JP2009284872A - Method for adjusting soil nourishment environment, and bag-like material and compost extracted solution to be used for the method - Google Patents

Method for adjusting soil nourishment environment, and bag-like material and compost extracted solution to be used for the method Download PDF

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JP2009284872A
JP2009284872A JP2008143380A JP2008143380A JP2009284872A JP 2009284872 A JP2009284872 A JP 2009284872A JP 2008143380 A JP2008143380 A JP 2008143380A JP 2008143380 A JP2008143380 A JP 2008143380A JP 2009284872 A JP2009284872 A JP 2009284872A
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soil
bag
zeolite
compost
base
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Hiroshi Kimura
弘 木村
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SOGO SEKKEI KENKYUSHO KK
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SOGO SEKKEI KENKYUSHO KK
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Abstract

<P>PROBLEM TO BE SOLVED: To provide a bag-like material for creating a soil environment which has a buffer action for not removing a base too much while removing a surplus base in soil, and to provide a method for adjusting a plant nourishment environment. <P>SOLUTION: The method for creating a balanced soil nourishment environment comprises physically taking out and removing a base from soil by substituting for and sticking to zeolite in a bag a surplus base in soil, and making organic matter extracted from compost act as a buffer material when substituting and sticking base by zeolite. <P>COPYRIGHT: (C)2010,JPO&INPIT

Description

本発明は、塩基吸着機能を持った物質を充填した袋を土中に埋設し、土中の塩基を袋中の吸着機能を持った物質に吸着せしめて、袋を土中から取り出す方法により土中の塩基を除去するとともに、土中に堆肥抽出による有機溶液を注入することによって土壌の緩衝能を増大せしめて、塩基除去に伴う土中塩類濃度の急激な変化に対する緩衝能を高め、もって植物に対する土壌養分環境を調節する土壌改良方法ならびにそれに使用する資材に関する。   In the present invention, a bag filled with a substance having a base adsorption function is embedded in the soil, the base in the soil is adsorbed by the substance having the adsorption function in the bag, and the bag is taken out of the soil by a method. In addition to removing the base in the soil, the buffer capacity of the soil is increased by injecting an organic solution by compost extraction into the soil, thereby increasing the buffer capacity against abrupt changes in soil salt concentration due to base removal. The present invention relates to a soil improvement method for adjusting the soil nutrient environment for the soil and materials used therefor.

近年農園芸の施設化と化学肥料の多様化が進み、土壌の塩類過剰集積が見られ、あるいは土壌中に有害重金属が集積し、更にはチッ素肥料の過剰施用にともなう栽培植物の軟弱生長が多く発生するなどの土壌養分環境の劣化が生じた。そのため土壌中の過剰塩基等の除去の必要性が高まってきた。
この土壌中の過剰塩基除去法で、従来より行われていた主なものは、次の3点である。
(1)土壌水洗法
(2)土壌の置き換え(客土法)
(3)ゼオライト等の塩基置換容量の大きい物質を土中に混合して塩基の吸着を行う方法
In recent years, the establishment of agricultural and horticultural facilities and the diversification of chemical fertilizers have progressed, and there has been an excessive accumulation of salt in the soil, or the accumulation of harmful heavy metals in the soil. Deterioration of soil nutrient environment, such as frequent occurrence, occurred. Therefore, the necessity of removing excess bases in soil has increased.
The following three points have been conventionally used in this method for removing excess base in soil.
(1) Soil flushing method (2) Replacing soil (custom soil method)
(3) A method of adsorbing a base by mixing a substance having a large base substitution capacity such as zeolite in the soil.

また土壌中の養分環境を調節する主な方法としては、次の3点が挙げられる。
(4)堆肥等有機物あるいは鉱物性の土壌改良材を固形分として土壌中に混入する方法
(5)フミン酸等の液体有機物を直接土壌に注入し、または固形物に含浸させて供給する方法
(6)長い網筒内に空隙率の大きい鉱物を詰めたものを土中に埋設する方法
Moreover, the following 3 points | pieces are mentioned as a main method of adjusting the nutrient environment in soil.
(4) Method of mixing organic matter such as compost or mineral soil improver into the soil as solid content (5) Method of supplying liquid organic material such as humic acid directly into the soil or impregnating the solid material 6) A method of burying a long net tube filled with minerals with a high porosity in the soil

前記(1)土壌水洗法では塩類を地下深部に流し込むだけであり、(2)客土法の場合は客土層の下に塩基濃度の高い土層が依然として存在するため前記(1)、(2)の方法では地下からの毛管水により塩基が再度上昇する可能性が高い。
また、(3)ゼオライト等の塩基置換容量の大きい物質を土壌中に混入する方法の場合、ゼオライト等の塩基吸着は可逆的な置換作用であるため、ゼオライト粒の周辺の塩基濃度が低下した場合、ゼオライト粒は吸着した塩基を放出してしまうという問題点がある。
このように、従来の塩基除去法は過剰塩基を確実に除去するものではなかった。
In the (1) soil washing method, only salt is poured into the deep underground. (2) In the case of the customer soil method, a soil layer having a high base concentration still exists under the customer soil layer. In the method 2), there is a high possibility that the base will rise again due to capillary water from the underground.
(3) In the case of a method in which a substance with a large base substitution capacity such as zeolite is mixed in the soil, the base adsorption around the zeolite particles decreases because the adsorption of the base such as zeolite is a reversible substitution action. The zeolite particles have a problem of releasing the adsorbed base.
As described above, the conventional base removal method does not reliably remove excess base.

