JP2724546B2 - Greening artificial soil layer for ground - Google Patents

Greening artificial soil layer for ground

Info

Publication number
JP2724546B2
JP2724546B2 JP7053630A JP5363095A JP2724546B2 JP 2724546 B2 JP2724546 B2 JP 2724546B2 JP 7053630 A JP7053630 A JP 7053630A JP 5363095 A JP5363095 A JP 5363095A JP 2724546 B2 JP2724546 B2 JP 2724546B2
Authority
JP
Japan
Prior art keywords
soil layer
soil
plant cultivation
coal ash
layer
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.)
Expired - Fee Related
Application number
JP7053630A
Other languages
Japanese (ja)
Other versions
JPH08214697A (en
Inventor
哲男 森
隆一郎 田坂
浩一 望月
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.)
Konoike Construction Co Ltd
Original Assignee
Konoike Construction Co Ltd
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 Konoike Construction Co Ltd filed Critical Konoike Construction Co Ltd
Priority to JP7053630A priority Critical patent/JP2724546B2/en
Publication of JPH08214697A publication Critical patent/JPH08214697A/en
Application granted granted Critical
Publication of JP2724546B2 publication Critical patent/JP2724546B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

Links

Description

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

【0001】[0001]

【産業上の利用分野】本発明は、サッカー場やゴルフ場
などのスポーツ施設、緑地、屋上庭園その他の緑化を目
的とした人工土層(本明細書において「グラウンド用緑
化人工土層」という。)に関するものである。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to an artificial soil layer for the purpose of greening sports facilities such as soccer fields and golf courses, green spaces, roof gardens and the like (hereinafter referred to as "greening artificial soil layer for grounds" in this specification). ).

【0002】[0002]

【従来の技術】従来、サッカー場やゴルフ場などのスポ
ーツ施設、緑地、屋上庭園その他の緑化を目的とした緑
化土層としては、排水性及び通気性のよい砂質土等の自
然土が用いられている。ところで、砂質土等の自然土か
らなる緑化土層の場合、夏期の高温乾燥時には土層中の
水分が不足するとともに高温となり、また、多雨時には
土層中の水分が過剰となり、芝等の植物の育成に問題が
生じることが多かった。これに対処するため、従来の緑
化土層の場合、緑化土層中に有孔管を埋設し、この有孔
管を介して強制的に換気及び給排水を行うようにするこ
とが提案されている。
2. Description of the Related Art Conventionally, natural soil such as sandy soil having good drainage and air permeability is used as a greening soil layer for the purpose of greening sports facilities such as soccer fields and golf courses, green spaces, roof gardens and the like. Have been. By the way, in the case of a green soil layer composed of natural soil such as sandy soil, the moisture in the soil layer becomes insufficient and high during summer high temperature drying, and the moisture in the soil layer becomes excessive during heavy rain, and Problems often arise in plant growth. In order to cope with this, in the case of the conventional green soil layer, it has been proposed to embed a perforated pipe in the green soil layer and to forcibly ventilate and supply / drain the water through the perforated pipe. .

【0003】[0003]

【発明が解決しようとする課題】しかしながら、従来の
緑化土層の場合、主として、換気及び給排水を行う設備
について開発研究がなされているに止まり、緑化土層を
構成する土壌については、現地土が排水不良な粘性土の
場合、排水性及び通気性のよい砂質土による客土を行
い、必要に応じて、砂質土に各種の保水材や保肥材等の
土壌改良材を混合する(例えば、アメリカゴルフ協会の
サンドグリーン造成用土壌の仕様も所定の粒度分布を持
つ砂質土に、ピートモス等の保水材を混合して用いるこ
ととしている。)程度で、ほとんど考慮されていなかっ
た。このため、緑化土層を構成する土壌の性状によっ
て、同じ設備であっても、その効果が大きく異なり、植
物の育成にとって最も好適な状態を実現することが困難
であり、また、緑化土層を構成する土壌をむらなく植物
の育成に好適な状態に維持するためには、緑化土層に埋
設する有孔管の敷設ピッチを小さくする必要が生じるこ
と等により、設備の構築コスト及び維持コストが高くな
るという問題点を有していた。
However, in the case of the conventional green soil layer, development and research are mainly being conducted on facilities for ventilation and water supply and drainage. In the case of cohesive soil with poor drainage, use soil with good drainage and air permeability, and mix soil improvement materials such as various water retention materials and fertilizer with sandy soil if necessary ( For example, the specification of sand green for soil formation by the American Golf Association also uses a water-retaining material such as peat moss mixed with sandy soil having a predetermined particle size distribution), and is hardly considered. For this reason, even if it is the same equipment, the effect greatly differs depending on the properties of the soil constituting the greening soil layer, and it is difficult to realize the most suitable state for growing plants. In order to maintain the composed soil in a state suitable for growing plants evenly, it is necessary to reduce the pitch of the perforated pipes buried in the green soil layer. There was a problem of becoming high.

