JP3479505B2 - Soil revegetation and stabilization material and its construction method - Google Patents

Soil revegetation and stabilization material and its construction method

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Publication number
JP3479505B2
JP3479505B2 JP2000294126A JP2000294126A JP3479505B2 JP 3479505 B2 JP3479505 B2 JP 3479505B2 JP 2000294126 A JP2000294126 A JP 2000294126A JP 2000294126 A JP2000294126 A JP 2000294126A JP 3479505 B2 JP3479505 B2 JP 3479505B2
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Japan
Prior art keywords
soil
greening
bacteria
cement
added
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Japanese (ja)
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JP2002101753A (en
Inventor
俊治 溝上
卓哉 丸本
敏宏 福永
Original Assignee
多機能フィルター株式会社
山口興産株式会社
株式会社オルタナ
綜合緑化株式会社
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  • Cultivation Of Plants (AREA)
  • Pit Excavations, Shoring, Fill Or Stabilisation Of Slopes (AREA)

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】この発明は、土壌、化成肥
料、パーク堆肥、ピートモス等の植生基盤材に強度保持
材として添加混合した石灰またはセメント系固化材の呈
するアルカリ性を低減して、植物の発芽、生育に適した
土壌基盤を作ることができる土壌緑化・安定化資材及び
その施工方法に関するものである。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention reduces the alkalinity exhibited by lime or cement-based solidifying material added and mixed as a strength-retaining material to vegetation base materials such as soil, chemical fertilizer, park compost, peat moss, etc. The present invention relates to a soil greening / stabilizing material capable of forming a soil base suitable for growth and a construction method thereof.

【0002】[0002]

【従来の技術】切土または盛土の法面は、法面造成時に
は安定しているが、時間の経過とともに不安定となり、
侵食、落石、崩壊などが生じて、徐々にその規模が拡大
することがある。このため、法面の保護が必要である。
表面強度のある一般的な土質の場合は、簡便な種子吹き
付けが行われるが、表面強度が弱い場合は、法を構築
するか、法面全面にモルタルを吹き付けるかしている。
2. Description of the Related Art The slope of cut or embankment is stable when the slope is created, but becomes unstable with the passage of time.
The scale may gradually increase due to erosion, rockfall, and collapse. Therefore, slope protection is necessary.
In the case of general soil with high surface strength, simple seed spraying is performed, but when surface strength is weak, a legal framework is constructed or mortar is sprayed over the entire slope.

【0003】[0003]

【発明が解決しようとする課題】ところが、モルタルの
吹き付けは、法面表面が灰色となるから、景観上からあ
まり好ましくない。安価で強度のある地表面の被覆材と
しては、セメント系固化材に勝るものはない。セメント
系の固化材は、早期に安定し、水に強く、雨に流亡され
にくい利点を有するためである。しかし、その強アルカ
リ性は、ほとんどの植物の生育に適さず、自然保護の面
からも、好ましくない。
However, spraying mortar is not very preferable from the viewpoint of landscape because the slope surface becomes gray. As an inexpensive and strong coating material for the ground surface, there is no substitute for the cement-based solidifying material. This is because the cement-based solidifying material has an advantage that it is stable in an early stage, is strong against water, and is hard to be washed away by rain. However, its strong alkalinity is not suitable for the growth of most plants and is not preferable from the viewpoint of nature protection.

【0004】この対策としては、過リン酸石灰等のpH
緩衝剤や硫酸アルミニウム等の酸性物質の添加によるア
ルカリ性低減策が提言されている。しかし、セメントの
強度とアルカリ性の低減との相克状態をいまだ脱却しえ
ていない。
As a countermeasure against this, the pH of lime superphosphate, etc.
A measure for reducing alkalinity by adding an acidic substance such as a buffer or aluminum sulfate has been proposed. However, the conflict between the strength of cement and the reduction of alkalinity has not yet been overcome.

【0005】環境と調和した法面を造成するためには、
法面に敷設する植生基盤材の強度を上げ、植生基盤材を
植物の生育に適するように改善し、その基盤材に植物を
導入して法面の保護を行うことが望ましい。植生基盤材
の強化には、セメント系固化材を利用すればよいが、そ
の場合に植物の生育に問題となるのが、セメントによる
アルカリ障害である。
In order to create a slope in harmony with the environment,
It is desirable to increase the strength of the vegetation base material laid on the slope, improve the vegetation base material so that it is suitable for plant growth, and introduce plants into the base material to protect the slope. A cement-based solidifying material may be used for strengthening the vegetation base material, but in that case, a problem with plant growth is alkali damage caused by cement.