また、前記(3)ゼオライト粒を土壌中に混合した場合において、ゼオライトはカリウム、チッ素(アンモニア)、ナトリウム、カルシウム等の植物養分を良く吸着する性質がある。植物の生育は、カリウムが十分であれば根部の発達がよく、チッ素が過少である場合は茎葉の生長が遅れる性質があることから、ゼオライトを施用すると根部の発達がよいものの、チッ素供給が少なめとなり、植物全体としての生育が遅れがちになるという問題があった。   Further, when (3) the zeolite particles are mixed in the soil, the zeolite has a property of adsorbing plant nutrients such as potassium, nitrogen (ammonia), sodium and calcium well. The plant grows well if potassium is sufficient, and if nitrogen is insufficient, the growth of the stem and leaves is delayed. There was a problem that the growth of the whole plant tends to be delayed.

さらに、土壌中の養分環境を調節する方法である前記(4)、(5)の方法の場合、これらの方法に用いられる土壌改良材等の資材は、塩基置換吸着能が小さく、かつ環境を調節する物質である固形物を土中の特に地表からの深さの特定位置に供給することが困難であった。また、(6)の方法は、網筒内に充填された物質が真珠岩系のものであって塩基置換容量の小さい物質であることから塩基除去機能が小さい等の問題があった。   Furthermore, in the case of the above methods (4) and (5), which are methods for adjusting the nutrient environment in the soil, the materials such as soil conditioners used in these methods have a small base substitution adsorption capacity, and the environment. It was difficult to supply the solid material as the substance to be adjusted to a specific position in the soil, particularly at a depth from the ground surface. In addition, the method (6) has a problem that the base removal function is small because the substance filled in the mesh tube is a pearlite-based substance with a small base substitution capacity.

本発明は前記従来方法の課題を解決するためになされたものであって、土壌中の塩基を、土壌中の任意の位置から吸着捕捉して直接的にとり出して除去する。さらに土壌中に有機溶液を注入することによって土壌の緩衝能を増大せしめて、塩基除去に伴う土中塩類濃度の急激な変化に対する緩衝能を高め、もって植物に対する土壌養分環境を調節する方法とそれに使用する資材を提供することを目的とする。   The present invention has been made in order to solve the problems of the conventional method described above, and a base in soil is adsorbed and captured from an arbitrary position in the soil and directly taken out and removed. Furthermore, by increasing the buffer capacity of the soil by injecting an organic solution into the soil, increasing the buffer capacity against a sudden change in the salt concentration in the soil due to base removal, and thereby adjusting the soil nutrient environment for plants The purpose is to provide materials to be used.

本発明の要旨とするところは、土壌養分環境を調節するために用いられる袋状資材において、一定の強度を有し、かつ堆肥抽出溶液を容易に浸透させることができる材質によって構成し、内部に土壌中の塩基を置換吸着させるためのゼオライトを充填したことを特徴とする袋状資材である。   The gist of the present invention is that the bag-like material used for adjusting the soil nutrient environment is made of a material having a certain strength and capable of easily infiltrating the compost extract solution. A bag-like material characterized by being filled with zeolite for substitution adsorption of a base in soil.

また、本発明の要旨とするところは、前記袋状資材に充填するゼオライトを、クリノプチロライト系の材質によって構成し、粒径1.5〜2.5ミリメートルとしたことを特徴とする請求項1記載の袋状資材である。   The gist of the present invention is that the zeolite filled in the bag-like material is made of a clinoptilolite-based material and has a particle size of 1.5 to 2.5 mm. The bag-shaped material according to Item 1.

また、本発明の要旨とするところは、完熟堆肥1.0キログラムに対して水5キログラムを標準とする割合で混和し42〜48時間水浸の後、これを65〜75℃で、3〜4時間の低温抽出をおこなったのち、この抽出物を沈殿濾過して採取した土壌養分環境を調節するための堆肥抽出溶液である。   Moreover, the place made into the summary of this invention is mixing in the ratio which uses 5 kilograms of water as a standard with respect to 1.0 kilograms of fully-ripened composts, and after water immersion for 42 to 48 hours, this is 65-75 degreeC, 3 to This is a compost extract solution for adjusting the soil nutrient environment obtained by performing low temperature extraction for 4 hours and then collecting the extract by precipitation filtration.

