JP2002272261A - Greening base - Google Patents

Greening base

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Publication number
JP2002272261A
JP2002272261A JP2001085433A JP2001085433A JP2002272261A JP 2002272261 A JP2002272261 A JP 2002272261A JP 2001085433 A JP2001085433 A JP 2001085433A JP 2001085433 A JP2001085433 A JP 2001085433A JP 2002272261 A JP2002272261 A JP 2002272261A
Authority
JP
Japan
Prior art keywords
soil
greening base
inorganic porous
greening
porous body
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.)
Pending
Application number
JP2001085433A
Other languages
Japanese (ja)
Inventor
Takeshi Oguri
健 小栗
Yasumasa Masu
泰将 桝
Nami Matsumoto
奈弥 松本
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.)
Inax Corp
Original Assignee
Inax Corp
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 Inax Corp filed Critical Inax Corp
Priority to JP2001085433A priority Critical patent/JP2002272261A/en
Publication of JP2002272261A publication Critical patent/JP2002272261A/en
Pending legal-status Critical Current

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Abstract

PROBLEM TO BE SOLVED: To obtain a greening base capable of sufficiently growing a plant and having a water purification function. SOLUTION: This greening base is obtained by mixing granular inorganic porous bodies with glass powder followed by baking and binding the granular inorganic porous bodies with each other with melted and solidified glass; wherein if the inorganic porous body has an ion exchange ability, water can be purified through passing water into the greening base since nitrogen (N) and phosphorus (P) components can be removed, and the greening base is made combined through setting a soil-holding layer on the top of the greening base and stuffing or depositing soil containing an organic binder in/on the soil-holding layer.

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】本発明は、植物を植栽するた
めの緑化基盤に係り、特に傾斜した屋根にも配置するこ
とができる緑化基盤に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a greening base for planting plants, and more particularly to a greening base that can be arranged on an inclined roof.

【0002】[0002]

【従来の技術】屋根の断熱や装飾等のために、屋根に植
栽を施すことが普及しつつある。このような屋根緑化用
のパネルとして、特開平6−141670号には、「セ
ラミック等の硬材からなる、直径1〜2mm程度の空隙
を有したパネル状の多孔質体の該空隙に培養土及び保水
材を混入させた緑化資材」が記載されている。
2. Description of the Related Art Planting a roof is widely used for heat insulation and decoration of the roof. As such a panel for roof greening, Japanese Patent Application Laid-Open No. 6-141670 discloses "a panel-shaped porous body made of a hard material such as ceramic and having a gap of about 1 to 2 mm in diameter. And a greening material mixed with a water retention material ”.

【0003】[0003]

【発明が解決しようとする課題】上記特開平6−141
670号には、上記の「セラミック等の硬材からなる多
孔質体」について「空隙が全体に渡って連続しているも
の」とのみ記述されており、それ以上の具体的記述はな
く、植物を確実に成育させるための構成は示されていな
い。
SUMMARY OF THE INVENTION The above-mentioned Japanese Patent Laid-Open No. 6-141 is disclosed.
No. 670 describes only the "porous body made of a hard material such as ceramic" described above as "a porous body continuous throughout the whole body", and there is no further specific description. No configuration is shown for ensuring the growth of E. coli.

【0004】本発明は、植物を十分に成育させることが
できる緑化基盤を提供することを目的とする。
[0004] An object of the present invention is to provide a greening base on which plants can be grown sufficiently.

【0005】また、本発明は、水浄化機能を有した緑化
基盤を提供することを目的とする。
Another object of the present invention is to provide a greening base having a water purification function.

【0006】[0006]

【課題を解決するための手段】本発明の緑化基盤は粒状
の無機多孔体を盤状に成形し固化させてなるものであ
る。
The greening substrate of the present invention is obtained by forming a granular inorganic porous body into a disk shape and solidifying it.

【0007】この緑化基盤は、粒状の無機多孔体とガラ
ス粉とを混合して焼成し、熔融して固化したガラスによ
って粒状無機多孔体同士を結着したものが好適である。
[0007] The greening substrate is preferably one in which a granular inorganic porous material and glass powder are mixed, fired, and the granular inorganic porous materials are bound to each other by a glass that has been melted and solidified.

【0008】かかる緑化基盤は、無機多孔体同士の間の
比較的大きな空隙に植物の根が入り込み易く、また無機
多孔体が保水や水浄化の機能を有し、植物の成育に好適
である。
[0008] Such a greening base is suitable for growing plants because the roots of the plant easily enter relatively large voids between the inorganic porous bodies, and the inorganic porous bodies have functions of water retention and water purification.