【0006】そこで、この発明においては、植物の生育
に問題となるセメント系固化材によるアルカリ障害の改
善を微生物の生態を利用して行うことを試みた。供試菌
株については、アルカリ性環境に生育する細菌を選抜す
ることとした。多くの細菌は、pHが9程度のアルカリ
性に対する耐性機構を有している。しかし、これらの細
菌は、中性の環境で生育しているものがほとんどであ
る。
Therefore, in the present invention, it was attempted to improve the alkali damage caused by the cement-based solidifying material which is a problem for the growth of plants by utilizing the ecology of microorganisms. For the test strains, it was decided to select bacteria that grow in an alkaline environment. Many bacteria have a resistance mechanism against alkalinity with a pH of about 9. However, most of these bacteria grow in a neutral environment.

【0007】ところが、pH10以上で最も生育が良
く、pH11.5でも生育する細菌が存在しており、そ
れらは好アルカリ性細菌と呼ばれている。好アルカリ性
細菌は、pHが中性や極端に高い培地で培養すると、そ
れらの培地は、アルカリ化したり、酸性化したりして、
やがて、pH9付近の値に落ち着くことが観察されてい
る。
However, there are bacteria that grow best at pH 10 or higher and grow even at pH 11.5, and they are called alkalophilic bacteria. When an alkalophilic bacterium is cultivated in a medium having a neutral pH or an extremely high pH, the medium becomes alkaline or acidified,
It has been observed that eventually it will settle to a value near pH 9.

【0008】この発明は、このような技術的背景の下に
なされたもので、特に、好アルカリ性細菌を利用して、
植生基盤材に添加混合する石灰またはセメント系固化材
のpHを低下させ、植物の生育しやすい土壌基盤をつく
ることができる土壌緑化・安定化資材とその施行法を提
案することを目的としている。
The present invention has been made under such a technical background, and particularly, by utilizing alkalophilic bacteria,
The purpose of the present invention is to propose a soil revegetation / stabilization material that can lower the pH of lime or cement-based solidifying material that is added to and mixed with the vegetation base material, and create a soil base on which plants can grow easily, and its enforcement method.

【0009】[0009]

【課題を解決するための手段】この発明が提供する土壌
緑化・安定化資材は、土壌、化成肥料、ーク堆肥、ピ
ートモス等の植生基盤材と石灰系またはセメント系固化
材との混合物である緑化資材と、この緑化資材に接種す
る好アルカリ性細菌とよりなるものである(以下、第1
の資材という)。
Means for Solving the Problems] Soil greening and stabilization material to which this invention provides is soil, fertilizer, bar click compost, with a mixture of vegetation base material and the lime or cement solidifying material such as peat moss It consists of a certain greening material and an alkaliphilic bacterium that inoculates this greening material (hereinafter referred to as the first
Of materials).

【0010】第1の資材における好アルカリ性細菌は、
Aeromonas hydrophila、Baci
llus alcalophilus、Bacillu
s thuringiensis、Claibact
er michiganense、Bacillus
subtilis、のうちの少なくとも1種である。
Alkaliphilic bacteria in the first material are
Aeromonas hydrophila, Baci
llus alcalophilus, Bacillu
s thuringiensis, Cla v ibact
er michiganense, Bacillus
subtilis, or at least one of them.

【0011】また、この発明が提供する土壌緑化・安定
資材の施工法は、緑化資材に水を加えてスラリーとし、
このスラリーに凝固剤と好アルカリ性細菌を添加混合す
る施工法である。
Further, the method for constructing a soil greening / stabilizing material provided by the present invention is to add water to the greening material to form a slurry,
This is a construction method in which a coagulant and alkalophilic bacteria are added to and mixed with this slurry.

【0012】この施行法において使用する好アルカリ性
細菌は、Aeromonas hydrophila、
Bacillus alcalophilus、Bac
illus thuringiensis、Cla
bacter michiganense、Bacil
lus subtilis、のうちの少なくとも1種で
ある。
Alkaliphilic bacteria used in this procedure are Aeromonas hydrophila,
Bacillus alcalophilus, Bac
illus thuringiensis, Cla v i
Bacter Michiganense, Bacil
at least one of L. subtilis.

【0013】上記セメント系固化材は、セメント、灰
分、硫酸礬土、土壌のうちの少なくともセメントを主成
分とするものである。
The cement-based solidifying material contains at least cement among cement, ash, sulphate and soil as a main component.