また、本発明の要旨とするところは、一定の強度を有する材質によって構成され、ゼオライトを充填した袋状資材を土壌中に設置して過剰塩基を置換吸着し、その後前記袋状資材をゼオライトと共に土壌中より取り出して土壌中の過剰塩基を除去する土壌養分環境調節方法である。   Further, the gist of the present invention is that the bag-shaped material, which is made of a material having a certain strength, is placed in the soil to displace and adsorb excess base, and then the bag-shaped material is combined with the zeolite. It is a soil nutrient environment control method that is taken out from soil and removes excess base in the soil.

また、本発明の要旨とするところは、一定の強度を有する材質によって構成され、ゼオライトを充填した袋状資材を土壌中に設置し、その後前記袋状資材を開封して、内部に土壌養分環境を調節するための堆肥抽出溶液を注入して、前記ゼオライトの塩基の置換吸着の水準及び時期を緩衝制御することにより土壌中の植物養分環境を調節する土壌養分環境調節方法である。   Further, the gist of the present invention is that the bag-shaped material, which is made of a material having a certain strength and filled with zeolite, is installed in the soil, and then the bag-shaped material is opened, and the soil nutrient environment is contained inside. This is a soil nutrient environment control method for adjusting the plant nutrient environment in the soil by injecting a compost extract solution for controlling the amount of the zeolite and buffering and controlling the level and timing of the substitutional adsorption of the base of the zeolite.

本発明は、ゼオライトを充填した袋状資材を用いることにより、土壌中の塩基を他の土壌中や地下水中に移動するのでなく、塩基を吸着捕捉して直接的に土中からとり出すことができる。さらに袋状資材の設置位置と時期を任意に設定できるから、植物の育成期間の適切な時期を選んで自由に挿入及び除去することができ、効果的な作業が可能となり、ゼオライト施用に伴う植物の生育遅れに対処すると共に、資源を有効に利用できるのである。
また、本発明は、ゼオライトを充填した袋を土中から取り出し、これを水洗することによって容易に再利用することが可能であることから、資源の有効利用の面で、意義が大きい。
前記ゼオライトを、硬度の高いクリノプチロライト系ゼオライト粒の粒径1.5〜2.5ミリメートルとした場合に最も効果が発揮される。
In the present invention, by using a bag-shaped material filled with zeolite, the base in the soil is not moved to other soil or groundwater, but can be directly taken out from the soil by adsorption and capture. it can. Furthermore, since the installation position and timing of the bag-like material can be set arbitrarily, it can be freely inserted and removed at an appropriate time during the plant growth period, enabling effective work, and the plant accompanying the application of zeolite. As well as dealing with growth delays, resources can be used effectively.
In addition, the present invention can be easily reused by taking out a bag filled with zeolite from the soil and washing it with water.
The effect is most effective when the zeolite has a clinoptilolite-based zeolite particle size of 1.5 to 2.5 millimeters with high hardness.

本発明の堆肥抽出溶液は、他の溶液系の有機性土壌環境改善資材において、その代表たる腐食酸系資材であるフミン酸がアルカリと酸で抽出される化学薬品を使用する方法であるのに対して、薬品を使用することなく抽出する方法であることから、抽出後の残渣をもって醗酵させて堆肥に再生することが可能であり、堆肥抽出液の製造においても資源の有効利用、環境への負荷がなく、その効果が高い。 The compost extraction solution of the present invention is a method using a chemical in which humic acid, which is a representative corrosive acid-based material, is extracted with an alkali and an acid in another solution-based organic soil environment improving material. On the other hand, because it is a method of extraction without using chemicals, it is possible to ferment the residue after extraction and regenerate it into compost. There is no load and the effect is high.

本発明は、ゼオライトを充填した袋状資材を土壌中に埋設し、土壌中の塩基をゼオライトの作用によって吸着捕捉したのち、埋設した袋を土壌から取り出す方法によって、環境改善を要する土壌部位から直接的、確実に過剰塩基を除去することができる。
また、ゼオライト施用に伴う植物の生育遅れが生じる場合には、堆肥抽出溶液の併用によってもたらされる塩基吸着を緩衝する作用により、成長促進の環境造成が図られるのである。
The present invention embeds a bag-shaped material filled with zeolite in the soil, adsorbs and captures the base in the soil by the action of zeolite, and then removes the buried bag from the soil, directly from the soil site requiring environmental improvement. Therefore, excess base can be removed reliably.
Moreover, when the growth delay of the plant accompanying zeolite application arises, the environment creation of growth promotion is achieved by the effect | action which buffers the base adsorption | suction brought about by combined use with a compost extract solution.

