JPH0860155A - Culture soil for growing germinated plant - Google Patents

Culture soil for growing germinated plant

Info

Publication number
JPH0860155A
JPH0860155A JP6215204A JP21520494A JPH0860155A JP H0860155 A JPH0860155 A JP H0860155A JP 6215204 A JP6215204 A JP 6215204A JP 21520494 A JP21520494 A JP 21520494A JP H0860155 A JPH0860155 A JP H0860155A
Authority
JP
Japan
Prior art keywords
soil
growth
germination
industrial waste
fertilizer
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
JP6215204A
Other languages
Japanese (ja)
Inventor
Kikuo Kishimoto
菊夫 岸本
Kazuo Fukase
和男 深瀬
Kyoichi Kitsugi
恭一 木次
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.)
NAISU TEC KK
Original Assignee
NAISU TEC KK
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 NAISU TEC KK filed Critical NAISU TEC KK
Priority to JP6215204A priority Critical patent/JPH0860155A/en
Publication of JPH0860155A publication Critical patent/JPH0860155A/en
Pending legal-status Critical Current

Links

Classifications

    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02ATECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
    • Y02A40/00Adaptation technologies in agriculture, forestry, livestock or agroalimentary production
    • Y02A40/10Adaptation technologies in agriculture, forestry, livestock or agroalimentary production in agriculture
    • Y02A40/20Fertilizers of biological origin, e.g. guano or fertilizers made from animal corpses

Abstract

PURPOSE: To obtain the culture soil capable of simply growing plants by supplying water content and useful for planting the plants by subjecting industrial waste soil to soil-culturing treatment and including a fertilizer thereinto, granulating the soil containing fertilizer and drying the soil. CONSTITUTION: This culture soil is obtained by subjecting soil such as bottom sludge of lakes, and marshes and harbors or waste soil of purification plant to soil culturing treatment, including fertilizer having an amount necessary to carry out initial growth of plants and granulating the soil containing the fertilizer and drying the soil. Thereby, disposal of industrial waste soil is not required and the soil is useful for improvement of environment. The culture soil may be installed in the objective place after germinating seeds and germination period can be controlled by increasing or decreasing water content in culture soil.

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、湖沼港湾の浚渫底泥、
浄水場廃土または建設残土など(以下、これらを産業廃
土と言う。)の植物の生育に適さない土壌を培土処理し
て用いた植物生育用培土であって、植物の種子と初期生
育に必要な肥料を含有しており、目的の場所に使用し、
発芽、生育の日時に合わせて水分を補給することによ
り、使用場所で簡単に植物を生育させることができる培
土に関し、本発明の培土によれば通常の植物の植え込み
はもとより、芝生の修復用培土などとして広範に利用す
ることができる。
BACKGROUND OF THE INVENTION The present invention relates to a dredged bottom mud of a lake port,
A soil for plant growth, which is obtained by treating soil that is not suitable for plant growth, such as wastewater from a water purification plant or construction residual soil (hereinafter referred to as industrial waste soil), and is used for plant seeds and initial growth. Contains the required fertilizer, use it in the intended place,
By hydrating according to the date of germination and growth, the present invention relates to a cultivating soil that allows a plant to be easily grown at a place of use.According to the cultivating soil of the present invention, not only normal planting but also lawn restoration cultivating soil can be used. It can be widely used as such.

【0002】[0002]