【0014】[0014]

【作用】この発明の好アルカリ性細菌による石灰系また
はセメント系固化材のアルカリ性の低減機構、すなわ
ち、石灰系またはセメント系固化材の固化の進行に伴っ
て生成する遊離アルカリの低減機構は、今後の研究に待
たざるを得ない。しかし、遊離アルカリの低減は、恐ら
く、上記微生物の生態作用によって発生する有機酸の中
和効果によるものと考えられる。
The mechanism for reducing the alkalinity of the lime-based or cement-based solidifying material by the alkali-philic bacteria of the present invention, that is, the mechanism for reducing the free alkali generated as the solidification of the lime-based or cement-based solidifying material progresses I have to wait for research. However, it is considered that the reduction of free alkali is probably due to the neutralizing effect of the organic acid generated by the ecological action of the above microorganisms.

【0015】従来のアルカリ性低減に使用される無機酸
性物質は、強酸性であり、その中和作用は、セメント自
体の中和にも消費され、場合によっては、セメントの強
度発現を阻害するような難点がある。これに対して、こ
の発明の好アルカリ細菌の生態作用によって発生する
と考えられる弱酸性の有機酸は、セメント本来の機能を
害うことなくセメントの強度発現物質である珪酸カルシ
ウム水和物ゲルの生成に伴って生じる遊離石灰のアルカ
リを中和すると考えられる。
The conventional inorganic acidic substances used for reducing alkalinity are strongly acidic, and their neutralizing action is also consumed for the neutralization of the cement itself and, in some cases, inhibits the strength development of the cement. There are difficulties. In contrast, weakly acidic organic acids which are considered to be generated by the ecological effects of alkalophilic bacteria of the present invention, the calcium silicate hydrate gel is strength development material cement without intends harm the cement original function It is considered to neutralize the alkali of free lime that accompanies the formation.

【0016】[0016]

【発明の実施の形態】以下、この発明の実施の形態を実
施例によって説明する。
BEST MODE FOR CARRYING OUT THE INVENTION Embodiments of the present invention will be described below with reference to examples.

【0017】(実施例1) 実施例1では、バーク堆肥、ピートモス、化成肥料から
なる植物基盤材にセメント系固化材を添加混合して得ら
れる緑化資材に、好アルカリ性細菌を接種して、調製す
る土壌緑化・安定化資材について説明する。
Example 1 In Example 1, a greening material obtained by adding and mixing a cement-based solidifying material to a plant base material composed of bark compost, peat moss, and chemical fertilizer was inoculated with an alkaliphilic bacterium for preparation. Explain the soil greening / stabilizing materials to be used.

【0018】この資材は、前記固化資材のpHを低下さ
せ、植物の生育しやすい土壌基盤、特に、切土または盛
土の法面の保護に適した土壌基盤を作るのに有効であ
る。
This material is effective in lowering the pH of the solidifying material and making a soil base on which plants can easily grow, especially a soil base suitable for protecting the slope of cut soil or embankment.

【0019】法面の土壌浸食防止と緑化を行う方法とし
ては、その表面層を土壌にセメントを混合したソイルセ
メントで形成する方法、あるいは池沼からの浚渫土ある
いは汚泥などを含む土壌にセメント系固化材を混合した
もので形成する方法がある。
As a method of preventing soil erosion and greening on the slope, a method of forming the surface layer with soil cement in which cement is mixed with soil, or a cement-based solidification method for soil containing dredged soil or sludge from an Ikenuma There is a method of forming a mixture of materials.

【0020】しかし、いずれの方法もその強アルカリ性
のため、植物の生育には不適切である。そこで、まず始
めに、好アルカリ性細菌を利用して強アルカリ性セメン
ト系資材のpHを低下させ、植物が生育しやすい土壌基
盤をつくることを目的として、好アルカリ性細菌のスク
リーニングを行った。
However, either method is not suitable for plant growth because of its strong alkalinity. Therefore, first, the alkali-philic bacteria were screened for the purpose of lowering the pH of the strongly alkaline cement-based material by utilizing the alkali-philic bacteria and creating a soil base on which plants can easily grow.

【0021】我が国には、アルカリ性土壌は極めて少な
いが、それらの地域の土壌から好アルカリ性細菌のスク
リーニングを行うことにした。供試土壌の採取場所は、
山口県S市、山口県Y市、島根県M市の3ヵ所である。
その後、上記3ヵ所で採取した8つの試料を用いて、菌
株のスクリーニングを行った。各試料のpHは、6.3
〜8.7の範囲にあった。スクリーニングは、上記3ヵ
所の土壌から、34種類の好アルカリ性細菌を単離し
た。このうち生育日数の早い(1〜3日)好アルカリ性
細菌15株を寒天培地を用いた接種試験に供した。
Although there are very few alkaline soils in Japan, we decided to screen the soils in those areas for alkalophilic bacteria. The sampling location of the test soil is
There are three locations, S city in Yamaguchi prefecture, Y city in Yamaguchi prefecture, and M city in Shimane prefecture.
After that, the strains were screened using the eight samples collected at the above-mentioned three places. The pH of each sample is 6.3.
It was in the range of ˜8.7. In the screening, 34 kinds of alkalophilic bacteria were isolated from the above-mentioned three soils. Of these, 15 strains of alkalophilic bacteria that had a fast growth period (1 to 3 days) were subjected to an inoculation test using an agar medium.