堆肥抽出溶液を容易に浸透せしめることができ、かつ土中から引き出す張力にたえる不織布よりなる袋状資材を、植物の生育段階あるいは植物の栽培目的に対応した寸法に設定して作成する(図1、表1参照)。前記袋状資材に、クリノプチロライト系の粒径1.5〜2.5ミリメートルのゼオライトを充填し封かんして複数個土壌中に設置する。
一方、完熟堆肥1キログラム当り水5リットルを標準として、堆肥を水浸し42時間以上水浸ののち、温度70℃において3時間以上の低温抽出を行い、沈殿濾過した上澄み液を濃縮液として採取して堆肥抽出溶液を得る(図2参照)。なお、この場合、堆肥の含水率によって加える水量を加減する。その後、この堆肥抽出溶液の10〜100倍の希釈液を、前記袋状資材を開封して注入する。
その後、前記袋状資材を土壌中から取り出して土壌中の植物養分環境を調節する。
A bag-like material made of non-woven fabric that can be easily infiltrated with the compost extract solution and can withstand the tension drawn from the soil is set to a size corresponding to the plant growth stage or plant cultivation purpose (Fig. 1, see Table 1). A plurality of clinoptilolite-based zeolites having a particle size of 1.5 to 2.5 mm are filled in the bag-like material, sealed, and placed in the soil.
On the other hand, with 5 liters of water per kilogram of ripe compost as standard, the compost is immersed in water for at least 42 hours, followed by low temperature extraction at a temperature of 70 ° C. for at least 3 hours, and the precipitate filtered and collected as a concentrate. A compost extract solution is obtained (see FIG. 2). In this case, the amount of water added is adjusted depending on the moisture content of the compost. Thereafter, a dilute solution 10 to 100 times the compost extract solution is injected by opening the bag-shaped material.
Then, the said bag-shaped material is taken out from soil and the plant nutrient environment in soil is adjusted.

また、別の実施形態としては前記袋状資材を複数個紐によって一定間隔で取り付けて、多数の袋を連続的に土壌中に埋設することもできる。さらに前記不織布の色彩は緩衝、栽培等の目的に適した黒色、濃灰色、淡白色等の色彩を選択できる。   In another embodiment, a plurality of bag-like materials can be attached with a plurality of strings at regular intervals, and a large number of bags can be continuously embedded in the soil. Furthermore, the color of the said nonwoven fabric can select colors, such as black, dark gray, and light white suitable for the objectives, such as a buffer and cultivation.

西洋シバを試験植物として本資材と方法を試験した。試験の方法と結果は次の通り。   The material and the method were tested using a western buckwheat as a test plant. The test methods and results are as follows.

[試験方法]
試験植物は、西洋シバ混合種。
ゼオライト充填袋は、長さ8センチメートル、重さ6グラムのものをポット1個に対して3個あて使用。
ゼオライトは、粒径1.5〜2.5ミリメートル混合のクリノプチロライト系ゼオライトを使用。
堆肥の分量は、堆肥1キログラムに対して水5キログラムの割合で、予め調製したものを使用した。
堆肥抽出溶液の分量は、ポット1個に対して100倍の希釈液を1回50グラムずつ2週間に1回、合計4回注入した。
試験方法は、土壌の構成を変えたポリエチレンポット径7.5センチメートルに播種して生育を観察し、生長量を計測する方法。
土壌の構成を変えたポリエチレンポットの種類は、次の4種類(この混合比は重量比)であり、図3において、右からa、b、c、dの順で示してある。
a.ゼオライト充填袋3袋+赤玉4:堆肥1の割合で混合
b.パーライト粉0.5:赤玉4:堆肥1の割で混合
c.ゼオライト粉0.5:赤玉4:堆肥1の割で混合
d.赤玉4:堆肥1の割合で混合
これを2007年12月23日蒔きとした。
肥料は元肥を施用せず、途中2週間ごとに2月中旬まで2週間に1回の間隔で水溶肥料を施した。肥料は化成肥料14:14:14を1000倍にして使用した。生育途中で1回、9センチポットに植え替えした。
[Test method]
The test plant is a mixed species of Western buckwheat.
Zeolite-filled bags with a length of 8 cm and a weight of 6 grams are used for 3 pots.
The zeolite used is a clinoptilolite-based zeolite with a particle size of 1.5 to 2.5 millimeters.
The amount of compost used was prepared in advance at a ratio of 5 kilograms of water to 1 kilogram of compost.
As for the amount of the compost extraction solution, a 100-fold diluted solution was injected into each pot for 50 grams at a time, once every two weeks, for a total of 4 times.
The test method is a method in which the growth is observed by seeding in a polyethylene pot diameter of 7.5 centimeters having a different soil composition, and the growth amount is measured.
The following four types of polyethylene pots with different soil configurations (the mixing ratio is a weight ratio) are shown in the order of a, b, c, and d from the right in FIG.
a. 3 zeolite-filled bags + red ball 4: mixed at a rate of 1 compost b. Pearlite powder 0.5: Akadama 4: Mixed with compost 1 c. Zeolite powder 0.5: Akadama 4: Mixed with compost 1% d. Akadama 4: Mixed at a rate of 1 compost This was sowed on December 23, 2007.
The fertilizer was not applied with the original fertilizer, and the water-soluble fertilizer was applied every two weeks until the middle of February every two weeks. The fertilizer used was a chemical fertilizer 14:14:14 multiplied by 1000. The plant was replanted once into a 9 cm pot during the growth.