【従来技術と問題点】ゴルフ場、スポーツ用グラウンド
などの芝生は、暫々、プレイ時に芝草が部分的に削ら
れ、各所に凹部(ディボット)が生じる。通常、ディボ
ットの修復には砂を入れて凹部を平坦化し、芝が自然に
再生することにより修復するか、あるいは緊急を要する
場合は別途育成した芝ソッドを凹部に移植して修復して
いる。従って、現状では芝生の修復に長時間を要し、し
かも人手がかかる。一方、建設残土、湖沼港湾等の浚渫
底泥あるいは浄水場廃土などの産業廃土は年々大量に発
生しており、その処分に問題を抱えている。これらの産
業廃土は植物の生育に有害な成分を含有する場合が多
く、土質も様々であるため、そのままでは園芸用土壌や
畑地、水田などの農業用土壌あるいは公園やゴルフ場、
各種グランドの芝生などの施設用土壌として利用するこ
とができず、大部分は産業廃棄物として埋立て処分され
ているのが現状である。
2. Description of the Related Art Problems on lawns such as golf courses and sports grounds are that the grass is partially cut off during play for a while, and recesses (divots) are formed in various places. Usually, in order to repair the divot, sand is put in to flatten the recess and the grass is naturally regenerated, or when an emergency is required, a separately grown grass sod is transplanted into the recess for repair. Therefore, at present, it takes a long time to repair the lawn, and moreover, it takes manpower. On the other hand, a large amount of construction waste soil, dredged mud in lake harbors, etc., or industrial waste soil such as wastewater from wastewater treatment plants is being generated every year, and there is a problem in its disposal. These industrial waste soils often contain components harmful to the growth of plants and have various soil qualities, so horticultural soils, upland fields, agricultural soils such as paddy fields, parks and golf courses,
It cannot be used as a soil for facilities such as lawns of various grounds, and most of it is currently landfilled as industrial waste.

【0003】[0003]

【発明の解決課題】本発明は、従来の上記問題を解決す
るものであって、年々大量に発生する産業廃土の理化学
性を改善して植物生育用土壌として利用できるように
し、その有効資材化を可能にすると共に、その好適な態
様として、芝生のディボットなどに使用することにより
芝生を容易に修復できるなど、従来の芝生修復の問題を
も解決する植物生育用培土を提供することを目的とす
る。
DISCLOSURE OF THE INVENTION The present invention solves the above-mentioned problems of the prior art, and improves the physicochemical properties of industrial waste soil, which is produced in large quantities year by year, so that it can be used as a soil for growing plants. The present invention aims to provide a vegetative soil for plant growth that solves the problems of conventional lawn restoration, such as the ability to easily restore the lawn by using it as a divot of lawn, etc. And

【0004】[0004]

【課題の解決手段】本発明によれば、以下の構成からな
る発芽生育培土が提供される。 (1)産業廃土を培土化処理すると共に植物の初期生育
に必要な量の肥料を含有させて造粒し、乾燥した発芽生
育培土。 (2)植物の初期生育に必要な量の肥料と共に植物種子
を含有させて造粒し、乾燥した上記(1) の発芽生育培
土。 (3)湖沼や港湾の浚渫底泥、建設残土あるいは浄水場
廃土の産業廃土を培土化処理して用いた上記(1) の発芽
生育培土。 (4)強アルカリ性の産業廃土に、該廃土のリン酸吸収
係数の2〜6%相当量の過リン酸石灰ないし重過リン酸
石灰を添加することにより水素イオン濃度を低下させ、
リン酸を富化した土壌を用いた上記(1) の発芽生育培
土。 (5)産業廃土に石膏を添加して廃土中の塩素イオンを
置換溶脱した土壌を用いた上記(1) の発芽生育培土。 (6)産業廃土に石灰質資材ないしケイ酸質資材を添加
して廃土中の硫化鉄に起因する酸性化を防止した土壌を
用いた上記(1) の発芽生育培土。 (7)産業廃土に石灰ないしケイ酸石灰を添加し、廃土
中の金属イオンを難溶性化合物に変えて不活性化した土
壌を用いた上記(1) の発芽生育培土。 (8)培土化処理した産業廃土に炭素資材を添加して保
水性を高めた土壌を用いた上記(1) の発芽生育培土。 (9)芝の種子を含有する芝生修復用の上記(1) 〜(8)
の何れかに記載の発芽生育培土。
According to the present invention, a germination growth medium having the following constitution is provided. (1) A germinated growth medium which is obtained by subjecting industrial waste soil to soil cultivation treatment, granulating it by adding an amount of fertilizer necessary for initial growth of plants, and drying. (2) The germination growth medium of (1) above, which is obtained by incorporating plant seeds together with an amount of fertilizer necessary for initial growth of the plant, granulating and drying. (3) The germination and growth medium of the above (1), which is obtained by cultivating industrial waste soil such as dredged mud in lakes and harbors, construction residual soil, or wastewater from water purification plants. (4) The hydrogen ion concentration is lowered by adding to the strongly alkaline industrial waste soil an amount of 2-6% or so of the phosphate absorption coefficient of the waste soil, that is, superphosphate or hypersuperphosphate,
The germination growth medium of the above (1) using a phosphate-enriched soil. (5) The germination and growth medium of (1) above, which uses soil in which gypsum was added to industrial waste soil to replace chloride ions in the waste soil and to be leached. (6) The germination growth soil of (1) above, which uses soil in which calcareous or siliceous materials have been added to industrial waste soil to prevent acidification due to iron sulfide in the waste soil. (7) The germination and growth medium of the above (1), which uses inactivated soil by adding lime or silicate lime to industrial waste soil and converting metal ions in the waste soil into sparingly soluble compounds. (8) The germination and growth medium of (1) above, which uses soil in which carbon materials have been added to the industrial waste soil that has been treated for soil cultivation to improve water retention. (9) Above (1) to (8) for lawn restoration containing turf seeds
The germination growth soil as described in any of 1.