【0022】接種試験では、細菌の培地のpHは、いず
れも、約1〜3低下することが分かった。このことか
ら、セメント系固化材に、これらの菌株を接種した場
合、それらの増殖に伴って、同固化材中のpHは低下す
ると考えられた。
In the inoculation test, it was found that the pH of the bacterial culture medium was lowered by about 1 to 3 in all cases. From this, it was considered that when the cement-based solidifying material was inoculated with these strains, the pH in the solidifying material was lowered with the growth of the strains.

【0023】(1)緑化資材に接種する好アルカリ性細
菌の選抜 好アルカリ性細菌の分離に用いた表1に示す組成の基本
培地から、寒天と炭酸ナトリウムを除いたものを、40
0mlのイオン交換水で溶解し、16本の100ml容
三角フラスコに20mlずつ分注するとともに、炭酸ナ
トリウムを100mlのイオン交換水で溶解し、それぞ
れ別々に、オートクレーブで120℃、20分間滅菌し
た。この後、クリーンベンチ内で無菌的に、上記16本
の三角フラスコの中に炭酸ナトリウムの溶液を5mlず
つ分注、混合した。
(1) Selection of alkalophilic bacteria to inoculate greening material A basal medium having the composition shown in Table 1 used for the isolation of alkalophilic bacteria, which is obtained by removing agar and sodium carbonate, is
It was dissolved in 0 ml of ion-exchanged water, dispensed in 20 ml portions into 16 100 ml Erlenmeyer flasks, sodium carbonate was dissolved in 100 ml of ion-exchanged water, and each was separately sterilized in an autoclave at 120 ° C. for 20 minutes. Then, aseptically in a clean bench, 5 ml of a solution of sodium carbonate was dispensed into each of the 16 Erlenmeyer flasks and mixed.

【0024】[0024]

【表1】 この好アルカリ性細菌用の液体培地に、前述の生育の早
い15菌株をそれぞれ植菌した。これを25℃で振盪培
養し、pHと吸光度の変化を測定した。
[Table 1] The above-mentioned fast-growing 15 strains were inoculated into the liquid medium for alkalophilic bacteria. This was shake-cultured at 25 ° C., and changes in pH and absorbance were measured.

【0025】その結果を基に、後述する緑化資材に接種
する好アルカリ性細菌として、次の5種を選抜した。こ
れらの細菌A〜Eは、初期pH値10の液体培養におい
て、培養後急激に菌が増殖し、pH値も、それに伴って
低下し、最終pHは約7.5という望ましい値を示し
た。
Based on the results, the following five species were selected as alkalophilic bacteria to be inoculated on the greening material described later. In the liquid cultures having an initial pH value of 10, these bacteria A to E showed rapid growth of the bacteria after the culture, the pH value thereof decreased correspondingly, and the final pH value showed a desirable value of about 7.5.

【0026】A:Aeromnas hydrohpi
la(以下、細菌Aという) B:Bacillus alcalohpilus(以
下、細菌Bという) C:Bacillus thuringiensis
(以下、細菌Cという) D:Claibacter michiganens
e(以下、細菌Dという) E:Bacillus subtilis(以下、細菌
Eという) (2)選抜した好アルカリ性細菌による液体培地のpH
および吸光度の変化 pH5、7、10の液体培地に、後述する緑化資材に接
種する好アルカリ性細菌A〜Dを約1×105cell
ml-1となるように、それぞれpH10の液体培地に植
菌した。これを25℃で振盪培養し、pHと吸光度の変
化を経時的に測定した。
A: Aeromnas hydrohpi
la (hereinafter, referred to as bacterium A) B: Bacillus alcalohpilus (hereinafter, referred to as bacterium B) C: Bacillus thuringiensis
(Hereinafter referred to as the bacteria C) D: Cla v ibacter michiganens
e (hereinafter referred to as Bacteria D) E: Bacillus subtilis (hereinafter referred to as Bacteria E) (2) pH of the liquid medium by the selected alkalophilic bacteria
And change in absorbance About 1 × 10 5 cells of alkaliphilic bacteria A to D to be inoculated into a greening material described later in a liquid medium of pH 5, 7, 10
Each of the cells was inoculated into a liquid medium having a pH of 10 so that the volume became ml −1 . This was shake-cultured at 25 ° C., and changes in pH and absorbance were measured with time.