[試験結果]
計測試験は2008年4月6日に行った。試験結果は図4、5、6に示すように、地上部の生育はa、b、dが生育良好で、cは生長が劣る。根部の生育はa、bに大差がなく最大であり、ポットから根がはみ出している。dは根部の生育が最も遅れている。
数値的計測では表2に示すように、シバ草丈はcが23センチメールで最大であり、aが22センチメートル、dが21センチメートルと続き、bは18センチメートルと最小である。葉身の最大幅はaが5ミリメートル1枚、4.5ミリメートル3枚、dは4.4ミリメートル6枚、c.4.4ミリメートル3枚、bは3.9ミリメートル3枚であり、草丈とは幅を合わせて評価すると、地上部の生長はd、a、cがよくて、その差は大差なく、bが最も遅れている。
以上の地上部、根部の生育を総体的に評価すれば、cは草丈が最大ではあるが、aとの差はわずかであり、葉身幅や根部の生長を含めて評価すると、aゼオライト充填袋を使用し堆肥抽出溶液を加えた場合が最も優秀であると認められる。
[Test results]
The measurement test was conducted on April 6, 2008. As shown in FIGS. 4, 5, and 6, the aerial part has good growth of a, b, and d, and c has poor growth. The growth of the root is the largest with no significant difference between a and b, and the root protrudes from the pot. d is the most delayed root growth.
In numerical measurement, as shown in Table 2, the height of shiba is the maximum at 23 centimeter mail, a is 22 centimeters, d is 21 centimeters, and b is the minimum at 18 centimeters. The maximum width of leaf blades is a piece of 5 mm, 3 pieces of 4.5 mm, d is 6 pieces of 4.4 mm, c. 4.4 mm 3 pieces, b is 3.9 millimeters 3 pieces, and the plant height is evaluated by combining the width, the growth of the ground part is good d, a, c, the difference is not much difference, b is The most late.
If the above-mentioned growth of the above-ground part and the root part is evaluated as a whole, the height of c is the largest, but the difference from a is slight. It is recognized that it is the best when the compost extract solution is used.

ハツカダイコンを試験植物として本資材と方法を試験した。試験の方法と結果は次の通り。   This material and method were tested using radish as a test plant. The test methods and results are as follows.

[試験方法]
試験植物は、ハツカダイコン(紅白)。
ゼオライト充填袋は長さ8センチメートル、重さ6グラムのものをポット1個に対して4個あて使用。
ゼオライトは粒径1.5〜2.5ミリメートル混合のクリノプチロライト系ゼオライトを使用。
堆肥の分量は、堆肥1キログラムに対して水5キログラムの割合で予め調製したものを使用した。
堆肥抽出溶液の分量(希釈度)は、ポット1個に対して、100倍の希釈液を1回60グラムずつ2週間に1回、合計4回注入した。
試験方法は、土壌の構成を変えたポリエチレンポット径12センチメートルに播種して生育を観察し、生長量を計測する方法。
土壌の構成を変えたポリエチレンポットの種類は、次の4種類(この混合費は重量比)である。図8において、右からa、b、c、dの順で示してある。
なお、図8はポットから取り出した根の分布状態の写真である。図7は、ハツカダイコン全体の姿の写真であり、供試体ポットと予備ポットを示す。右から左にaゼオライト充填袋使用のポット、a−1予備ポット(aと同様組成)、b赤玉+堆肥のポット、b−1予備ポット(bと同様組成)。
a.ゼオライト充填袋4袋+赤玉4:堆肥1の割合で混合・・袋に堆肥抽出溶液注入
b.赤玉4:堆肥1の割で混合
c.ゼオライト粉0.5:赤玉4:堆肥1の割で混合・・土中に堆肥抽出溶液注入
d.ゼオライト粉0.5:赤玉4:堆肥1の割で混合
これを、2007年12月23日蒔きとした。
肥料は元肥を施用せず、途中2週間ごとに翌2008年2月中旬まで2週間に1回の間隔で水溶肥料を施した。肥料は化成肥料14:14:14を1000倍にして使用した。
[Test method]
The test plant is radish (red and white).
Zeolite-filled bags are 8 centimeters long and weigh 6 grams, using 4 pots per pot.
The zeolite used is a clinoptilolite-based zeolite with a particle size of 1.5 to 2.5 millimeters.
The amount of compost used was prepared in advance at a ratio of 5 kilograms of water to 1 kilogram of compost.
As for the amount (dilution degree) of the compost extraction solution, a 100-fold diluted solution was injected into a pot once every two weeks for 60 grams once, for a total of 4 times.
The test method is a method of sowing seeds in a polyethylene pot diameter of 12 centimeters with different soil composition, observing the growth, and measuring the amount of growth.
There are the following four types of polyethylene pots with different soil configurations (the mixing cost is weight ratio). In FIG. 8, a, b, c, and d are shown from the right.
FIG. 8 is a photograph of the distribution of roots taken out from the pot. FIG. 7 is a photograph of the overall shape of the radish, showing a specimen pot and a spare pot. From right to left, a pot using a zeolite-filled bag, a-1 preliminary pot (same composition as a), b red ball + compost pot, b-1 preliminary pot (same composition as b).
a. 4 zeolite-filled bags + Akadama 4: mixed at a rate of 1 compost-Inject compost extract solution into the bag b. Akadama 4: Mixed with compost 1 c. Zeolite powder 0.5: Akadama 4: Composting 1 compost, and compost extraction solution injection into the soil d. Zeolite powder 0.5: Akadama 4: Mixed with compost 1 This was fired on December 23, 2007.
The fertilizer was not applied with the original fertilizer, and the water-soluble fertilizer was applied every two weeks until the next mid-February 2008 every two weeks. The fertilizer used was a chemical fertilizer 14:14:14 multiplied by 1000.