【0005】[0005]

【具体的な説明】以下に本発明を実施例と共に具体的に
説明する。なお、以下の説明において%は特に述べない
限り重量%である。
[Detailed Description] The present invention will be specifically described below with reference to Examples. In the following description,% means% by weight unless otherwise specified.

【0006】上記産業廃土を植物生育用の土壌として利
用するには、該廃土中の有害成分を除去して土質を整え
る培土化処理を施す必要がある。この培土化処理は産業
廃土に含まれる有害成分の種類によって異なり、産業廃
土の種類に応じて次のような培土化処理が施される。 イ.廃土中の有害成分を難溶性化合物に変化させて無害
化する。 ロ.廃土中の有害成分を複分解により溶脱して無害化す
る。 ハ.廃土の理化学性、特にpHを植物の生育に適する範
囲に矯正する。 さらに、本発明の発芽生育培土は、培土化処理した土壌
に植物種子と初期生育に必要な量の肥料を添加して造粒
し、乾燥したものであり、目的の場所に設置して水分を
補給するだけで、植物が発芽、生育する特徴を有する。
In order to use the industrial waste soil as soil for growing plants, it is necessary to remove soil harmful substances from the waste soil to improve soil quality. This cultivating treatment differs depending on the type of harmful components contained in the industrial waste soil, and the following cultivating treatment is performed according to the type of industrial waste soil. I. It converts harmful components in waste soil into sparingly soluble compounds to render them harmless. B. Detoxify harmful components in waste soil by metathesis to make them harmless. C. Correct the physicochemical properties of waste soil, especially pH, to a range suitable for plant growth. Furthermore, the germination growth soil of the present invention is a soil that has been treated with soil by adding a plant seed and a fertilizer in an amount necessary for initial growth, granulated, and dried. It has the characteristic that the plant germinates and grows only by supplementing it.

【0007】産業廃土の具体的な培土化処理を以下に示
す。 (I) 建設残土は石灰などを含み強アルカリ性を有する
場合があるが、このような強アルカリ性の産業廃土につ
いては、その水素イオン濃度(pH)を矯正する方法とし
て、硫酸等の過激な薬物を使用せずに、過リン酸石灰や
重過リン酸石灰などのリン酸石灰を加え、土壌のpHを
低下させると共に必須栄養源であるリン酸を富化する。
これらリン酸石灰の添加量は廃土のリン酸吸収係数の2
〜6%相当量が適当であり、このリン酸石灰の添加によ
り廃土のpHを7〜9に低下させる。培土のpHがこの
範囲であれば植物の生育に支障がない。一般に、通常の
土壌のリン酸吸収係数は1000〜1500であるが、建設残土
などのように石灰を加えて強アルカリ処理されたものの
リン酸吸収係数は2000前後であり、建設残土の単位重量
(100kg)当たり0.2〜1.2kgの過リン酸石灰ないし
重過リン酸石灰を添加することにより、残土のpHが7
〜9に矯正される。
The concrete soil sewage treatment of industrial waste soil is shown below. (I) Construction residual soil may contain lime and the like and has a strong alkalinity. For such strongly alkaline industrial waste soil, as a method for correcting the hydrogen ion concentration (pH), a radical drug such as sulfuric acid is used. Without using lime, lime phosphates such as lime superphosphate and lime superphosphate are added to lower the pH of the soil and enrich the phosphate as an essential nutrient source.
The amount of lime phosphate added is 2 of the phosphate absorption coefficient of waste soil.
An amount equivalent to ~ 6% is suitable, and the pH of waste soil is lowered to 7-9 by the addition of this lime phosphate. If the pH of the cultivated soil is within this range, the growth of plants will not be hindered. Generally, the phosphate absorption coefficient of normal soil is 1000 to 1500, but the phosphate absorption coefficient of strong alkaline treatment with lime such as construction residual soil is around 2000, and the unit weight of construction residual soil
The pH of the residual soil is adjusted to 7 by adding 0.2 to 1.2 kg of superphosphate or hypersuperphosphate per 100 kg.
Corrected to ~ 9.