【0027】pH10の液体培地において、好アルカリ
性細菌の増殖に伴うpHの低下パターンは、2通りある
ことが分かった。1つは、徐々に菌が増殖し、pHもそ
れに伴って低下するが、その後再び上昇するパターンで
あり、もう1つは、培養後急激に菌が増殖し、pHもそ
れに伴って低下するパターンである。また、それぞれの
菌株について、pH5、7、10の液体培地におけるp
Hと吸光度の変化を測定した結果、細菌Aは、pH7で
の生育が最も早いが、最初の培地pHが5、7、10い
ずれの時も、pH9付近に落ち着いた。細菌Bは、pH
10での生育が最も早かった。細菌Cは、pH7での生
育が最も早く、pH5付近まで低下させるが、pH5お
よび10で培養開始したものは、pH9付近に落ち着い
た。細菌D、Eは、pH7での生育が最も早く、pH5
および7で培養開始したものは、pH4付近まで低下さ
せるが、pH10で開始したものは、pH9付近に落ち
着いた。
It has been found that there are two patterns of pH decrease associated with the growth of alkalophilic bacteria in a liquid medium having a pH of 10. One is a pattern in which the bacteria gradually grow and the pH decreases with it, but then it rises again, and the other is a pattern in which the bacteria grow rapidly after culturing and the pH also decreases with it. Is. Also, for each strain, p in liquid medium of pH 5, 7, 10
As a result of measuring changes in H and absorbance, bacteria A grew fastest at pH 7, but settled to around pH 9 when the initial medium pH was 5, 7, or 10. Bacteria B has a pH
Growth at 10 was fastest. Bacterium C grows fastest at pH 7 and decreases to around pH 5, but those that started culturing at pH 5 and 10 settled at around pH 9. Bacteria D and E grow fastest at pH 7 and at pH 5
The cultures started at 7 and 7 lowered to around pH 4, but those started at pH 10 settled at around pH 9.

【0028】(3)緑化資材への選抜した好アルカリ性
細菌の接種 植生基盤材(ーク堆肥、ピートモスの混合物)15g
と化成肥料0.11gをフラスコに入れ、シリコン栓を
した後、オートクレーで120℃、20分間滅菌し
た。セメント系固化材(表5の固化材)0.15gを薬
包紙に包んでシャーレに入れ、170℃で1時間滅菌し
た。これらをクリーンベンチ内で無菌的に混合して緑化
資材とした。
[0028] (3) inoculation vegetation base material of alkalophilic bacteria were selected to greening materials (bar click compost, a mixture of peat moss) 15 g
And put fertilizer 0.11g flask, after the silicone stopper, 120 ° C. in an autoclave, and sterilized 20 min. 0.15 g of the cement-based solidifying material (solidifying material in Table 5) was wrapped in medicine packing paper, put in a petri dish, and sterilized at 170 ° C. for 1 hour. These were aseptically mixed in a clean bench to obtain a greening material.

【0029】一方、液体培地で生育させた細菌A〜Eの
数を測定し、それぞれの菌株をピペットで1mlずつ取
り、無菌水9mlに加えたものを1次希釈液とし(希釈
倍率10-1)、各1次希釈液を更に、それぞれ2×10
4 cellml-1となるように調製した。得られた各希
釈液0.5mlを、それぞれ10本の三角フラスコに入
れた緑化資材に接種した。
On the other hand, the number of bacteria A to E grown in a liquid medium was measured, 1 ml of each strain was taken with a pipette and added to 9 ml of sterile water to make a primary dilution (dilution ratio 10 -1). ), Further add each primary dilution to 2 x 10
It was adjusted to 4 cellml -1 . 0.5 ml of each of the obtained diluted solutions was inoculated into the greening material contained in 10 Erlenmeyer flasks.

【0030】この操作は、いずれもクリーンベンチ内で
無菌的に行った。緑化資材のpHは、同資材25gに無
菌水50mlを加え、pHメーターにて測定した。緑化
資材中の生菌数は、希釈平板法(基本培地:表1)にて
測定した。
This operation was performed aseptically in a clean bench. The pH of the greening material was measured with a pH meter by adding 50 ml of sterile water to 25 g of the same material. The viable cell count in the greening material was measured by the dilution plate method (basic medium: Table 1).

