JP3828737B2 - Planting soil and its manufacturing method - Google Patents
Planting soil and its manufacturing method Download PDFInfo
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- JP3828737B2 JP3828737B2 JP2000330757A JP2000330757A JP3828737B2 JP 3828737 B2 JP3828737 B2 JP 3828737B2 JP 2000330757 A JP2000330757 A JP 2000330757A JP 2000330757 A JP2000330757 A JP 2000330757A JP 3828737 B2 JP3828737 B2 JP 3828737B2
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Description
【0001】
【発明の属する技術分野】
本発明は、例えば建設汚泥などの土を改質処理する方法と同方法によって得られた処理土に関する。本方法で得られた処理土は、団粒化しており再泥化しないために環境への影響が少なく、かつ保水性に優れているために植栽用の土壌としての有効利用が可能である。
【0002】
【従来の技術】
土とは、主として岩石の風化作用によってできた比較的粒径の小さい粒の集合体であり、土質工学でいう「土」は、地盤を構成するあらゆる材料を含んでいるため、岩塊から粘度に至るまで、その粒子の大きさも広範囲であり、また、構成する材料も純粋な鉱物から産業廃棄物までいろいろな種類のものを含んでいる。例えば、建設汚泥、有機物含有量の多い河川、湖沼、運河、海域などに堆積したヘドロ、セメント等の固化材によって改質された浚渫埋立土が含まれる。したがって、その挙動はきわめて複雑で変化に富んでいる。
【0003】
上述した土でも、建設汚泥は高含水比状態を呈し、本来地盤を形づくっていた土が建設工事の過程で泥状となった場合が多く、有害物質などを含有する例は極めて稀である。
【0004】
【発明が解決しようとする課題】
建設汚泥は、建設工事に伴って発生する掘削汚泥や微細な泥状土などであり、そのままでは盛土などに直接流用できない。このため、現状ではごく一部再利用されるものを除き、大部分は産業廃棄物である「汚泥」として中間処理施設で脱水処理を行ない、あるいは直接最終処分場に持ち込まれている。しかし、脱水作業は水処理施設も含めて多大な設備と費用を要し、また作業には広い面積の土地が必要である。このため、建設汚泥を脱水作業をしないで処理してリサイクルに供することができる簡易な方法が望まれていた。
また、浄水場にて浄水処理の過程で発生する発生土(高含水泥土)も同様である。
【0005】
本発明は、建設汚泥、浄水汚泥等のような高含水比の土を処理して他の有効な用途に供することができるリサイクル方法を提供することを目的としている。
【0006】
【課題を解決するための手段】
請求項1に記載された植栽土壌の製造方法は、高含水比の汚泥に1cm四方以下で厚さ0.1mm以下の古紙とアクリル系ポリマーを添加して機械的剪断応力を加えることにより前記汚泥に動圧と回転運動を与えて空隙率を低下させ、土粒子間の距離を短くして土粒子間結合力の増大による粘りを発生させて内部に水分を閉じ込めた状態で前記汚泥を団粒化することを特徴としている。
【0007】
請求項2に記載された植栽土壌は、高含水比の汚泥に1cm四方以下で厚さ0.1mm以下の古紙とアクリル系ポリマーを添加して機械的剪断応力を加えることにより前記汚泥に動圧と回転運動を与えて空隙率を低下させ、土粒子間の距離を短くして土粒子間結合力の増大による粘りを発生させて内部に水分を閉じ込めた状態で前記汚泥を団粒化させたものである。
【0008】
【発明の実施の形態】
本発明に係る植栽土壌の製造方法を説明する。
建設汚泥を貯泥槽に投入する。貯泥槽内に繊維状物質としての新聞紙古紙片等を投入して撹拌する。新聞紙古紙片は汚泥中の自由水を吸水する。貯泥槽内に高分子凝集材を添加して撹拌する。
水溶性高分子が泥土の粒子表面の吸着水と反応するとともに架橋作用により粒子が結合する。
次に機械的せん断応力を加えると団粒状態となる。
【0009】
前述した例において使用した高分子改良材としては、従来より土壌改良材として知られているポリアクリル酸、ポリアクリル酸塩、ポリアクリル酸エステル、ポリアクリルアミド、それらの組み合せによるコポリマーや、それらのポリアルキレングリコールや無水マレイン酸、エポキシ化合物等とのコポリマー等の各種のものが考慮されるが、なかでも水溶性のポリマーが好適なものとして挙げられる。例えば、主成分をポリアクリル系ポリマーとする合成水溶性ポリマー粉末(PH7〜8、水分10±2%、嵩比重0.6〜0.7、真比重1.4〜1.5)などが使用できる。これらの高分子改良材については、対象土1m3 に対して1kg以上の割合で添加するのが望ましい。
【0010】
また、繊維状物質としては、前述した新聞紙の古紙等の他、天然又は合成の各種のものが使用できる。これらの繊維状物質については、その形状は細片状、小片状、糸状、布状等の各種の形状であってよく、例えば古紙においては、1cm四方以下で厚さ0.1mm以下のものとして添加することができる。添加量については、高分子系改良材の添加量との相乗効果が大きなものとなるように、対象土の種類、性質に応じて適宜実験的に定めることができる。例えば、その添加量は対象土1m3 に対して、古紙の場合は望ましくは30kgから90kg程度とすることが目安として考慮される。さらに、高含水汚泥の場合は、100kg以上が必要である。