【0008】強アルカリ性の建設残土(土壌pH:11 , リ
ン酸吸収係数2000)に、過リン酸石灰を所定量添加した
場合の土壌pH値を表1に示す。なお、試料No5は過リ
ン酸石灰と共に硫安を添加したものであり、試料No6は
過リン酸石灰に代えて硫酸を用いた比較例である。ま
た、pH値は試料土壌1gに水2.5gを添加して測定
した。表示されるように、過リン酸石灰の添加により添
加量に比例して土壌pHが低下しており、硫安を併用し
たものはpHの低下効果が高い。
Table 1 shows soil pH values when a predetermined amount of lime superphosphate was added to the strongly alkaline construction residual soil (soil pH: 11, phosphate absorption coefficient 2000). Sample No. 5 is a sample in which ammonium sulfate is added together with lime superphosphate, and Sample No. 6 is a comparative example in which sulfuric acid is used instead of lime superphosphate. The pH value was measured by adding 2.5 g of water to 1 g of the sample soil. As shown, the addition of lime superphosphate lowers the soil pH in proportion to the addition amount, and the one using ammonium sulfate in combination has a high pH lowering effect.

【0009】[0009]

【表1】 [Table 1]

【0010】(II) 産業廃土が港湾などの浚渫底泥の場
合は、海水の食塩に由来する多量の塩素イオンを含む場
合が多く、この塩素イオンは植物に有害なので、この浚
渫底泥に石膏(CaSO4・2H2 O )を添加し、底泥中の塩素
イオンを置換溶脱させる。石膏の添加量は底泥の食塩量
が0.15%以下になる量が適当である。食塩の含有量
が0.15%を越える土壌は塩素イオンの影響が著し
い。概ね、浚渫底泥中の食塩に対して0.5〜1.5当
量の石膏を添加することにより食塩含有量を0.15%
以下に減少することができる。
(II) When the industrial waste is dredged mud such as in a harbor, it often contains a large amount of chlorine ions derived from salt of seawater, and this chlorine ion is harmful to plants. Gypsum (CaSO 4・ 2H 2 O) is added to replace chloride ions in the bottom mud for leaching. The amount of gypsum added is preferably such that the salt content of the bottom mud is 0.15% or less. The effect of chloride ions is remarkable in soils with a salt content exceeding 0.15%. Generally, the salt content is 0.15% by adding 0.5 to 1.5 equivalents of gypsum to the salt in the dredged bottom mud.
It can be reduced to:

【0011】乾土中に3.8%の食塩を含有する港湾浚
渫底泥について、含有食塩に対して0.5〜1.5当量
の石膏を添加し、攪拌後、ブフナー漏斗で吸引濾過する
ことにより含有食塩を溶脱処理した土壌の残留食塩量を
表2に示した。含有食塩に対して等量以上の石膏を添加
した土壌の残留食塩量は0.15%以下に減少してい
る。
With respect to the harbor dredged bottom mud containing 3.8% of salt in dry soil, 0.5 to 1.5 equivalents of gypsum are added to the contained salt, and after stirring, suction filtration is performed with a Buchner funnel. Table 2 shows the residual salt amount of the soil from which the contained salt was leached. The amount of residual salt in soil in which an equal amount or more of gypsum was added to the contained salt decreased to 0.15% or less.