【0031】その結果、緑化資材へ選抜した細菌A〜E
を接種した際、殆どの菌株が培養7日目で、緑化資材の
pH値を約0.5〜1低下させていた。このことから、
当初の目的であった植物の生育初期でのアルカリ障害を
早い時期に改善できることが分かった。
As a result, bacteria A to E selected as greening materials
When inoculated with, most of the strains lowered the pH value of the greening material by about 0.5 to 1 on the 7th day of culture. From this,
It was found that alkaline damage at the early stage of plant growth, which was the original purpose, could be improved early.

【0032】植物の発芽・生育に必要な土壌の条件とし
て、一般的に、pH値が8.5以下、硬さが、中山式硬
度指数値で20以下が望ましいと言われている。本発明
者の経験によると、セメント系固化材による土壌pH値
の推移は、強度発現の進行に伴い生じる遊離石灰が、雨
水や、土壌中の酸性物質により中和されるか、そのまま
流出するかで、比較的早い時期にpH値は8.5内外に
達する。しかし、更にpH値を0.5〜1.0低下さ
せ、植物の発芽・生育により望ましいpH値の領域:
7.0〜7.5以下に到達させるには、可成りの日数を
要する。
It is generally said that a pH value of 8.5 or less and a hardness of 20 or less in terms of Nakayama's hardness index value are desirable as soil conditions required for germination and growth of plants. According to the experience of the present inventor, the change in soil pH value due to the cement-based solidifying material indicates whether free lime generated along with the progress of strength expression is neutralized by rainwater or acidic substances in the soil, or flows out as it is. Then, the pH value reaches 8.5 or less at a relatively early time. However, the pH value is further lowered by 0.5 to 1.0, and the pH value range desirable for germination and growth of plants is:
It takes a considerable number of days to reach 7.0 to 7.5 or less.

【0033】この点、実施例3の緑化資材のpH値は、
一週間という初期の段階で、0.5〜1.0低下した。
この事実は、実施例の土壌緑化・安定化資材の実用化を
可能にするものと考えられる。
In this respect, the pH value of the greening material of Example 3 is
In the early stage of one week, it decreased by 0.5 to 1.0.
This fact is considered to enable the practical use of the soil greening / stabilizing material of the examples.

【0034】(実施例2) 実施例1に示した植生基盤材100g、化成肥料0.7
5g、セメント系固化材2g(20kg/m3相当)、
種子として、トールフェスクファルコン0.1g(30
粒)を良く混合して緑化資材とした。
Example 2 100 g of the vegetation base material shown in Example 1 and 0.7 of chemical fertilizer.
5 g, cement-based solidifying material 2 g (equivalent to 20 kg / m 3 ),
As seeds, tall fescue falcon 0.1 g (30 g
Granules) were mixed well to make a greening material.

【0035】一方、液体培養で、望ましいpH値の低減
を示した細菌Aを実施例1と同じ2×104cellm
-1なる希釈液とし、この希釈液3.3mlを上記緑化
資材に加えて良く混合し、然る後、底にメッシュ網を敷
いた200mlの3号鉢に、充填し、良く押さえつけて
植生ポットとした。植生ポットは、各細菌Aを加えたも
のを4個作った。また、菌株を添加しないブランク試料
を入れた植生ポットも同様の方法で4個作成した。
On the other hand, the same 2 × 10 4 cellm as used in Example 1 was used for the bacterium A showing a desired reduction in pH value in liquid culture.
A diluted solution of l −1 was added, and 3.3 ml of this diluted solution was added to the above-mentioned greening material and mixed well, then filled in a 200 ml No. 3 pot with a mesh net on the bottom, and well pressed down to vegetate. It was a pot. Four vegetation pots were prepared by adding each bacterium A. Four vegetation pots containing blank samples to which no strain was added were also prepared in the same manner.

【0036】このようにして得られた植生ポットを、温
度条件20〜25℃の温室に配置した。表2は、3週後
の、発芽生育本数、ポット中の緑化資材のpH値と硬度
指数を示す。表2の試験結果より、菌株有りの方が、発
芽生育率が1.5倍高く、pH値は0.5低く、硬度指
数は、変わらず、好ましい値となっていた。
The vegetation pot thus obtained was placed in a greenhouse under temperature conditions of 20 to 25 ° C. Table 2 shows the number of germinated growth after 3 weeks, the pH value of the greening material in the pot, and the hardness index. From the test results shown in Table 2, the germination growth rate was 1.5 times higher, the pH value was 0.5 lower, and the hardness index was the same without change, with the presence of the strain.