[試験結果]
計測試験は2008年4月6日に行った。試験結果は図8、9、10に示すように、地上部の生育はa、b、c、dとも生育に大差がない。根部の生育はa、cに大差がなく最大である。b、dは根部の生育が遅れている。
数値的計測では表3に示すように、全草重量はハツカダイコン4本の合計がaが78グラムで最大であり、dが73グラム、cが70グラム、bが55グラムで最小である。根部については、aが55グラム、bは54グラム、cは50グラム、dは40グラムで最小である。
以上の全草、根部の生育を総体的に評価すれば、aが最も優秀であると認められる。
[Test results]
The measurement test was conducted on April 6, 2008. As shown in FIGS. 8, 9 and 10, the test results show that there is no significant difference in the growth of the above-ground parts in all of a, b, c and d. The root growth is maximum with no significant difference between a and c. In b and d, the root growth is delayed.
In the numerical measurement, as shown in Table 3, the total weight of the four radish is the maximum when a is 78 grams, d is 73 grams, c is 70 grams, and b is 55 grams. For the root, a is 55 grams, b is 54 grams, c is 50 grams, and d is 40 grams.
If overall growth of the above whole plant and root is evaluated, it is recognized that a is the most excellent.

ムギを試験植物として本資材と方法を試験した。試験の方法と結果は次の通り。   This material and method were tested using wheat as a test plant. The test methods and results are as follows.

[試験方法]
試験植物は、ムギ(品種名:笹の雪)。
ゼオライト充填袋は長さ6センチメートル、重さ3.5グラムのものをポット1個に対して3個あて使用。
ゼオライトは粒径1.5〜2.5ミリメートル混合のクリノプチロライト系ゼオライトを使用。
堆肥の分量は、堆肥1キログラムに対して水5キログラムの割合で調製したものを使用した。
堆肥抽出溶液の分量(希釈度)は、ポット1個に対して、100倍の希釈液30グラムを2週間に1回の割合で合計4回注入した。
試験方法は、土壌の構成を変えたポリエチレンポット径9センチメートルに播種して生育を観察し、生長量を計測する方法。
土壌の構成を変えたポリエチレンポットの種類は、次の2種類(この混合比は重量比)である。図11において、上からa、bの順で示してある。
a.ゼオライト充填袋3袋+赤玉6.7:堆肥1の割合で混合・・袋に堆肥抽出溶液注入。
b.赤玉6.7:堆肥1の割合で混合
これを、2007年12月23日蒔きとした。
肥料は元肥を施用せず、途中2週間ごとに翌2008年2月中旬まで2週間に1回の間隔で水溶肥料を施した。肥料は化学肥料14:14:14を1000倍にして使用した。
[Test method]
The test plant is wheat (variety name: strawberry snow).
Zeolite-filled bags with a length of 6 centimeters and a weight of 3.5 grams are used for three pots.
The zeolite used is a clinoptilolite-based zeolite with a particle size of 1.5 to 2.5 millimeters.
The amount of compost used was prepared at a ratio of 5 kilograms of water to 1 kilogram of compost.
As for the amount (dilution degree) of the compost extraction solution, 30 grams of a 100-fold diluted solution was injected into the pot four times at a rate of once every two weeks.
The test method is a method in which the growth is observed by sowing seeds in a polyethylene pot diameter of 9 centimeters in which the soil structure is changed, and the amount of growth is measured.
There are the following two types of polyethylene pots with different soil configurations (the mixing ratio is the weight ratio). In FIG. 11, a and b are shown in order from the top.
a. 3 zeolite-filled bags + red ball 6.7: mixed at a rate of 1 compost.
b. Akadama 6.7: Mixed at a rate of 1 compost This was sowed on December 23, 2007.
The fertilizer was not applied with the original fertilizer, and the water-soluble fertilizer was applied every two weeks until the next mid-February 2008 every two weeks. The fertilizer used was a chemical fertilizer 14:14:14 multiplied by 1000.