【0004】また、従来の緑化土層を構成する土壌に主
に用いられる砂質土は、次のような問題点を有してい
た。 (1) 植物を良好に生育させるためには、通気性及び排水
性を損なうことなく、保水性及び保肥性を有する良質の
土壌を必要とするが、このためには、良質の砂質土や土
壌改良材を必要とし、材料コスト、造成コストが高くな
る。 (2) 植物を良好に生育させるための良質の土壌を維持す
るためには、肥料の散布、雑草の除去が頻繁に必要とな
り、維持コストが高くなる。 (3) 土壌の構成材料の分離、移動による目詰まりや、踏
圧による固結が生じやすく、通気性及び排水性が低下す
る。なお、この傾向は、砂質土にピートモス、テンポロ
ン、高吸水性樹脂(WAP)等の有機系保水材を土壌改
良材として混合する場合や、丸い粒子形の砂質土を用い
る場合に特に顕著である。
[0004] The sandy soil mainly used for the soil constituting the conventional greening soil layer has the following problems. (1) In order for plants to grow well, good-quality soil having water retention and fertilizing properties is required without impairing air permeability and drainage. And soil improvement materials are required, which increases material costs and construction costs. (2) In order to maintain good-quality soil for growing plants well, it is necessary to frequently spray fertilizers and remove weeds, which increases maintenance costs. (3) Clogging due to the separation and movement of soil constituent materials and consolidation due to treading are likely to occur, resulting in poor ventilation and drainage. This tendency is particularly remarkable when an organic water-retaining material such as peat moss, temporon, or a highly water-absorbent resin (WAP) is mixed with the sandy soil as a soil improving material, or when a round particle-type sandy soil is used. It is.

【0005】本発明は、緑化土層を構成する土壌を植物
の育成に好適な状態に安定的に維持することが容易にで
き、設備の構築コスト及び維持コストが低廉で、かつ、
従来、緑化土層を構成する土壌に主に用いられていた砂
質土の有する問題点を解決し、植物を良好に生育させる
ことが可能な、石炭灰を主成分とする植物栽培土壌層を
有するグラウンド用緑化人工土層を提供することを目的
とする。
According to the present invention, the soil constituting the greening soil layer can be easily maintained stably in a state suitable for growing plants, the facility construction cost and the maintenance cost are low, and
Conventionally, a plant cultivation soil layer mainly composed of coal ash that solves the problems of the sandy soil that has been mainly used for the soil constituting the greening soil layer and can grow plants well. It is intended to provide a greening artificial soil layer for a ground having.

【0006】[0006]

【課題を解決するための手段】上記目的を達成するた
め、本発明のグラウンド用緑化人工土層は、粒径が75
〜850μmの範囲の単一径の石炭灰で構成した石炭灰
を主成分とする植物栽培土壌層を有し、植物栽培土壌層
の換気及び給排水を行う有孔管を配設したことを特徴と
する。
Means for Solving the Problems To achieve the above object, the artificial green soil layer for ground of the present invention has a particle size of 75%.
It has a plant cultivation soil layer mainly composed of coal ash composed of a single diameter coal ash in a range of 8850 μm, and is provided with a perforated pipe for ventilating and supplying / draining the plant cultivation soil layer. I do.

【0007】また、同じ目的を達成するため、本発明の
グラウンド用緑化人工土層は、粒径が5〜106μmの
石炭灰を10〜25重量パーセント、106〜425μ
mの石炭灰を25〜50重量パーセント、425〜20
00μmの石炭灰を30〜50重量パーセント含有した
石炭灰を主成分とする植物栽培土壌層を有し、植物栽培
土壌層の換気及び給排水を行う有孔管を配設したことを
特徴とする。
In order to achieve the same object, the artificial ground greening layer according to the present invention comprises coal ash having a particle size of 5 to 106 μm in an amount of 10 to 25% by weight, and 106 to 425 μm.
m of coal ash at 25-50 weight percent, 425-20
It has a plant cultivation soil layer mainly composed of coal ash containing 30 to 50% by weight of 00 μm coal ash, and is provided with perforated pipes for ventilating and supplying / draining the plant cultivation soil layer.

【0008】この場合において、植物栽培土壌層の下方
にフィルター排水層を形成し、換気及び給水を行う有孔
管を植物栽培土壌層に埋設し、排水を行う有孔管をフィ
ルター排水層に埋設することが望ましい。
In this case, a filter drainage layer is formed below the plant cultivation soil layer, a perforated pipe for ventilation and water supply is buried in the plant cultivation soil layer, and a perforated pipe for drainage is buried in the filter drainage layer. It is desirable to do.

【0009】[0009]