【0011】
前記工程において、土に繊維状物質と高分子系改良材を添加した後に、撹拌するなどの手段で土に機械的剪断応力を加えると、前述したように土は団粒化するが、その際土の特性は破壊しにくくねばり強くなる方向に制御されている。
一般に一軸圧縮強度が高い改良土に撹拌のような機械的剪断応力を加えると砕石状になる。また、一軸圧縮強度が低い改良土の場合にはペースト状になる。
このように改良土を団粒化することは従来は困難なこととされていた。
しかし、本発明では、繊維状物質と高分子系改良材の添加といった操作を行なうことによって適度な圧縮強度と大きな破壊ひずみを得ることができる。そして、機械的剪断応力による動圧と回転運動を与えると、大きな圧縮ひずみ応力を有する処理土は、その空隙率を低下させる。すなわち、空隙率の低下は、処理土を構成する粒子間の距離が短くなることを意味する。その結果、粒子間結合力増大による粘りが発生して団粒化を可能にするのである。
【0012】
従来、建設汚泥に固化材を加える固化処理が知られていたが、この方法では固化した汚泥を破砕、ときほぐしする必要があったが、本例で得られた土は、はじめから団粒化しているので破砕、ときほぐしする必要がない。当然、従来の建設汚泥のようにプレスで水分を抜く必要もない。この状態でダンプトラックに積み込んで運び出すことができる。即ち、養生時間が不要となるために仮置場を必要としない。
【0013】
また、本例で得られた土は、保水性に優れており、植栽土壌として有用であるという特徴がある。
本例の土Aと、他の土B、Cを比較した。Bは法面緑化吹付工用の基盤材土である。Cは一般園芸用土である。各土の含水比はそれぞれ異なる。各土A〜Cの各々1リットルの塊を用意する。各土の塊をそれぞれ別々の貯槽の水中に所定時間浸漬した。水中から取り出した各土の塊の重量を測定すると、本例の土の塊は1.7kg、Bは1.3kg、Cは1.1kgであった。
【0014】
これら各土の塊を直射日光のあたらない屋外に放置し、その重量の日変化を測定した。結果を図1に示す。本例の土Aは、最も多くの水分を含んでおり、徐々に水分を蒸発させて一定の重量に落ち着いて水分の蒸発が略止まるまでに概ね30日の長期間を要した。この間に放出した水分の量は図1中に示すaで表される。これに比較し、土Bは水分の蒸発が止まるまでに約10日であり、この間に放出した水分の量は図1中に示すbであった。土Cは水分の蒸発が止まるまでに概ね5日であり、この間に放出した水分の量は図1中に示すcであった。図から明かなように、a>b、cである。
【0015】
このように本例の土によれば、他の土に比べて保水性が良好である。即ち、本例の土は保水量が多く、保水日数が長い。従って、この本例の土を植栽土壌に使用すれば、水遣り頻度が少なくても植物は適正に発芽し、成長することができる。この本例の土と、前記他の土をそれぞれ同量を鉢に入れて小松菜種を播種し、同様の条件で水遣りする実験を行なった。その結果、15日めでは本例の土土の全面に小松菜が成育したのに対し、他の例では全く発芽が見られなかった。
【0016】
このように、本例の土は、水分を内部に閉じ込めた状態で団粒化しているため、外部の水に接触しても溶けだしにくく、上記実験で貯槽の水中に浸漬しても貯槽中の水が濁ることはなかった。従って、本例の土を公園などの植栽土壌として使用しても、降雨時などに土が溶け出して環境を汚染するといった不都合が生じるおそれはない。
【0017】
さらに、以上説明したような本例の土の特性に鑑みれば、公園などに用いる単なる植栽土壌としてのみならず、法面緑化成育基盤材、屋上緑化成育基盤材に使用することができる。また、荒廃した自然や農耕地を回復させるために積極的に使用することもできる。例えば、火山活動などによって火山灰の泥流土で山林や農耕地が覆われた場合、この泥流土を前述した本発明の方法で処理して保水性の良好な団粒化した土とすれば、降雨などによる流出のおそれがなく、また高い保水性によって植生の回復も円滑に進むことが期待できる。また、本発明は、沖縄などで問題となっている赤水問題、即ち山の赤土が雨水とともに海に流れ込んで当該海域を汚染する問題に対する対策としても効果がある。
【0018】
【発明の効果】
本発明に係る植栽土壌及びその製造方法によれば、建設汚泥などに繊維状物質と高分子系改良材を添加して撹拌することにより、土を団粒化させて保水性を向上させることができるので、従来産業廃棄物として高コストで処理しなければならなかった建設汚泥等を低いコストで広い有用な用途の植栽土壌としてリサイクルできるという効果が得られる。
【図面の簡単な説明】
【図1】本発明によって処理した土と他の土との保水性を比較した実験結果を示す図である。[0001]
BACKGROUND OF THE INVENTION
The present invention relates to a treated soil obtained by the same method as a method for modifying soil such as construction sludge. The treated soil obtained by this method is agglomerated and does not re-mud, so it has little impact on the environment, and because it has excellent water retention, it can be effectively used as planting soil. .
[0002]
[Prior art]