【0037】[0037]

【表2】 (実施例3) 実施例3では、まず、表3に示す植生基盤材932gと
実施例1のセメント系固化材20gの混合物に水260
gを加えて、移送可能なスラリーとし、これに凝固剤を
加えた場合の性状について調べた。本来ならば、このス
ラリーの吹き付けノズル出口に、凝固剤を加え、吹き付
け後のスラリーを一瞬にして、固形化させ、ダレないコ
ンポジットを生成させることになるが、この実施例で
は、そのモデル実験として、表4に示す各種凝固剤をス
ラリーに20gずつ添加し、添加前後のスラリーの性状
を調べた。表4はその性状を示す。
[Table 2] (Example 3) In Example 3, first, a mixture of 932 g of the vegetation base material shown in Table 3 and 20 g of the cementitious solidifying material of Example 1 was mixed with water 260.
g was added to obtain a transferable slurry, and the properties when a coagulant was added were examined. Originally, a coagulant was added to the outlet of the spray nozzle of this slurry, and the slurry after spraying was instantly solidified to produce a composite without sagging, but in this example, as a model experiment thereof, 20 g of each coagulant shown in Table 4 was added to the slurry, and the properties of the slurry before and after the addition were examined. Table 4 shows the properties.

【0038】いずれの場合も、準スランプ値は低下し、
ダレ難いコンポジットへ変化していた。
In any case, the quasi-slump value decreases,
It had changed to a composite that was difficult to sag.

【0039】[0039]

【表3】 [Table 3]

【0040】[0040]

【表4】 上記モデル実験で得られた各種凝固剤添加後のダレ難い
コンポジットを、素早く樋型耐散水試験器具(自作品)
の充填箱(125×125×45mm)3個に分けて詰
め、屋外に放置し、耐散水試験用試験体を作成した。1
日経過後、各充填箱から取り出した試験体(コンポジッ
ト)をそれぞれ個別に8分勾配になるようにセットした
木製箱型樋にのせ、各試験体に全自動噴霧器により、約
100mm/hr程度の散水強度で、水を噴霧した。
[Table 4] Quickly gutter type water sprinkling resistance test equipment (own work)
The filling box (125 × 125 × 45 mm) was packed into 3 pieces and left outdoors, and a test piece for a water resistance test was prepared. 1
After a lapse of days, the test pieces (composite) taken out from each filling box were placed on a wooden box type gutter which was set individually to have a gradient of 8 minutes, and each test piece was sprayed with a fully automatic sprayer at about 100 mm / hr. Intense, water sprayed.

【0041】表5は、コンポジットの1日後の流出土量
の測定結果を示す。流出土量はコンポジット試験体3個
の平均値である。噴霧散水強度:100mm/hr前後
の流出土量は、いずれのセメント系固化材〜凝固剤の場
合も、ブランク(セメント系固化材及び凝固剤を添加せ
ず)の場合より、少なく、大幅な改善が認められた。
Table 5 shows the results of measuring the amount of runoff soil one day after the composite. The amount of soil runoff is the average value of three composite specimens. Spray sprinkling strength: The amount of runoff soil around 100 mm / hr is less than any blank case (without adding the cement-based solidifying material and the solidifying agent) in any of the cement-based solidifying material to the solidifying agent, which is a significant improvement. Was recognized.

【0042】[0042]

【表5】 次に、表3に示す植生基盤材932gに、化成肥料(ス
ミカエース)5g、実施例1のセメント系固化材20
g、種子として、トールフェスクファルコン1.0(3
00粒)を加え、良く混合して緑化資材とした。つい
で、この資材に水260gを加えてスラリーとし、これ
に凝固剤として、3号珪曹((株)トクヤマ社製)(1
+1)希釈水溶液20gと、実施例1で示した細菌Aの
2×104cellml-1の希釈液33mlを加え良く
混合した。
[Table 5] Next, to 932 g of the vegetation base material shown in Table 3, 5 g of chemical fertilizer (Sumika Ace), and the cementitious solidifying material 20 of Example 1 were used.
g, as seed, tall fescue falcon 1.0 (3
(00 grains) was added and mixed well to obtain a greening material. Then, 260 g of water was added to this material to form a slurry, and as a coagulant, No. 3 silica (manufactured by Tokuyama Corp.) (1
+1) 20 g of the diluted aqueous solution and 33 ml of the 2 × 10 4 cell ml −1 diluted solution of the bacterium A shown in Example 1 were added and mixed well.

【0043】得られた土壌緑化・安定化資材を植生試験
用ポット5個に、150mlずつ充填した。また、菌株
を添加しないブランク試料についても同様な方法でポッ
ト5個を作成した。このようにして得られた植生ポット
を屋外に設置した。
The obtained soil greening / stabilizing material was filled in 5 pots for vegetation test, 150 ml each. In addition, 5 pots were prepared in the same manner for blank samples to which no strain was added. The vegetation pot thus obtained was installed outdoors.