【作 用】本発明のグラウンド用緑化人工土層の植物栽
培土壌層の主成分である石炭灰は、多数の粒子内連通毛
管孔隙及び独立孔隙を有する多孔質体であるため、植物
栽培土壌を、粒子間の平均孔隙径が12〜132μmの
範囲となるように、粒径が75〜850μmの範囲の単
一径の石炭灰で構成したり、粒径が5〜106μmの石
炭灰を10〜25重量パーセント、106〜425μm
の石炭灰を25〜50重量パーセント、425〜200
0μmの石炭灰を30〜50重量パーセント含有した石
炭灰で構成する(石炭灰に特別な処理を施さず、単に粒
径を調整する)ことにより、適度の通気性及び排水性、
保水性及び保肥性並びに断熱性を有するとともに、ま
た、均等係数(加積通過率60%に相当する粒径を加積
通過率10%に相当する粒径で割った値)が、アメリカ
ゴルフ協会の定めるサンドグリーン造成用土壌の粒度分
布から得られる均等係数などと比べて大きく、粒子形状
が角張って凹凸に富んでおり、さらに、物理的にも、ま
た化学的にも崩壊しにくいため、土壌の構成材料の分
離、移動による目詰まりや、踏圧による固結が生じにく
く、通気性及び排水性が低下することがないという特性
を有している。このため、緑化土層を構成する土壌を植
物の育成に好適な状態に安定的に維持することが容易に
できるとともに、植物栽培土壌層の換気及び給排水を行
う有孔管の敷設ピッチを従来より大きく設定することが
可能となること等により、設備の構築コスト及び維持コ
ストを低廉にすることができる。
[Operation] Coal ash, which is a main component of the plant cultivation soil layer of the greening artificial soil layer for the ground of the present invention, is a porous body having a large number of intraparticle communicating capillary pores and independent pores. A coal ash having a single diameter in a range of 75 to 850 μm, or a coal ash having a particle diameter of 5 to 106 μm in a range of 10 to 132 μm so that the average pore diameter between the particles is in a range of 12 to 132 μm. 25 weight percent, 106-425 μm
25-50 weight percent of coal ash, 425-200
By comprising coal ash containing 30 to 50% by weight of 0 μm coal ash (the coal ash is not subjected to any special treatment and simply adjusted in particle size), it has an appropriate air permeability and drainage property,
It has water retention, fertilizer retention, and heat insulation properties, and has an equality coefficient (a value obtained by dividing a particle diameter corresponding to a cumulative passing rate of 60% by a particle diameter corresponding to a cumulative passing rate of 10%). Larger than the uniformity coefficient obtained from the particle size distribution of sand green construction soil determined by the association, the particle shape is angular and rich in irregularities, and furthermore, it is difficult to physically and chemically collapse, Clogging due to separation and movement of the constituent materials of the soil, and consolidation due to treading are unlikely to occur, and the air permeability and drainage properties are not reduced. For this reason, it is easy to stably maintain the soil constituting the greening soil layer in a state suitable for growing plants, and the laying pitch of perforated pipes for ventilating and supplying / draining the plant cultivation soil layer has been increased compared to the past. By making it possible to set a large value, the construction cost and maintenance cost of the equipment can be reduced.

【0010】[0010]

【実施例】以下、本発明のグラウンド用緑化人工土層を
図示の実施例に基づいて説明する。本発明のグラウンド
用緑化人工土層の植物栽培土壌層に使用する石炭灰は、
従来廃棄処理していた火力発電所、その他の事業所より
産出される産業廃棄物であり、図1(a)に模式的に示
すように、石炭灰1の粒子内に多数の粒子内連通毛管孔
隙1b及び独立孔隙1cを有する多孔質体からなり、こ
のような粒子内連通毛管孔隙及び独立孔隙を有していな
い、図1(b)に模式的に示す砂質土2(非多孔質体)
とは、異なる基本構造を有している。
BRIEF DESCRIPTION OF THE DRAWINGS FIG. 1 is a perspective view showing an artificial soil layer for greening according to the present invention. Coal ash used for the plant cultivation soil layer of the greening artificial soil layer for the ground of the present invention,
This is industrial waste produced from thermal power plants and other business sites that have been conventionally disposed of, and as shown schematically in FIG. 1 (a), a large number of intra-particle communication capillaries within the particles of coal ash 1. The sandy soil 2 (non-porous material) which is composed of a porous material having pores 1b and independent pores 1c and which does not have such intraparticle communicating capillary pores and independent pores, is schematically shown in FIG. )
Has a different basic structure.

【0011】ところで、一般に植物を生育させる土壌の
機能についていえば、図3に示すように、その土壌を構
成する構成材料の粒径によりその排水性、通気性、保水
性、保肥性等の機能が変化する。通気性及び排水性は粒
径が小さいほどその機能が低下し、粒径が大きいほどそ
の機能が向上する。反対に保水性及び保肥性は粒径が小
さいほどその機能が向上し、大きいほどその機能が低下
する。
In general, regarding the function of soil for growing plants, as shown in FIG. 3, depending on the particle size of the constituent materials constituting the soil, its drainage, air permeability, water retention, fertilization, etc. Function changes. The function of the air permeability and the drainage property decreases as the particle size decreases, and the function improves as the particle size increases. Conversely, the smaller the particle size, the better the function of water retention and fertilization, and the smaller the particle size, the lower the function.

【0012】そして、通気性、排水性、保水性、保肥性
等の土壌の機能のうち通気性及び排水性に関しては、降
雨や灌水後の重力水(非有効水)は、石炭灰1からなる
土壌も、砂質土2からなる土壌も、粒子間の孔隙(非毛
管孔隙)1a,2aを通し排出され、通気性が確保され
る。
[0012] Among the soil functions such as breathability, drainage, water retention, and fertilization, regarding the permeability and drainage, gravity water (ineffective water) after rainfall or irrigation is produced from coal ash 1. Both the soil and the sandy soil 2 are discharged through the pores (non-capillary pores) 1a and 2a between the particles, and the air permeability is secured.

【0013】しかし、保水性及び保肥性に関しては、石
炭灰1の場合は、粒子内に外部と連続した連通毛管孔隙
1bを有するため、重力水が排除された後もこの中に毛
管水として植物根が吸収可能な水分(有効水)が貯留さ
れるのに対し、砂質土2の場合は、粒子間にわずかの水
分が貯留されるのみで、有効水が少なく保水性に乏し
い。
However, with regard to water retention and fertilization, in the case of coal ash 1, since the particles have the communicating capillary pores 1b connected to the outside in the particles, even after gravity water is removed, they remain as capillary water. While water (effective water) that can be absorbed by plant roots is stored, in the case of sandy soil 2, only a small amount of water is stored between particles and effective water is small and water retention is poor.