Soil is an aggregate of grains with relatively small particle size, mainly made by the weathering action of rocks. In soil engineering, “soil” contains all the materials that make up the ground. The size of the particles is wide, and the materials of the materials include various kinds from pure minerals to industrial waste. For example, construction sludge, dredged landfills modified with solidified materials such as sludge and cement deposited in rivers, lakes, canals, and sea areas with high organic matter content are included. Therefore, its behavior is extremely complex and varied.
[0003]
Even in the soil described above, construction sludge exhibits a high water content, and the soil originally forming the ground often becomes mud in the course of construction work, and examples containing harmful substances are extremely rare.
[0004]
[Problems to be solved by the invention]
Construction sludge is excavation sludge or fine mud soil that is generated during construction work, and cannot be directly used for embankment. For this reason, with the exception of what is currently being partially reused, most of it is dewatered at intermediate treatment facilities as “sludge”, which is industrial waste, or directly brought to the final disposal site. However, dewatering work requires a large amount of equipment and costs including water treatment facilities, and work requires a large area of land. For this reason, there has been a demand for a simple method capable of treating construction sludge without dehydration and recycling it.
The same applies to the generated soil (high water content mud) generated in the process of water purification at the water purification plant.
[0005]
An object of this invention is to provide the recycling method which can process the soil of high moisture content like construction sludge, purified water sludge, etc., and can use it for another effective use.
[0006]
[Means for Solving the Problems]
The method for producing a planting soil according to claim 1 is characterized by adding a mechanical shear stress by adding waste paper and acrylic polymer having a thickness of 0.1 mm or less and a thickness of 0.1 cm or less to sludge having a high water content ratio. Applying dynamic pressure and rotational motion to the sludge to lower the porosity, shortening the distance between the soil particles, generating stickiness due to the increase in the bonding force between the soil particles, and consolidating the sludge in a state where moisture is confined inside It is characterized by granulation.