【0044】表6は3週後の発芽成育本数、ポット中の
緑化資材のpH値と硬度指数を示す。表6の試験結果よ
り、菌株有りの方が、発芽生育率が1.3倍高く、pH
値は0.5低く、硬度指数も2低く、好ましい値を示し
ていることが分かった。
Table 6 shows the number of germinated seedlings after 3 weeks, the pH value of the greening material in the pot and the hardness index. From the test results in Table 6, the germination growth rate was 1.3 times higher and the pH was higher with the strain.
It was found that the value was 0.5 lower and the hardness index was 2 lower, indicating a preferable value.

【0045】[0045]

【表6】 [Table 6]

【0046】[0046]

【発明の効果】以上説明したように、この発明によれ
ば、上述のような構成としたから、植生基盤材に添加混
合される石灰系またはセメント系固化材の固化に伴って
生成する遊離アルカリを低減し、植物の生育しやすい土
壌基盤をつくることができる。
As described above, according to the present invention, since it has the above-mentioned constitution, the free alkali generated by the solidification of the lime-based or cement-based solidifying material added to and mixed with the vegetation base material. Can be reduced and a soil base on which plants can grow easily can be created.

───────────────────────────────────────────────────── フロントページの続き (72)発明者 溝上 俊治 山口県徳山市大字徳山1007−14 (72)発明者 丸本 卓哉 山口県山口市中尾702−2 (72)発明者 福永 敏宏 山口県下松市末武中和田1337 (56)参考文献 特開 平10−98938(JP,A) (58)調査した分野(Int.Cl.7,DB名) A01G 1/00 303 E02D 17/20 102 ─────────────────────────────────────────────────── --- Continuation of the front page (72) Inventor Shunji Mizoue 1007-14 Tokuyama, Tokuyama City, Yamaguchi Prefecture (72) Inventor Takuya Marumoto 702-2 Nakao, Yamaguchi City, Yamaguchi Prefecture (72) Toshihiro Fukunaga Shimomatsu City, Yamaguchi Prefecture Suetake Kaneda 1337 (56) Reference JP-A-10-98938 (JP, A) (58) Fields investigated (Int.Cl. 7 , DB name) A01G 1/00 303 E02D 17/20 102

Claims (4)

(57)【特許請求の範囲】(57) [Claims] 【請求項1】 土壌、化成肥料、ーク堆肥、ピートモ
ス等の植生基盤材と石灰系またはセメント系固化材との
混合物である緑化資材と、この緑化資材に接種する好ア
ルカリ性細菌とよりなる土壌緑化・安定化資材。
1. A soil, the more chemical fertilizers, bar click compost, and planting material is a mixture of vegetation base material and the lime or cement solidifying material such as peat moss, and alkalophilic bacteria inoculated into the planting material Soil greening and stabilizing material.
【請求項2】 前記好アルカリ性細菌は、 Aeromonas hydrophila、 Bacillus alcalophilus、 Bacillus thuringiensis、 Claibacter michiganense、 Bacillus subtilis、 の少なくとも1種である請求項1記載の土壌緑化・安定
化資材。
Wherein said alkalophilic bacteria, Aeromonas hydrophila, Bacillus alcalophilus, Bacillus thuringiensis, Cla v ibacter michiganense, Bacillus subtilis, according to claim 1 soil greening and stabilization material according at least one.
【請求項3】 請求項1の土壌緑化・安定化資材の施工
法であって、緑化資材に水を加えてスラリーとし、この
スラリーに凝固剤と好アルカリ性細菌を添加混合するこ
とを特徴とする土壌緑化・安定化資材の施工法。
3. The method for constructing a soil greening / stabilizing material according to claim 1, wherein water is added to the greening material to form a slurry, and a coagulant and an alkaliphilic bacterium are added to and mixed with the slurry. Construction method of soil greening and stabilizing materials.
【請求項4】 前記好アルカリ性細菌は、 Aeromonas hydrophila、 Bacillus alcalophilus、 Bacillus thuringiensis、 Claibacter michiganense、 Bacillus subtilis、 のうちの少なくとも1種である請求項3記載の土壌緑化
・安定化資材の施行法。
Wherein said alkalophilic bacteria, Aeromonas hydrophila, Bacillus alcalophilus, Bacillus thuringiensis, Cla v ibacter michiganense, Bacillus subtilis, at least one kind Enforcement Act soil greening and stabilization material according to claim 3, wherein one of .
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