【0014】なお、保水性を高めるために、砂質土に、
ピートモス等の保水材を混合して用いると、図2に示す
ように、砂質土2の粒子間の孔隙2aが保水材3により
塞がれ、排水性及び通気性が阻害されるという欠点があ
る。また、粘性土のように粒径がきわめて小さい場合、
土壌の孔隙率は大きく土壌水は多量に存在するが、その
孔隙が微細なため土壌と強く結合し植物根が吸収不可能
な拘束水の割合が多く、孔隙中に存在する有効水が占め
る割合はさほど多くなく、また、非毛管孔隙が少なく排
水性が劣るため、重力水が速やかに排除されず、通気性
が悪く植物が生育しにくく、さらに、粒子間の孔隙径が
小さいため植物根が通過・貫入できず、生長が阻害され
るという欠点を有している。また、有機物が多く微生物
や小動物の活動が活発で、肥沃な畑地土壌などでは、団
粒構造が発達して排水性及び通気性並びに保水性及び保
肥性に富み、植物生育に適した土壌(団粒土)である
が、団粒土の生成のためには良質な有機物の長年の投与
と、頻繁な耕起を必要とし、また踏圧などによって団粒
構造が破壊される欠点を有している。
In order to increase water retention, sandy soil
When a water retention material such as peat moss is mixed and used, as shown in FIG. 2, the pores 2 a between the particles of the sandy soil 2 are closed by the water retention material 3, and the drainage and air permeability are impaired. is there. Also, when the particle size is extremely small, such as in cohesive soil,
The porosity of the soil is large and a large amount of soil water is present, but the pores are so fine that they bind strongly to the soil and the proportion of confined water that cannot be absorbed by plant roots is large, and the proportion of available water in the pores Not so much, and non-capillary pores are small and drainage is inferior, gravity water is not quickly removed, poor ventilation and plant growth is difficult, and plant roots are small due to small pore size between particles. It has the drawback that it cannot pass and penetrate, and its growth is hindered. In addition, in the fertile field soil, which has a large amount of organic matter and active activities of microorganisms and small animals, the soil structure suitable for plant growth is rich in drainage and aeration, water retention and fertilization, and fertilizer structure is developed. Agglomerated soil), but it requires long-term administration of high-quality organic matter and frequent tillage to produce the aggregated soil, and has the disadvantage that the aggregate structure is destroyed by treading pressure etc. I have.

【0015】これに対して、石炭灰1は、粒子内連通毛
管孔隙1b、独立孔隙1c及び粒子内連通非毛管孔隙1
dを有する多孔質体であるのみならず、均等係数が大き
く、また、粒子形状が角張って凹凸に富んでおり、さら
に、粒子自体が強い構造を有し、物理的にも、化学的に
も崩壊しにくいことから、土壌の構成材料の分離、移動
による目詰まりや、踏圧による固結が生じにくく、通気
性及び排水性が低下せず、適度の通気性及び排水性、保
水性及び保肥性並びに断熱性を有するものである。図3
(a)に、粘土、まさ土、砂、多孔質体(石炭
灰)の各土壌の粒子の集合体の模式図を、同図(b)
に、上記各土壌の実際の孔隙構成を、同図(c)に、上
記各土壌の植物の育成に関連する諸機能をまとめて記載
する。
On the other hand, the coal ash 1 contains the intra-particle communicating capillary pores 1b, the independent pores 1c, and the intra-particle communicating non-capillary pores 1
Not only a porous body having d, but also a large uniformity coefficient, the particle shape is angular and rich in irregularities, and the particles themselves have a strong structure, physically and chemically. Because it is hard to collapse, clogging due to separation and movement of soil constituent materials and hardening due to treading hardly occur, air permeability and drainage does not decrease, moderate ventilation and drainage, water retention and fertilization It has properties and heat insulation. FIG.
(A) is a schematic diagram of an aggregate of particles of each soil of clay, Masato, sand, and a porous body (coal ash);
Next, the actual pore configuration of each of the above soils is shown, and in FIG. 3 (c), various functions related to plant growth in each of the above soils are collectively described.

【0016】以上、土壌の種類の違いによる粒子間の孔
隙及び粒子内の連通孔隙が、植物の生育の良否を決定す
る通気性、排水性、保水性、保肥性、断熱性という土壌
の植物の育成に関連する機能を決定する重要な因子とな
ることを説明したが、次に、土壌の種類と土壌の換気及
び給排水を行うために配設される有孔管との関連につい
て、図4〜図5を用いて説明する。
As described above, the pores between the particles and the communication pores within the particles due to the difference in the type of soil determine the quality of plant growth. It has been explained that it is an important factor that determines the function related to the growth of cultivation. Next, the relationship between the type of soil and the perforated pipes provided for ventilation and water supply and drainage of the soil is shown in FIG. This will be described with reference to FIG.