【0009】この無機多孔体がイオン交換能を有するも
のである場合、窒素(N)やリン(P)成分を除去する
ことができるので、水を緑化基盤に通すことにより水を
浄化することができる。このようなイオン交換能を有す
る無機多孔体としては、ゼオライト、バーミキュライ
ト、鹿沼土などが例示される。
When the inorganic porous material has an ion exchange ability, nitrogen (N) and phosphorus (P) components can be removed, so that water can be purified by passing water through a greening base. it can. Examples of the inorganic porous material having such ion exchange ability include zeolite, vermiculite, and Kanuma earth.

【0010】無機多孔体に鉄分の多い都市ゴミ焼却灰
や、鉄屑、石灰石、貝殻など、鉄イオン、カルシウムイ
オン供給能を有する成分を含有させることにより、水中
のリンをリン酸鉄やリン酸カルシウムとして固定して除
去することができる。
[0010] Phosphorus in water is converted into iron phosphate or calcium phosphate by incorporating a component capable of supplying iron ions and calcium ions, such as incinerated ash, garbage, limestone, and shells, which contain a large amount of iron, into the inorganic porous material. Can be fixed and removed.

【0011】本発明では、この緑化基盤の無機多孔体同
士の間の空隙に土を詰めても良い。この場合、土に有機
系バインダーを含有させることにより、降雨による土の
流去や、風による土の飛散を防止することができる。
In the present invention, the space between the inorganic porous bodies on the greening base may be filled with soil. In this case, by allowing the soil to contain an organic binder, it is possible to prevent the soil from running off due to rainfall and the soil from scattering due to wind.

【0012】本発明では、この緑化基盤の上面に土保持
層を設け、有機系バインダーを含有する土をこの土保持
層に詰めるか又は土保持層の上に堆積させて複合緑化基
盤としてもよい。かかる複合緑化基盤にあっては、土が
十分に保持されており、植物を十分に成育させることが
できる。
In the present invention, a soil holding layer may be provided on the upper surface of the greening base, and soil containing an organic binder may be filled in the soil holding layer or deposited on the soil holding layer to form a composite greening base. . In such a complex greening base, the soil is sufficiently maintained, and the plant can be sufficiently grown.

【0013】[0013]

【発明の実施の形態】以下、本発明の実施の形態につい
て詳細に説明する。
Embodiments of the present invention will be described below in detail.

【0014】本発明の緑化基盤を構成する粒状の無機多
孔体としては、ゼオライト、バーミキュライト、鹿沼
土、マサ土、赤玉土などが好適である。この無機多孔体
の平均粒径は、0.5〜10mm特に2〜5mmが好ま
しい。この無機多孔体は、天然鉱物を粗砕して上記粒度
に篩分けしたのものであってもよく、それよりも細かい
粒度のものを造粒して焼成し、粒状としたものであって
もよい。
As the granular inorganic porous material constituting the greening substrate of the present invention, zeolite, vermiculite, Kanuma earth, Masa earth, Akadama earth and the like are suitable. The average particle size of the inorganic porous body is preferably 0.5 to 10 mm, particularly preferably 2 to 5 mm. This inorganic porous material may be a material obtained by coarsely crushing a natural mineral and sieving it to the above particle size, or may be a material obtained by granulating and firing a finer particle than that and granulating it. Good.

【0015】この無機多孔体がゼオライトである場合、
N,P両成分を除去することができる。無機多孔体がバ
ーミキュライトであれば、N分を除去でき、鹿沼土であ
ればP分を除去できる。無機多孔体が、鉄分の多い都市
ゴミなどの焼却灰(例えばFeを1%以上特に1
0%以上含むもの)や、鉄屑、石灰石、貝殻など、鉄イ
オン、カルシウムイオンを供給するものを含有する場
合、P分をリン酸鉄やリン酸カルシウムとして除去する
ことができる。
When the inorganic porous material is zeolite,
Both N and P components can be removed. If the inorganic porous material is vermiculite, N can be removed, and if it is Kanuma soil, P can be removed. When the inorganic porous material is used to burn incinerated ash (eg, Fe 2 O 3 by 1% or more,
0% or more), iron scraps, limestone, shells, and other substances that supply iron ions and calcium ions, the P content can be removed as iron phosphate or calcium phosphate.