[試験結果]
計測試験は2008年4月26日に行った。試験計測は、草丈(頴を除く)、稈直径(地上15cm)、穂長(頴を除く)、穂幅の4項目である。計測結果は4項のうち、草丈、穂長、穂幅の3項目でaがbを上回り、稈直径ではbがaを上回っている。しかしながら、bの平均値は未だ出穂していない1茎を除外したものである事から、ムギの生育は全体としてaがbを上回る成績であると評価できる。これを表4および図11、12に示す。
[Test results]
The measurement test was conducted on April 26, 2008. There are four test measurements: plant height (excluding cocoons), cocoon diameter (15 cm above the ground), panicle length (excluding cocoons), and panicle width. Of the four measurement results, a is greater than b in three items of plant height, ear length, and ear width, and b is greater than a in the heel diameter. However, since the average value of b excludes one stem that has not yet emerged, the growth of wheat can be evaluated as a result in which a exceeds b as a whole. This is shown in Table 4 and FIGS.

[実施例1、2、3の総合評価]
以上の試験結果を全体的に見ると、成績の最も優秀であるのは、aゼオライトを充填した袋を土中に埋め込み、溶液を注入したポットであり、堆肥と赤玉土を混合した場合に比べて根部の発達がよく植物全体としても生育の良いことが、明らかである。
このようにして、本資材ならびに資材の使用方法の有効性は明らかである。また、本資材は、全体的に土壌から回収して再利用することが可能であることから、資源の有効利用が可能であり、環境への負荷が小さく、経済性に富んでいる。これらのことから、農園芸上の効果とともに社会的にも有意な資材ならびに技術である。
[Comprehensive evaluation of Examples 1, 2, and 3]
Looking at the above test results as a whole, the one with the best results is a pot filled with a zeolite filled in the soil and injected with the solution, compared to a mixture of compost and red crust. It is clear that the roots are well developed and the whole plant grows well.
In this way, the effectiveness of this material and the method of using the material is clear. In addition, since this material can be recovered from the soil as a whole and reused, resources can be used effectively, the burden on the environment is small, and the economy is high. From these facts, it is a material and technology that are socially significant as well as agricultural and horticultural effects.

(表1)ゼオライトを充填した袋の寸法

(Table 1) Dimensions of bags filled with zeolite

(表2)西洋シバ試験結果

(Table 2) Western wrinkle test results

(表3)ハツカダイコン試験結果

(Table 3) Radish test results

(表4)ムギ試験結果
(Table 4) Wheat test results

ゼオライトを充填した袋の写真Photo of a bag filled with zeolite 容器に入れた堆肥抽出溶液の写真Photograph of compost extract solution in container 西洋シバ全体の姿の写真A picture of the entire Western Shiba 西洋シバの根の発達状態の写真Photograph of the developmental state of the roots of Western Shiba 西洋シバの根の分布状態の写真Photo of the distribution of the roots of Western deer 西洋シバの根の発達状態で、白色の袋の周りの根の状態の写真A photograph of the state of the roots around a white bag in the developmental state of the roots of Western Shiba ハツカダイコン全体の姿の写真。供試体と予備ポットを示すA picture of the whole radish. Show specimen and spare pot ハツカダイコンの根の分布状態の写真Photograph of root distribution of radish ゼオライトを充填した袋にハツカダイコンの根が絡む状態の写真Photograph of the roots of radish tangled in a bag filled with zeolite ハツカダイコンの根を洗った状態で、供試体aの根の伸張が著しいことを示す写真A photograph showing that the roots of Specimen a are markedly stretched with the roots of radish washed. ムギ全体の姿の写真A picture of the whole wheat ムギの穂の状態の写真State of wheat ears

Claims (5)