【0017】まず、土壌の換気性能については、図4に
示すように、多孔質体土壌(図4(a))は、粒子内連
通非毛管孔隙1dを有するとともに、粒子形状が角張っ
て凹凸に富んでおり、さらに、粒子自体が強い構造を有
し、物理的にも、化学的にも崩壊しにくいことから、非
多孔質体土壌(図4(b))と比較して、非毛管孔隙率
が高く、このため、土壌の水平方向及び垂直方向の換気
性能がよく、非多孔質体土壌の場合との比較において、
土壌の換気を行う有孔管の敷設ピッチを大きく設定する
とともに、有孔管の埋設深さを深く設定することが可能
となり、これにより、有孔管の破損を防止することがで
きるとともに、設備の構築コスト(ポンプ等の設備費、
有孔管の敷設等の工事費等)及び維持コスト(エネルギ
費、保守点検費等)を低廉にすることができる。
First, regarding the ventilation performance of the soil, as shown in FIG. 4, the porous soil (FIG. 4 (a)) has an intra-particle communicating non-capillary pore 1d, and the particle shape is angular and uneven. Is rich, and the particles themselves have a strong structure and are hard to physically or chemically disintegrate. Therefore, compared to the non-porous soil (FIG. 4B), the non-capillary pores The rate is high, therefore, the horizontal and vertical ventilation performance of the soil is good, compared with the case of non-porous soil,
In addition to setting a large pitch for laying perforated pipes that ventilate the soil, it is possible to set the burial depth of the perforated pipes deep, thereby preventing damage to the perforated pipes and Construction costs (equipment costs such as pumps,
Construction costs for laying perforated pipes, etc.) and maintenance costs (energy costs, maintenance and inspection costs, etc.) can be reduced.

【0018】次に、土壌の給水性能については、図5に
示すように、多孔質体土壌(図5(a))は、粒子内連
通毛管孔隙1bを有することから、非多孔質体土壌(図
4(b))と比較して、毛管孔隙率が高く、このため、
一般の散水(a−1、b−1)、人工土層上部からの給
水(a−2、b−2)、人工土層下部からの給水(a−
3、b−3)のいずれの場合においても、土壌の水平方
向及び垂直方向の給水性能がよく、非多孔質体土壌の場
合との比較において、土壌の給水を行う有孔管の敷設ピ
ッチを大きく設定することが可能となるともに、非多孔
質体土壌と比べ、毛管上昇高さが高いため、非多孔質体
土壌の場合との比較において、有孔管の埋設深さを深く
設定することが可能となり、これにより、有孔管の破損
を防止することができるとともに、設備の構築コスト
(ポンプ等の設備費、有孔管の敷設等の工事費等)及び
維持コスト(エネルギ費、保守点検費等)を低廉にする
ことができる。
Next, regarding the water supply performance of the soil, as shown in FIG. 5, the porous soil (FIG. 5 (a)) has the intracellular communicating capillary pores 1b, so that the non-porous soil ( As compared with FIG. 4 (b)), the capillary porosity is higher,
General watering (a-1, b-1), water supply from the upper part of the artificial soil layer (a-2, b-2), water supply from the lower part of the artificial soil layer (a-
3, b-3) In any case, the water supply performance in the horizontal and vertical directions of the soil is good, and in comparison with the case of the non-porous soil, the laying pitch of the perforated pipe for supplying the soil is reduced. In addition to being able to set large, the height of capillary rise is higher than that of non-porous soil, so it is necessary to set the burial depth of perforated pipe deeper compared to the case of non-porous soil. This makes it possible to prevent the perforated pipe from being damaged, and to construct the equipment (e.g., pump and other equipment costs, the cost of laying perforated pipes, etc.) and the maintenance costs (energy costs, maintenance, etc.). Inspection costs) can be reduced.

【0019】なお、多孔質体土壌は、粒子内独立孔隙1
cを有することから、非多孔質体土壌と比較して、断熱
性能がよく、非多孔質体土壌の場合との比較において、
夏期に有孔管から供給する冷風、冷水、冬季に有孔管か
ら供給する温風、温水の熱効率を向上することができ、
これにより、設備の維持コスト(エネルギ費)を低廉に
することができる。
Incidentally, the porous material soil is formed by independent pores 1 in the particles.
Since it has c, compared with the non-porous soil, the heat insulation performance is good, and in comparison with the case of the non-porous soil,
It is possible to improve the thermal efficiency of cold air and cold water supplied from perforated pipes in summer and hot air and hot water supplied from perforated pipes in winter,
Thereby, the maintenance cost (energy cost) of the equipment can be reduced.

【0020】次に、石炭灰を主成分とする植物栽培土壌
層を有する本発明のグラウンド用緑化人工土層を図6の
実施例に基づいて説明する。このグラウンド用緑化人工
土層は、石炭灰1を主成分とし、芝等の植生10を行う
植物栽培土壌層11を有し、この植物栽培土壌層11の
下方に砕石等から構成したフィルター排水層12を形成
し、植物栽培土壌層11及びフィルター排水層12の周
囲を合成樹脂シート等から構成した遮断層13により囲
うことにより、周囲地盤14との間の気体及び水分の移
動を防ぐようにしている。
Next, the ground greening artificial soil layer of the present invention having a plant cultivation soil layer mainly composed of coal ash will be described based on the embodiment of FIG. This artificial greening layer for grounding has a plant cultivation soil layer 11 mainly composed of coal ash 1 and vegetation 10 such as turf, and a filter drainage layer made of crushed stone or the like below the plant cultivation soil layer 11. 12 is formed, and the surroundings of the plant cultivation soil layer 11 and the filter drainage layer 12 are surrounded by a blocking layer 13 made of a synthetic resin sheet or the like, so that movement of gas and moisture between the soil layer 14 and the surrounding ground 14 is prevented. I have.