【0016】この焼却灰等は、ゼオライト、バーミキュ
ライト、鹿沼土などの粉体あるいは粉粒体と混合され、
造粒及び焼成されて粒状体とされる。焼却灰等の配合割
合は、ゼオライト等100重量部に対し、都市ゴミ焼却
灰の場合5〜20重量部、鉄屑の場合1〜15重量部、
石灰石及び貝殻の場合5〜50重量部程度が好ましい。
The incinerated ash and the like are mixed with powder or granules such as zeolite, vermiculite, and Kanuma soil,
It is granulated and fired to form a granular material. The incorporation ratio of incinerated ash etc. is 100 parts by weight of zeolite, etc., 5 to 20 parts by weight in the case of municipal waste incinerated ash, 1 to 15 parts by weight of iron scrap,
In the case of limestone and shells, the content is preferably about 5 to 50 parts by weight.

【0017】この緑化基盤を製造する場合、上記無機多
孔体に対しガラス粉を添加し、このガラスの融点よりも
高い温度にまで加熱し、ガラスを熔融させ、次いで冷却
してガラスを固化させ、この固化したガラスによって無
機多孔体同士を結着するのが好ましい。
When the greening substrate is manufactured, glass powder is added to the inorganic porous body, heated to a temperature higher than the melting point of the glass, the glass is melted, and then cooled to solidify the glass. It is preferable to bind the inorganic porous bodies to each other by the solidified glass.

【0018】このガラスとしては珪酸ソーダガラス、ホ
ウ珪酸ソーダガラスなどの珪酸系のものが好適である
が、これに限定されるものではない。ガラスは、新品の
ガラスであってもよく、廃ガラスであってもよい。釉薬
に用いられるガラスフリットであってもよい。ガラス粉
の平均粒径は10〜2000μm特に10〜50μmが
好ましい。ガラス粉の配合量は無機多孔体100重量部
に対し5〜100重量部特に20〜50重量部程度が好
ましい。
The glass is preferably a silicate glass such as sodium silicate glass and sodium borosilicate glass, but is not limited thereto. The glass may be new glass or waste glass. It may be a glass frit used for glaze. The average particle size of the glass powder is preferably from 10 to 2000 μm, particularly preferably from 10 to 50 μm. The compounding amount of the glass powder is preferably 5 to 100 parts by weight, particularly preferably about 20 to 50 parts by weight, based on 100 parts by weight of the inorganic porous material.

【0019】製造された緑化基盤には、粒状無機多孔体
同士の間に平均して500μm〜5mm程度の空隙が形
成されていることが好ましい。
It is preferable that a void having an average of about 500 μm to 5 mm is formed between the granular inorganic porous bodies in the produced greening substrate.

【0020】製造された緑化基盤は、一辺が30〜90
cm程度の方形であることが好ましい。
The greening substrate thus manufactured has a side of 30-90.
It is preferably a square of about cm.

【0021】この緑化基盤の無機多孔体同士の間の空隙
に、有機系バインダーが配合された土を詰めてもよい。
この有機系バインダーとしては、デンプン、メチルセル
ロース(MC)、カルボキシメチルセルロース(CM
C)、「とびこ(飛粉)」と称されるこんにゃく粉など
が好適である。有機系バインダーの添加量は、乾燥重量
で100重量部の土に対し、10〜30重量部が好適で
ある。
The space between the inorganic porous bodies on the greening base may be filled with soil containing an organic binder.
Such organic binders include starch, methylcellulose (MC), carboxymethylcellulose (CM
C) and konjac powder called "tobiko (flying powder)" are suitable. The amount of the organic binder to be added is preferably 10 to 30 parts by weight based on 100 parts by weight of dry soil.

【0022】このような土を目詰めした緑化基盤又は土
を目詰めしていない緑化基盤の上に土の保持層を設け、
この土の保持層に土を詰めるか又は土の保持層の上に土
を堆積させてもよい。この土としては、降雨による流去
や風による飛散を防止するために上記の有機系バインダ
ー配合土を用いる。
[0022] A soil holding layer is provided on such a greening base filled with soil or a greening base not filled with soil,
The soil retaining layer may be filled with soil or soil may be deposited on the soil retaining layer. As the soil, the organic binder-containing soil described above is used to prevent runoff due to rainfall and scattering due to wind.