【0012】[0012]

【表2】 [Table 2]

【0013】(III)また、河川や港湾、湖沼などに堆積
した底泥は大部分が嫌気性環境下にあるため、土壌中の
鉄分が硫化鉄の形で存在しており、これを浚渫して大気
中に放置すると硫化鉄が酸化して土壌が酸性化する。そ
こで、この酸性化対策として、浚渫底泥に石灰質資材あ
るいはケイ酸質資材を添加することにより硫化鉄に由来
する硫酸を中和し、酸性化を抑制する。石灰質資材とし
ては消石灰、ケイ酸石灰(トバモライト)などが用いら
れ、添加量としては浚渫底泥の乾燥重量に対して1〜3
%が適当である。ケイ酸質資材の添加については、底泥
をプリコートにより脱水する際に、トバモライト粉末を
プリコート助剤として使用することにより、脱水と共に
ケイ酸質資材を添加でき、また同時にトバモライトのp
H矯正作用を利用することができる。
(III) In addition, since most of the bottom mud deposited in rivers, harbors, lakes and marshes is under anaerobic environment, iron in the soil exists in the form of iron sulfide, which is dredged. When left in the atmosphere for a long time, iron sulfide is oxidized and the soil is acidified. Therefore, as a measure against this acidification, a calcareous material or a siliceous material is added to the dredged bottom mud to neutralize the sulfuric acid derived from iron sulfide and suppress the acidification. Slaked lime, silicate lime (tobermorite), etc. are used as the calcareous material, and the addition amount is 1 to 3 with respect to the dry weight of the dredged bottom mud.
% Is appropriate. Regarding the addition of siliceous materials, by using tobermorite powder as a pre-coating aid when dewatering bottom mud by precoating, it is possible to add the siliceous material together with dehydration, and at the same time, tobermorite p
The H straightening effect can be utilized.

【0014】含水量35%の浚渫底泥に所定量のトバモ
ライト(ケイ酸質資材)および消石灰を添加し、攪拌混
合した後のpH値を表3に示した。添加量は底泥乾土当
りトバモライト1%および3%、消石灰1%である。p
H値は乾土1g当り2.5gの水を添加して測定した。
ケイ酸質資材および石灰質資材の添加により、底泥の酸
性化が長期間抑制される。
Table 3 shows the pH values after adding a predetermined amount of tobermorite (silicic material) and slaked lime to a dredged bottom mud having a water content of 35% and stirring and mixing. The addition amounts are 1% and 3% tobermorite and 1% slaked lime per dry soil of bottom mud. p
The H value was measured by adding 2.5 g of water per 1 g of dry soil.
The addition of siliceous materials and calcareous materials suppresses acidification of bottom mud for a long time.

【0015】[0015]

【表3】 [Table 3]

【0016】(IV) 浄水場廃土は、通常、マンガンやア
ルミニウムなどの金属イオンの含有量が高く、これらは
酸性下で活性化し、植物の生育を阻害するので、浄水場
廃土に石灰ないしケイ酸石灰を添加し、土壌のpHを7
以上に中和して廃土中の金属イオンを難溶性化合物に変
えて不活性化すると共にリン酸吸収係数の5%前後のリ
ン酸質資材の添加を行う。
(IV) Wastewater from the purification plant usually has a high content of metal ions such as manganese and aluminum, which are activated under acidic conditions and inhibit the growth of plants. Add lime silicate to increase soil pH to 7
As described above, neutralization is performed to change the metal ions in the waste soil into a sparingly soluble compound to inactivate it, and a phosphate material having a phosphate absorption coefficient of about 5% is added.

【0017】上記(I) 〜(IV)の培土処理を経た土壌に、
木炭屑などの炭素資材を添加して保水性を高めると良
い。炭素資材としては木炭屑のほかに廃活性炭などが用
いられる。また添加量は土壌の乾燥単位重量当たり0.
3%以下が適当である。
To the soil that has undergone the soil treatment of (I) to (IV) above,
It is recommended to add carbon materials such as charcoal scraps to improve water retention. As the carbon material, not only charcoal scraps but also waste activated carbon is used. The addition amount is 0. per dry unit weight of soil.
3% or less is suitable.