【0021】植物栽培土壌層11の底部近傍に、植物栽
培土壌層11の換気及び給水を行う有孔管15を埋設
し、フィルター排水層12の底部に、排水を行う有孔管
16を埋設する。また、植物栽培土壌層11の換気及び
給水を行う有孔管15には、有孔管15を介して植物栽
培土壌層11の換気及び給水を選択的に行うとともに、
換気を行う場合に、植物栽培土壌層11に供給する空気
を飽和状態に加湿するための制御装置17を連接する。
A perforated pipe 15 for ventilating and supplying water to the plant cultivation soil layer 11 is buried near the bottom of the plant cultivation soil layer 11, and a perforated pipe 16 for draining is buried at the bottom of the filter drainage layer 12. . In addition, the perforated pipe 15 for ventilating and supplying water to the plant cultivation soil layer 11 is selectively ventilated and supplied to the plant cultivation soil layer 11 through the perforated pipe 15.
When performing ventilation, the control device 17 for humidifying the air supplied to the plant cultivation soil layer 11 to a saturated state is connected.

【0022】この場合において、有孔管15から植物栽
培土壌層11中の空気を吸引することにより、植物栽培
土壌層11の換気を行うようにしたり、有孔管15を植
物栽培土壌層11の換気を行う有孔管と給水を行う有孔
管とに区分したり、有孔管15を省略し、有孔管16に
より植物栽培土壌層11の換気及び給水を行うようにす
ることができる。なお、有孔管16により植物栽培土壌
層11の換気及び給水を行う場合には、給水時の水位を
植物栽培土壌層11の位置まで上昇すればよく、この状
態で、有孔管16から空気を供給すれば、飽和状態に加
湿した空気を植物栽培土壌層11に供給し、換気を行う
ことができる。
In this case, the air in the plant cultivation soil layer 11 is sucked from the perforated pipe 15 so as to ventilate the plant cultivation soil layer 11, and the perforated pipe 15 is connected to the plant cultivation soil layer 11. It can be divided into a perforated pipe for ventilation and a perforated pipe for water supply, or the perforated pipe 15 can be omitted, and the perforated pipe 16 can be used for ventilation and water supply of the plant cultivation soil layer 11. In addition, when ventilation and water supply of the plant cultivation soil layer 11 are performed by the perforated pipe 16, the water level at the time of water supply may be raised to the position of the plant cultivation soil layer 11, and in this state, the air is supplied from the perforated pipe 16 to the air. Is supplied, air humidified to a saturated state can be supplied to the plant cultivation soil layer 11 to perform ventilation.

【0023】図7に、このグラウンド用緑化人工土層の
空気と水分の移動のプロセスを模式的に示す。図7
(a)に示す加湿状態の場合、余剰の水分は、石炭灰の
非毛管孔隙を通ってフィルター排水層12に埋設した有
孔管16に排水され、植物栽培土壌層11は、図7
(b)に示す植物の育成に好適な状態に維持される。図
7(c)に示す乾燥状態の場合、不足する水分は、有孔
管15から給水され、供給された水分は、石炭灰の毛管
孔隙に保持され、植物栽培土壌層11は、図7(b)に
示す植物の育成に好適な状態に維持される。また、有孔
管15から植物栽培土壌層11中に空気を供給したり、
植物栽培土壌層11中の空気を吸引し、植物栽培土壌層
11の換気を行うことにより、植物栽培土壌層11の二
酸化炭素等の植物の育成に有害な気体は、石炭灰の非毛
管孔隙を通って、前者の場合は地表面から放出され、後
者の場合は有孔管15から放出されることにより、植物
栽培土壌層11は、植物の育成に好適な状態に維持され
る。
FIG. 7 schematically shows a process of moving air and moisture in the artificial green soil layer for ground use. FIG.
In the case of the humidified state shown in (a), excess water is drained to the perforated pipe 16 embedded in the filter drainage layer 12 through the non-capillary pores of coal ash, and the plant cultivation soil layer 11
It is maintained in a state suitable for growing plants shown in (b). In the case of the dry state shown in FIG. 7 (c), the insufficient water is supplied from the perforated pipe 15, the supplied water is retained in the pores of the coal ash, and the plant cultivation soil layer 11 It is maintained in a state suitable for growing plants shown in b). In addition, air is supplied from the perforated pipe 15 into the plant cultivation soil layer 11,
By sucking air in the plant cultivation soil layer 11 and ventilating the plant cultivation soil layer 11, gases harmful to plant growth such as carbon dioxide in the plant cultivation soil layer 11 remove non-capillary pores of coal ash. As a result, the former is released from the ground surface in the former case, and the latter is released from the perforated pipe 15 in the latter case, so that the plant cultivation soil layer 11 is maintained in a state suitable for growing plants.