【0023】土の保持層としては、ヤシやココナツの木
の繊維をマット状に成形したヤシマットやココナツマッ
ト、ガラス繊維、スラグ繊維等の鉱物質繊維の不織布、
ウレタン等の軟質合成樹脂のスポンジ等が好適である。
この土保持層の厚さは10〜50mm程度が好適であ
る。この土保持層は、繊維同士の間やスポンジ孔等に土
の少なくとも一部が入り込むので土の流去や飛散を防止
する機能を有する。
As the soil retaining layer, non-woven fabrics of mineral fibers such as palm mats, coconut mats, glass fibers and slag fibers formed by shaping palm or coconut tree fibers into a mat shape;
A sponge made of a soft synthetic resin such as urethane is suitable.
The thickness of the soil retaining layer is preferably about 10 to 50 mm. This soil holding layer has a function of preventing runoff and scattering of the soil because at least a part of the soil enters between the fibers or into a sponge hole or the like.

【0024】この土の保持層に詰めるか又はその上に堆
積させる土の量は植物の種類に応じて適宜定めればよ
い。
The amount of soil packed in or deposited on the soil holding layer may be determined as appropriate according to the type of plant.

【0025】この緑化基盤あるいは複合緑化基盤に成育
させる植物は、スナゴケ、ハイゴケ等のコケ類、メキシ
コマンネングサ、ツルマンネングサ、サカサマンネング
サなどのセダム類が好適である。このセダム類は、多年
草であり、成長しても高さが低く、屋根において成育さ
せるのに好適である。
As the plants grown on the greening base or the complex greening base, mosses such as Snagoke and Hygomosa, and sedums such as Mexican stonecrop, Tsurumannengusa and Sasasa stonecrop are suitable. The sedums are perennials, have a low height even when grown, and are suitable for growing on a roof.

【0026】[0026]

【実施例】実施例1 粒径1〜3mmであり平均粒径2mmのバーミキュライ
ト100重量部に対しガラスフリット PN−5425
(日本フリット株式会社製)(平均粒径30μm)30
重量部をCMC80重量部と共に添加して混合した後、
15×15×3cmの大きさに成形し、乾燥した後、8
00℃×8Hr焼成し、次いで自然冷却することにより
緑化基盤を製造した。この緑化基盤の粒状無機多孔体と
してのバーミキュライト粒状体同士の間には、平均して
1mmの空隙があいていた。
Example 1 100 parts by weight of vermiculite having a particle diameter of 1 to 3 mm and an average particle diameter of 2 mm was used with a glass frit PN-5425.
(Nippon Frit Co., Ltd.) (Average particle size 30 μm) 30
Parts by weight together with 80 parts by weight of CMC and mixing,
After being formed into a size of 15 × 15 × 3 cm and dried, 8
The greening substrate was manufactured by firing at 00 ° C. × 8 hours and then naturally cooling. There was an average gap of 1 mm between the vermiculite granules as the granular inorganic porous bodies of the greening substrate.

【0027】この緑化基盤に、有機系バインダー配合土
を2g/cmの割合で目詰めしながら堆積させ、次い
でスナゴケを植えた。なお、有機系バインダーとしては
飛粉を土100重量部(乾燥重量)に対し20重量部の
割合で添加したものを用いた。
On this greening substrate, an organic binder compounding soil was deposited at a rate of 2 g / cm 2 while being plugged, and then a snake mushroom was planted. Here, as the organic binder, used was one in which flying powder was added at a ratio of 20 parts by weight to 100 parts by weight of soil (dry weight).

【0028】夏季にこの緑化基盤をビルの屋上に設置
し、小型合併浄化槽の処理水(N濃度15mg/L、P
濃度1mg/L)を緑化基盤に対し10L/m・da
yの割合で散水した。その結果、スナゴケは翌年に到る
まで順調に成育しつづけていることが認められた。ま
た、緑化基盤を透過してきた水の水質を測定したとこ
ろ、年間平均値としてN濃度6mg/L、P濃度0.9
8mg/Lであった。
In the summer, this greening base is installed on the roof of a building, and treated water (N concentration 15 mg / L, P
(Concentration: 1 mg / L) was applied to the greening substrate at 10 L / m 2 · da
Water was sprinkled at the rate of y. As a result, it was confirmed that Snagoke continued to grow smoothly until the following year. Further, when the quality of the water transmitted through the greening base was measured, the N concentration was 6 mg / L and the P concentration was 0.9 as an annual average value.
It was 8 mg / L.

