 1987-08-10

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