【0024】[0024]

【発明の効果】本発明によれば、粒径が75〜850μ
mの範囲の単一径の石炭灰又は粒径が5〜106μmの
石炭灰を10〜25重量パーセント、106〜425μ
mの石炭灰を25〜50重量パーセント、425〜20
00μmの石炭灰を30〜50重量パーセント含有した
石炭灰を主成分とする植物栽培土壌層と植物栽培土壌層
の換気及び給排水を行う有孔管とを組み合わせて用いる
ことにより、グランド用緑化人工土層を構成する植物栽
培土壌を植物の育成に好適な状態に安定的に容易に維持
することができるとともに、植物栽培土壌層の換気及び
給排水を行う有孔管の敷設ピッチを従来より大きく設定
することが可能となること等により、設備の構築コスト
及び維持コストを低廉にすることができる。また、本発
明のグランド用緑化人工土層を構成する植物栽培土壌層
は、従来廃棄処理していた火力発電所、その他の事業所
より産出する産業廃棄物である石炭灰を主成分として用
いるため、材料コスト及び造成コストを低廉にすること
ができ、また、産業廃棄物の有効利用の点でもきわめて
有益である。また、石炭灰は、多数の粒子内の連通孔隙
を有する多孔質体であるため、用いる石炭灰の粒径を調
整することにより、適度の通気性及び排水性、保水性及
び保肥性並びに断熱性を有し、植物を良好に生育させる
ことが可能な植物栽培土壌を提供することができる。ま
た、石炭灰は、均等係数が大きく、粒子形状が角張って
凹凸に富んでおり、さらに、物理的にも、また化学的に
も崩壊しにくいため、土壌の構成材料の分離、移動によ
る目詰まりや、踏圧による固結が生じにくく、通気性及
び排水性が低下することがない。そして、この植物栽培
土壌は、頻繁な肥料の散布を必要とせず、また、石炭灰
を構成材料として用いるため、雑草種子の混在がなく、
長期間雑草の除去を必要とせず、土壌を植物を良好に生
育させる状態に維持するためのコストを低廉にすること
ができ、さらに、適度な粗粒状態であるため表面付近を
乾燥状態に保つとともに、断熱作用によって地温を安定
化させ、これにより植物の生育を促進させることができ
るとともに、病害の発生を抑制することができる。この
ため、農薬の使用量を低減することができ、肥料の使用
量を低減することができることと合わせて周辺環境に対
する負荷を軽減し、また、産業廃棄物の有効利用の点も
含め、地球環境の改善に役立つものである。
According to the present invention, the particle size is 75 to 850 μm.
m in the range of 10 to 25 weight percent, 106 to 425 μm
m of coal ash at 25-50 weight percent, 425-20
By using a plant cultivation soil layer composed mainly of coal ash containing 30 to 50% by weight of 00 μm coal ash and a perforated pipe for ventilating and supplying / draining the plant cultivation soil layer, an artificial greening soil for ground is used. The plant cultivation soil constituting the layer can be stably and easily maintained in a state suitable for growing plants, and the pitch of the perforated pipes for ventilating and supplying / draining the plant cultivation soil layer is set to be larger than before. This makes it possible to reduce equipment construction costs and maintenance costs. In addition, the plant cultivation soil layer constituting the ground greening artificial soil layer of the present invention uses coal ash, which is industrial waste produced from thermal power plants and other business sites that have conventionally been disposed of, as a main component. In addition, it is possible to reduce material costs and construction costs, and it is extremely advantageous in terms of effective use of industrial waste. In addition, since coal ash is a porous body having communication pores in a large number of particles, by adjusting the particle size of the coal ash to be used, appropriate air permeability and drainage, water retention and fertilization, and heat insulation are provided. It is possible to provide a plant cultivation soil having a property and capable of favorably growing plants. In addition, coal ash has a large uniformity coefficient, has a sharp and irregular particle shape, and is hard to physically or chemically disintegrate. Also, consolidation due to treading is unlikely to occur, and there is no reduction in air permeability and drainage. And this plant cultivation soil does not require frequent application of fertilizers, and because coal ash is used as a constituent material, there is no weed seed mixture,
No need to remove weeds for a long period of time, the cost of maintaining the soil in a state where plants can grow well can be reduced, and the surface near the surface is kept dry because it is in a moderately coarse state At the same time, the ground temperature is stabilized by the heat insulating effect, whereby the growth of plants can be promoted and the occurrence of diseases can be suppressed. For this reason, the use of pesticides can be reduced, the use of fertilizers can be reduced, and the burden on the surrounding environment is also reduced. It will help to improve.

【0025】また、換気及び給水を行う有孔管を植物栽
培土壌層に埋設し、排水を行う有孔管をフィルター排水
層に埋設することにより、植物栽培土壌層の換気及び給
排水を良好に行うことができる。
In addition, by burying a perforated pipe for ventilation and water supply in the plant cultivation soil layer and burying a perforated pipe for drainage in the filter drainage layer, the ventilation and water supply and drainage of the plant cultivation soil layer can be satisfactorily performed. be able to.

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

【図1】(a)石炭灰(多孔質体)及び(b)砂質土
(非多孔質体)を示す模式図である。
FIG. 1 is a schematic diagram showing (a) coal ash (porous body) and (b) sandy soil (non-porous body).

【図2】保水材を混合した状態の砂質土(非多孔質体)
を示す模式図である。
Fig. 2 Sandy soil (non-porous material) mixed with water retention material
FIG.