【0029】実施例2 図1に示す複合緑化基盤を、実施例1の緑化基盤を用い
て製造した。即ち、実施例1において緑化基盤1に土を
目詰めすることなく、その上にヤシマット2を1cm厚
に敷き、その上に上記有機系バインダー配合土3を1c
m厚で堆積させた。この複合緑化基盤に植物4としてメ
キシコマンネングサを50本/mの割合で植えた後、
実施例1と同じくビルの屋上に設置し、同一の浄化槽処
理水を10L/m・dayの割合で散水した。このメ
キシコマンネングサは翌年に到るまで順調に成育しつづ
けている。複合緑化基盤を透過してきた水の水質は年間
平均値としてN濃度3.8mg/L、P濃度0.98m
g/Lであった。
Example 2 The composite greening substrate shown in FIG. 1 was manufactured using the greening substrate of Example 1. That is, in Example 1, the coconut mat 2 was spread to a thickness of 1 cm on the greening base 1 without clogging the soil, and the organic binder-containing soil 3 was placed thereon for 1 c.
m thickness. After planting Mexican stonecrop as a plant 4 at a rate of 50 / m 2 on this complex greening base,
The same septic tank treated water was sprinkled at a rate of 10 L / m 2 · day in the same manner as in Example 1 on the roof of a building. The Mexican stonecrop has grown steadily until the following year. The average water quality of the water that has passed through the complex greening base is 3.8 mg / L for N concentration and 0.98 m for P concentration.
g / L.

【0030】実施例3 バーミキュライトの代りにゼオライトを用いたこと、及
び有機系バインダーとしてデンプンの代りにコンニャク
とびこを用いたこと以外は実施例2と同様の試験を行っ
た。その結果、メキシコマンネングサは翌年に到るまで
順調に成育しつづけている。また、複合緑化基盤を透過
してきた水の水質は、年間平均値としてN濃度3.5m
g/L、P濃度0.4mg/Lであった。
Example 3 The same test as in Example 2 was carried out except that zeolite was used in place of vermiculite and konjac tobiko was used in place of starch as an organic binder. As a result, Mexican stonecrops continue to grow steadily until the following year. In addition, the quality of the water that has passed through the complex greening base has an annual average N concentration of 3.5 m.
g / L and P concentration were 0.4 mg / L.

【0031】実施例4 平均粒径2mmのバーミキュライト粉末100重量部に
対し平均粒径2mmの石灰石粉末20重量部をCMC8
0重量部と共に添加し、800℃×8Hrで焼成した。
無機多孔体としてかかる焼結体を用いたこと以外は実施
例2と同様に試験を行ったところ、メキシコマンネング
サは翌年に到るまで順調に成育しつづけた。複合緑化基
盤を透過してきた水の水質は年間平均値としてN濃度
3.8mg/L、P濃度0.3mg/Lであった。
Example 4 20 parts by weight of limestone powder having an average particle size of 2 mm was added to 100 parts by weight of vermiculite powder having an average particle size of 2 mm by CMC8.
It was added together with 0 parts by weight and fired at 800 ° C. × 8 hours.
A test was conducted in the same manner as in Example 2 except that such a sintered body was used as the inorganic porous body. As a result, Mexican stonecrop continued to grow smoothly until the following year. The water quality of the water permeating through the composite greening base was 3.8 mg / L in N concentration and 0.3 mg / L in P concentration as annual average values.

【0032】[0032]

【発明の効果】以上の通り、本発明によると、屋上や屋
根に設置するのに好適な緑化基盤が提供される。この緑
化基盤は、NやPなどの河川、湖沼、海などの水域の富
栄養化の原因物質を除去する機能を具備しうる。本発明
の緑化基盤は、有機系バインダー配合土を用いることに
より、降雨や風によっても土が流失することがない構成
とすることができ、水平な屋上や陸屋根に限らず、傾斜
屋根にも十分に適用可能である。この緑化基盤を屋根に
設けることにより、夏季には水の蒸発による冷房効果を
得ることもできる。また、緑化基盤の断熱効果を得るこ
とも可能である。
As described above, according to the present invention, a greening base suitable for installation on a roof or a roof is provided. This greening base can have a function of removing substances causing eutrophication of water bodies such as rivers, lakes and mars, and seas such as N and P. The greening base of the present invention can be configured so that the soil is not washed away by rainfall or wind by using the organic binder compounding soil. Applicable to By providing this greening base on the roof, a cooling effect by evaporation of water can be obtained in summer. It is also possible to obtain the heat insulating effect of the greening base.