[0007]
The planting soil described in claim 2 is moved to the sludge by adding mechanical shear stress by adding waste paper and acrylic polymer having a thickness of 0.1 cm or less and a thickness of 0.1 mm or less to sludge having a high water content ratio. Applying pressure and rotational motion to lower the porosity, shortening the distance between the soil particles, generating stickiness due to the increase in the bonding force between the soil particles and aggregating the sludge in a state where moisture is confined inside It is a thing.
[0008]
DETAILED DESCRIPTION OF THE INVENTION
The manufacturing method of the planting soil which concerns on this invention is demonstrated.
Put construction sludge into the storage tank. A piece of waste paper as fibrous material is put into the mud storage tank and stirred. Used newspaper wastepaper absorbs free water in the sludge. Add polymer agglomerate into the mud storage tank and stir.
The water-soluble polymer reacts with the adsorbed water on the surface of the mud particles, and the particles are bonded by the crosslinking action.
Next, when a mechanical shear stress is applied, a aggregated state is obtained.
[0009]
Examples of the polymer improver used in the above-described examples include polyacrylic acid, polyacrylate, polyacrylate ester, polyacrylamide, a copolymer obtained by a combination thereof, and polyacrylic acid, which are conventionally known as soil improvers. Various types such as alkylene glycol, maleic anhydride, a copolymer with an epoxy compound and the like are considered, and water-soluble polymers are particularly preferable. For example, synthetic water-soluble polymer powder (PH7-8,
[0010]
Further, as the fibrous material, various kinds of natural or synthetic materials can be used in addition to the above-mentioned used newspaper paper. About these fibrous substances, the shape may be various shapes such as a strip shape, a small piece shape, a thread shape and a cloth shape. Can be added as The amount added can be appropriately determined experimentally according to the type and properties of the target soil so that the synergistic effect with the amount added of the polymer-based improving material becomes large. For example, the amount added is preferably about 30 kg to 90 kg in the case of waste paper with respect to 1 m 3 of the target soil. Furthermore, in the case of a high water content sludge, 100 kg or more is required.
[0011]
In the above process, when a mechanical shear stress is applied to the soil by means such as stirring after adding the fibrous substance and the polymer-based improving material to the soil, the soil aggregates as described above. The characteristics of the soil are controlled in such a way that they are hard to break and sticky.
In general, when a mechanical shear stress such as agitation is applied to improved soil having a high uniaxial compressive strength, it becomes crushed. In the case of improved soil with low uniaxial compressive strength, it becomes a paste.
Thus, it has been considered difficult to aggregate the improved soil.
However, in the present invention, an appropriate compressive strength and a large fracture strain can be obtained by performing an operation such as adding a fibrous substance and a polymer-based improving material. And if the dynamic pressure and rotational motion by a mechanical shear stress are given, the process soil which has a big compressive-strain stress will reduce the porosity. That is, the decrease in the porosity means that the distance between the particles constituting the treated soil is shortened. As a result, the stickiness due to the increase in the bonding force between the particles is generated and the agglomeration becomes possible.
[0012]
Conventionally, a solidification process in which a solidification material is added to construction sludge has been known, but this method required crushing and occasionally loosening the solidified sludge, but the soil obtained in this example was aggregated from the beginning. Because there is no need to crush and loosen. Of course, it is not necessary to remove moisture with a press unlike conventional construction sludge. In this state, it can be loaded onto a dump truck and taken out. In other words, since no curing time is required, no temporary storage is required.
[0013]
In addition, the soil obtained in this example is excellent in water retention and is useful as planting soil.
The soil A of this example was compared with the other soils B and C. B is a base material soil for slope greening spraying. C is general gardening soil. The water content of each soil is different. Prepare a litter lump for each soil A-C. Each lump of soil was immersed in the water of a separate storage tank for a predetermined time. When the weight of each soil lump taken out from the water was measured, the soil lump of this example was 1.7 kg, B was 1.3 kg, and C was 1.1 kg.