【0018】上記培土処理を経て得た土壌に植物種子を
混合し、さらに該植物の初期生育に必要な量の肥料を含
有させる。肥料成分としては、必須栄養素の窒素、燐、
カリの供給源である硫安、過リン酸石灰および塩化カリ
が添加され、その含有量としては、土壌1ton 当り、硫
安1.0〜3.0kg、過リン酸石灰1.0〜3.0kg、
塩化カリ0.5〜1.5kgが適当である。本発明の培土
は必要量の肥料を含有するので、目的の場所に使用し、
水分を補給するだけで植物を発芽、生育させることがで
きる。
[0018] Plant seeds are mixed with the soil obtained through the above-mentioned soil treatment, and fertilizer is added in an amount necessary for the initial growth of the plant. Fertilizer components include essential nutrients such as nitrogen, phosphorus,
Ammonium sulphate, lime superphosphate and potassium chloride, which are sources of potassium, are added, and the content of ammonium sulphate is 1.0 to 3.0 kg and lime superphosphate is 1.0 to 3.0 kg per ton of soil.
0.5 to 1.5 kg of potassium chloride is suitable. Since the soil of the present invention contains the required amount of fertilizer, it is used at the intended place,
A plant can be germinated and grown only by supplying water.

【0019】植物種子は、施肥培土1kg(乾燥重量)当
り20〜30g混合すると良い。植物種子および肥料を
添加した培土を、必要に応じて加水し、造粒して乾燥す
る。造粒物を乾燥(通風乾燥)し、含有水分量により発
芽時期を制御することができる。一例として、芝草の種
子について室温下での含水量と発芽時期との関係を表5
に示す。概ね、培土の含水量を15%以下に保つことに
より培土中の種子の発芽を止めることができる。使用時
には生育に必要な量の水分を適宜補給する。補給水分量
と温度を調整することにより目的の日時に発芽させるこ
とができる。なお、植物の種子を予め発芽用加温器中で
発芽させた後に、肥料入り培土と混合して使用しても良
く、また、種子と肥料とを培土に混合し、これを発芽用
加温器に入れて発芽させた後に目的の場所で使用しても
良い。この場合には、目的の場所で使用後、発芽に要す
る期間を短縮できる。
The plant seeds are preferably mixed in an amount of 20 to 30 g per 1 kg (dry weight) of fertilized soil. The soil containing the plant seeds and the fertilizer is watered if necessary, granulated and dried. The granulated product can be dried (ventilated drying) and the germination time can be controlled by the water content. As an example, Table 5 shows the relationship between water content and germination time at room temperature for turfgrass seeds.
Shown in Generally, germination of seeds in the soil can be stopped by keeping the water content of the soil at 15% or less. At the time of use, the amount of water necessary for growth is appropriately replenished. It is possible to germinate at the target date and time by adjusting the amount of supplemental water and the temperature. The seeds of the plant may be pre-germinated in a germination warmer and then mixed with fertilizer-containing soil, or the seeds and fertilizer may be mixed with the soil and warmed for germination. It may be used in the intended place after being put into a container and germinated. In this case, the period required for germination can be shortened after use at the intended place.

【0020】[0020]

【表4】 [Table 4]

【0021】本発明の培土は植物の種子と肥料を含有し
て造粒したものであり、粒状であるため取扱い容易く、
所定の場所に均一に使用することができる。造粒培土の
粒径は0.5〜6.0mmが適当である。本発明の培土
は、通常の土壌と混合して使用しても良い。
The culture medium of the present invention is a granulated product containing plant seeds and fertilizers, and is easy to handle because it is granular.
It can be used uniformly in a predetermined place. A suitable grain size of the granulation medium is 0.5 to 6.0 mm. The culture medium of the present invention may be used as a mixture with ordinary soil.

【0022】[0022]

【実施例】本発明の実施例を以下に示す。なお本実施例
は例示であり、本発明の範囲を限定するものではない。
EXAMPLES Examples of the present invention are shown below. It should be noted that the present embodiment is merely an example and does not limit the scope of the present invention.