【図3】(a)各種土壌の粒子の集合体の模式図、
(b)各種土壌の孔隙構成及び(c)各種土壌の植物の
育成に関連する諸機能を示す図である。
FIG. 3 (a) is a schematic diagram of an aggregate of particles of various soils,
It is a figure which shows the pore structure of (b) various soils, and (c) the various functions relevant to the plant growth of various soils.

【図4】土壌の換気性能を示す図である。FIG. 4 is a diagram showing ventilation performance of soil.

【図5】土壌の給水性能を示す図である。FIG. 5 is a view showing water supply performance of soil.

【図6】本発明のグラウンド用緑化人工土層の1実施例
を示す図である。
FIG. 6 is a view showing an embodiment of a greening artificial soil layer for a ground according to the present invention.

【図7】本発明のグラウンド用緑化人工土層の空気と水
分の移動のプロセスを示す模式図である。
FIG. 7 is a schematic view showing a process of moving air and moisture in the artificial green soil layer for grounding according to the present invention.

【符号の説明】 1 石炭灰(多孔質体の模式図) 1a 粒子間の孔隙(非毛管孔隙) 1b 粒子内の連通毛管孔隙 1c 粒子内の独立孔隙 1d 粒子内の連通非毛管孔隙 2 砂質土(非多孔質体の模式図) 2a 粒子間の孔隙(非毛管孔隙) 10 植生 11 植物栽培土壌層 12 フィルター排水層 13 遮断層 14 周囲地盤 15 有孔管 16 有孔管[Explanation of Symbols] 1 Coal ash (schematic diagram of porous body) 1a Pores between particles (non-capillary pores) 1b Communicating capillary pores in particles 1c Independent pores in particles 1d Communicating non-capillary pores in particles 2 Sandy Soil (schematic diagram of non-porous material) 2a Pores between particles (non-capillary pores) 10 Vegetation 11 Plant growing soil layer 12 Filter drainage layer 13 Blocking layer 14 Surrounding ground 15 Perforated pipe 16 Perforated pipe

───────────────────────────────────────────────────── フロントページの続き (51)Int.Cl.6 識別記号 庁内整理番号 FI 技術表示箇所 A01G 25/06 602 A01G 25/06 602 E02B 11/00 E02B 11/00 Z ──────────────────────────────────────────────────続 き Continued on the front page (51) Int.Cl. 6 Identification code Agency reference number FI Technical display location A01G 25/06 602 A01G 25/06 602 E02B 11/00 E02B 11/00 Z

Claims (3)

(57)【特許請求の範囲】(57) [Claims] 【請求項1】 粒径が75〜850μmの範囲の単一径
の石炭灰で構成した石炭灰を主成分とする植物栽培土壌
層を有し、植物栽培土壌層の換気及び給排水を行う有孔
管を配設したことを特徴とするグラウンド用緑化人工土
層。
1. A perforated plant cultivation soil layer mainly composed of coal ash composed of a single diameter coal ash having a particle size in the range of 75 to 850 μm, for ventilating and supplying / draining the plant cultivation soil layer. A greening artificial soil layer for the ground, which is provided with pipes.
【請求項2】 粒径が5〜106μmの石炭灰を10〜
25重量パーセント、106〜425μmの石炭灰を2
5〜50重量パーセント、425〜2000μmの石炭
灰を30〜50重量パーセント含有した石炭灰を主成分
とする植物栽培土壌層を有し、植物栽培土壌層の換気及
び給排水を行う有孔管を配設したことを特徴とするグラ
ウンド用緑化人工土層。
2. Coal ash having a particle size of 5 to 106 μm is
25 weight percent, 106-425 μm coal ash
It has a plant cultivation soil layer mainly composed of coal ash containing 5 to 50% by weight and 30 to 50% by weight of 425 to 2000 μm coal ash, and has a perforated pipe for ventilating and supplying / draining the plant cultivation soil layer. A greening artificial soil layer for the ground, which was established.
【請求項3】 植物栽培土壌層の下方にフィルター排水
層を形成し、換気及び給水を行う有孔管を植物栽培土壌
層に埋設し、排水を行う有孔管をフィルター排水層に埋
設したことを特徴とする請求項1又は2記載のグラウン
ド用緑化人工土層。
3. A filter drainage layer is formed below the plant cultivation soil layer, a perforated pipe for ventilation and water supply is buried in the plant cultivation soil layer, and a perforated pipe for drainage is buried in the filter drainage layer. The artificial green soil layer for ground according to claim 1 or 2, characterized in that:
JP7053630A 1995-02-17 1995-02-17 Greening artificial soil layer for ground Expired - Fee Related JP2724546B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP7053630A JP2724546B2 (en) 1995-02-17 1995-02-17 Greening artificial soil layer for ground

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP7053630A JP2724546B2 (en) 1995-02-17 1995-02-17 Greening artificial soil layer for ground

Publications (2)

Publication Number Publication Date
JPH08214697A JPH08214697A (en) 1996-08-27
JP2724546B2 true JP2724546B2 (en) 1998-03-09

Family

ID=12948234

Family Applications (1)

Application Number Title Priority Date Filing Date
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Country Link
JP (1) JP2724546B2 (en)

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CN102783346A (en) * 2012-08-23 2012-11-21 天津市津美园林工程有限公司 Method for treating lawn pelade
KR101644630B1 (en) * 2015-11-03 2016-08-10 정필호 Agricultural Air injection apparatus

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