土壌養分環境を調節するために用いられる袋状資材において、
一定の強度を有し、かつ堆肥抽出溶液を容易に浸透させることができる材質によって構成し、内部に土壌中の塩基を置換吸着させるためのゼオライトを充填したことを特徴とする袋状資材。
In the bag-like material used to adjust the soil nutrient environment,
A bag-like material comprising a material having a certain strength and capable of easily infiltrating a compost extraction solution and filled with zeolite for substitution adsorption of a base in soil.
前記袋状資材に充填するゼオライトを、クリノプチロライト系の材質によって構成し、粒径1.5〜2.5ミリメートルとしたことを特徴とする請求項1記載の袋状資材。 The bag-shaped material according to claim 1, wherein the zeolite filled in the bag-shaped material is made of a clinoptilolite-based material and has a particle size of 1.5 to 2.5 millimeters. 完熟堆肥1.0キログラムに対して水5キログラムを標準とする割合で混和し42〜48時間水浸の後、これを65〜75℃で、3〜4時間の低温抽出をおこなったのち、この抽出物を沈殿濾過して採取した土壌養分環境を調節するための堆肥抽出溶液。 After mixing with 5 kg of water as a standard to 1.0 kg of fully-ripened compost and soaking for 42 to 48 hours, this was subjected to low temperature extraction at 65 to 75 ° C. for 3 to 4 hours. Compost extract solution for adjusting the soil nutrient environment collected by precipitation filtration of the extract. 一定の強度を有する材質によって構成され、ゼオライトを充填した袋状資材を土壌中に設置して過剰塩基を置換吸着し、その後前記袋状資材をゼオライトと共に土壌中より取り出して土壌中の過剰塩基を除去する土壌養分環境調節方法。   It is composed of a material having a certain strength, and a bag-shaped material filled with zeolite is placed in the soil to displace and adsorb excess base, and then the bag-shaped material is taken out of the soil together with the zeolite to remove excess base in the soil. How to remove soil nutrient environment. 一定の強度を有する材質によって構成され、ゼオライトを充填した袋状資材を土壌中に設置し、その後前記袋状資材を開封して、内部に土壌養分環境を調節するための堆肥抽出溶液を注入して、前記ゼオライトの塩基の置換吸着の水準及び時期を緩衝制御することにより土壌中の植物養分環境を調節する土壌養分環境調節方法。 A bag-shaped material composed of a material having a certain strength and filled with zeolite is placed in the soil, then the bag-shaped material is opened, and a compost extraction solution for injecting a soil nutrient environment is injected into the inside. A soil nutrient environment adjustment method for adjusting the plant nutrient environment in the soil by buffering and controlling the level and timing of the base substitution adsorption of the zeolite.
JP2008143380A 2008-05-30 2008-05-30 Method for adjusting soil nourishment environment, and bag-like material and compost extracted solution to be used for the method Pending JP2009284872A (en)

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Citations (10)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS6173639A (en) * 1984-09-17 1986-04-15 オリンパス光学工業株式会社 Head apparatus of ultrasonic endoscope
JPS63101023A (en) * 1986-10-16 1988-05-06 Mitsubishi Heavy Ind Ltd Forming method for sheet stock
JPH05230459A (en) * 1991-12-04 1993-09-07 Nkk Corp Culture soil structure for salt-injured land
JPH05230457A (en) * 1991-12-04 1993-09-07 Nkk Corp Culture soil structure for arid land
JPH10210855A (en) * 1997-01-31 1998-08-11 Sumitomo Forestry Co Ltd Plant growing culture medium obtained by adding zeolite to soil generated at water purifying plant and manufacture therefor
JPH10304763A (en) * 1997-05-05 1998-11-17 Yukihiko Murata Wooded area managing method
JP2000188946A (en) * 1998-12-25 2000-07-11 Sumitomo Forestry Co Ltd Welsh onion nursing medium and method for producing same
JP2002051645A (en) * 2000-08-11 2002-02-19 Akimoto Tensanbutsu:Kk Flowerpot weight stone
JP2003342092A (en) * 2002-03-18 2003-12-03 Sanko:Kk Compost leach, method for producing the same, and plant growth promoting material
JP2004166645A (en) * 2002-11-21 2004-06-17 Misumi Sangyo:Kk Flowerpot stand

Patent Citations (10)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS6173639A (en) * 1984-09-17 1986-04-15 オリンパス光学工業株式会社 Head apparatus of ultrasonic endoscope
JPS63101023A (en) * 1986-10-16 1988-05-06 Mitsubishi Heavy Ind Ltd Forming method for sheet stock
JPH05230459A (en) * 1991-12-04 1993-09-07 Nkk Corp Culture soil structure for salt-injured land
JPH05230457A (en) * 1991-12-04 1993-09-07 Nkk Corp Culture soil structure for arid land
JPH10210855A (en) * 1997-01-31 1998-08-11 Sumitomo Forestry Co Ltd Plant growing culture medium obtained by adding zeolite to soil generated at water purifying plant and manufacture therefor
JPH10304763A (en) * 1997-05-05 1998-11-17 Yukihiko Murata Wooded area managing method
JP2000188946A (en) * 1998-12-25 2000-07-11 Sumitomo Forestry Co Ltd Welsh onion nursing medium and method for producing same
JP2002051645A (en) * 2000-08-11 2002-02-19 Akimoto Tensanbutsu:Kk Flowerpot weight stone
JP2003342092A (en) * 2002-03-18 2003-12-03 Sanko:Kk Compost leach, method for producing the same, and plant growth promoting material
JP2004166645A (en) * 2002-11-21 2004-06-17 Misumi Sangyo:Kk Flowerpot stand

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