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

【図1】実施の形態に係る複合緑化基盤の断面図であ
る。
FIG. 1 is a cross-sectional view of a composite greening substrate according to an embodiment.

【符号の説明】[Explanation of symbols]

1 緑化基盤 2 ヤシマット 3 有機系バインダー配合土 4 植物(メキシコマンネングサ) 1 Greening base 2 Palm mat 3 Organic binder compound soil 4 Plant (Mexic stonecrop)

───────────────────────────────────────────────────── フロントページの続き (72)発明者 松本 奈弥 愛知県常滑市鯉江本町5丁目1番地 株式 会社イナックス内 Fターム(参考) 2B022 AB04 BA02 BA03 BA04 BA05 BA12 BA23 BB01 BB02 BB03 ────────────────────────────────────────────────── ─── Continued on the front page (72) Inventor Naya Matsumoto 5-1-1 Koiehonmachi, Tokoname-shi, Aichi F-term in Inax Co., Ltd. (Reference) 2B022 AB04 BA02 BA03 BA04 BA05 BA12 BA23 BB01 BB02 BB03

Claims (6)

【特許請求の範囲】[Claims] 【請求項1】 粒状の無機多孔体を盤状に成形し固化さ
せてなる緑化基盤。
1. A greening base formed by shaping a granular inorganic porous body into a disk shape and solidifying it.
【請求項2】 請求項1において、前記粒状の無機多孔
体とガラス粉とを混合して焼成し、ガラスによって粒状
の該無機多孔体を結合させて固化させてなることを特徴
とする緑化基盤。
2. The greening substrate according to claim 1, wherein the granular inorganic porous body and glass powder are mixed and fired, and the granular inorganic porous body is bonded and solidified by glass. .
【請求項3】 請求項1又は2において、前記無機多孔
体がイオン交換能を有することを特徴とする緑化基盤。
3. The greening substrate according to claim 1, wherein the inorganic porous body has an ion exchange ability.
【請求項4】 請求項3において、前記無機多孔体がリ
ン除去成分を含有することを特徴とする緑化基盤。
4. The greening substrate according to claim 3, wherein the inorganic porous body contains a phosphorus removing component.
【請求項5】 請求項1ないし4のいずれか1項におい
て、有機系バインダーを含有させた土が目詰めされてな
ることを特徴とする緑化基盤。
5. The greening base according to claim 1, wherein the soil containing an organic binder is plugged.
【請求項6】 請求項1ないし4のいずれか1項の緑化
基盤と、 該緑化基盤の上面に設けられた土保持材層と、 該土保持材層に詰められるか又は該土保持材層の上に堆
積された、有機系バインダーを含有する土と、を有する
複合緑化基盤。
6. The greening base according to any one of claims 1 to 4, a soil holding material layer provided on an upper surface of the greening base, and a soil holding material layer packed in the soil holding material layer. And a soil containing an organic binder deposited thereon.
JP2001085433A 2001-03-23 2001-03-23 Greening base Pending JP2002272261A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP2001085433A JP2002272261A (en) 2001-03-23 2001-03-23 Greening base

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP2001085433A JP2002272261A (en) 2001-03-23 2001-03-23 Greening base

Publications (1)

Publication Number Publication Date
JP2002272261A true JP2002272261A (en) 2002-09-24

Family

ID=18940946

Family Applications (1)

Application Number Title Priority Date Filing Date
JP2001085433A Pending JP2002272261A (en) 2001-03-23 2001-03-23 Greening base

Country Status (1)

Country Link
JP (1) JP2002272261A (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2013519358A (en) * 2010-02-11 2013-05-30 エックスエフ テクノロジーズ ベスローテン フェノーツハップ Vegetation elements for planting artificial or natural surfaces with tall plants and / or tall plants and methods for producing vegetation elements
CN106797815A (en) * 2017-01-16 2017-06-06 广州市林业和园林科学研究院 A kind of liver moss greening patch and preparation method thereof

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2013519358A (en) * 2010-02-11 2013-05-30 エックスエフ テクノロジーズ ベスローテン フェノーツハップ Vegetation elements for planting artificial or natural surfaces with tall plants and / or tall plants and methods for producing vegetation elements
CN106797815A (en) * 2017-01-16 2017-06-06 广州市林业和园林科学研究院 A kind of liver moss greening patch and preparation method thereof

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