[0014]
These soil clumps were left outdoors where they were not exposed to direct sunlight, and their daily changes in weight were measured. The results are shown in FIG. The soil A of this example contained the most water, and it took a long period of about 30 days for the water to gradually evaporate and settle down to a constant weight, and the evaporation of the water almost stopped. The amount of moisture released during this period is represented by a shown in FIG. In comparison, soil B had approximately 10 days before the evaporation of water stopped, and the amount of water released during this period was b shown in FIG. Soil C was approximately 5 days before the evaporation of moisture stopped, and the amount of moisture released during this period was c shown in FIG. As is clear from the figure, a> b, c.
[0015]
Thus, according to the soil of this example, the water retention is better than other soils. That is, the soil of this example has a large amount of water retention and a long water retention period. Therefore, if the soil of this example is used as planting soil, the plant can germinate and grow properly even if watering frequency is low. An experiment was conducted in which the same amount of the soil of this example and the other soil were placed in a pot, seeded with Komatsu rapeseed, and watered under the same conditions. As a result, on the 15th day, Komatsuna grew on the entire surface of the soil of this example, whereas in other examples no germination was observed.
[0016]
Thus, since the soil of this example is agglomerated in a state where moisture is confined inside, it is difficult to melt even if it contacts external water, and even if immersed in the water of the storage tank in the above experiment, The water did not become cloudy. Therefore, even if the soil of this example is used as planting soil in a park or the like, there is no risk that the soil will melt and contaminate the environment when it rains.
[0017]
Furthermore, in view of the characteristics of the soil of this example as described above, it can be used not only as a planting soil used in parks and the like, but also as a slope greening base material and a rooftop greening base material. It can also be used actively to restore devastated nature and farmland. For example, when a forest or cultivated land is covered with a mud flow of volcanic ash due to volcanic activity, etc. In addition, there is no risk of runoff due to rainfall, etc., and vegetation recovery can be expected to proceed smoothly due to high water retention. The present invention is also effective as a countermeasure against the red water problem that is a problem in Okinawa and the like, that is, the problem that the red soil of the mountain flows into the sea together with rainwater and pollutes the sea area.
[0018]
【The invention's effect】
According to the planting soil and the method for producing the same according to the present invention, by adding a fibrous substance and a polymer-based improving material to construction sludge and stirring, the soil is agglomerated and water retention is improved. Therefore, it is possible to recycle the construction sludge, which has been conventionally treated as an industrial waste at a high cost, as planting soil for a wide range of useful uses at a low cost.
[Brief description of the drawings]
FIG. 1 is a diagram showing experimental results comparing water retention between soil treated according to the present invention and other soil.
Claims (2)
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP2000330757A JP3828737B2 (en) | 2000-10-30 | 2000-10-30 | Planting soil and its manufacturing method |
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| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP2000330757A JP3828737B2 (en) | 2000-10-30 | 2000-10-30 | Planting soil and its manufacturing method |
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| Publication Number | Publication Date |
|---|---|
| JP2002125459A JP2002125459A (en) | 2002-05-08 |
| JP3828737B2 true JP3828737B2 (en) | 2006-10-04 |
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| JP2000330757A Expired - Fee Related JP3828737B2 (en) | 2000-10-30 | 2000-10-30 | Planting soil and its manufacturing method |
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Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP2008187971A (en) * | 2007-02-06 | 2008-08-21 | Masahito Mori | Fibrous greening base material and method for producing the same |
Families Citing this family (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP2008133311A (en) * | 2006-11-27 | 2008-06-12 | Toyo Constr Co Ltd | Sediment improvement method and vegetation soil |
| KR101285326B1 (en) | 2011-09-27 | 2013-07-11 | 한국건설기술연구원 | Construction method for structure using wood chip |
| JP7270811B1 (en) | 2022-05-19 | 2023-05-10 | 雅人 森 | Method for manufacturing embankment body material and method for improving soil material |
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Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP2008187971A (en) * | 2007-02-06 | 2008-08-21 | Masahito Mori | Fibrous greening base material and method for producing the same |
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| JP2002125459A (en) | 2002-05-08 |
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