【0023】実施例1 湖沼浚渫底泥を吸引し、プリコートフィルターで瀘過脱
水を行ない、含水量約40〜45%の脱水ケーキを得
た。このケーキを風乾等により乾燥し含水量を30%前
後にした後、2%のトバモライト粉末を加え、さらにチ
ッ素(N),リン酸(P2 O 5 ) 、カリ(K2 O)を各々0.05
%相当量含む肥料を添加した。この土壌に目的の植物種
子を加え、水をバインダ−として造粒した。造粒土壌を
含水量15%以下に乾燥して、肥料種子入りの本発明品
培土とした。この培土を任意の容器に入れ、培土の含水
量が30%以上になるように潅水して室温下に置いたと
ころ、4〜10月の期間に7〜12日で発芽し、生育し
始めた。
Example 1 Lake mud dredged bottom mud was sucked and filtered and dehydrated with a precoat filter to obtain a dehydrated cake having a water content of about 40 to 45%. This cake is dried by air-drying to adjust the water content to about 30%, 2% tobermorite powder is added, and further nitrogen (N), phosphoric acid (P 2 O 5 ), and potassium (K 2 O) are added. 0.05
A fertilizer containing an equivalent amount of% was added. Target plant seeds were added to this soil and granulated using water as a binder. The granulated soil was dried to a water content of 15% or less to obtain fertilizer seed-containing present invention soil. When this soil was put in an arbitrary container, water was irrigated so that the water content of the soil was 30% or more, and it was placed at room temperature, it sprouted in 7 to 12 days in the period of 4 to 10 months and started to grow. .

【0024】実施例2 強アルカリ性(pH:10 〜12) の建設残土にリン酸吸収係
数の5%相当量の普通過リン酸石灰を添加して混合し、
これに生理的酸性肥料である硫安ないし塩化カリを各成
分毎に0.05%相当量を加え、土壌pHを9.0以下
に調整した。次に木炭屑を乾土の0.3%添加した培土
に、この1kg当たり20〜30gの催芽した芝草の種子
を添加混合して芝生修復用培土を得た。この培土をゴル
フ場のディボットに埋め、通常の管理条件下に放置した
ところ、4〜10月の期間に7〜12日で発芽し、約2
0日間で周囲の芝草と同程度の高さに成長した。なお、
これにより芝草の種子では培土のpHが9前後でも必須
栄養素であるチッ素、リン酸、カリを適量含む肥料を十
分添加しておけば、芝草が良く生育するが確認された。
Example 2 To a strongly alkaline (pH: 10 to 12) construction residual soil, 5% of a phosphate absorption coefficient of ordinary superphosphate was added and mixed,
Ammonium sulfate or potassium chloride, which is a physiologically acidic fertilizer, was added to each component in an amount of 0.05% to adjust the soil pH to 9.0 or less. Next, 20 to 30 g of germinated turfgrass seeds per 1 kg of this was added to and mixed with the soil containing charcoal dust in an amount of 0.3% of dry soil to obtain a soil for lawn restoration. When this soil was buried in a divot on a golf course and left under normal management conditions, it germinated in 7 to 12 days in a period of 4 to 10 months and about 2
It grew to the same height as the surrounding grass in 0 days. In addition,
From this, it was confirmed that, even if the pH of the turf was around 9, the turfgrass seeds were well grown in the turfgrass seeds if the fertilizer containing a proper amount of the essential nutrients such as nitrogen, phosphoric acid and potassium was added.

【0025】実施例3 食塩含量3.8%(乾土)の港湾底泥に、食塩と等量の
石膏および底泥乾土当たり3%相当量のトバモライト粉
末を加え、吸引、脱水後、乾燥して食塩含量0.15%
の土壌を得た。この土壌に芝草の初期生育を十分にする
量の肥料をチッ素、リン酸、カリの各成分を0.05%
相当量加え、さらに予め出芽させた芝草種子を培土1kg
当たり30g混合して芝草修復用培土を得た。この培土
を芝生のデボットに埋め、通常の管理条件下に放置し
た。この結果、培土使用後2週間目で、凹部の80%以
上が培土から生育した芝草によって被覆された。なお、
芝草の種子に代えて水稲の種子を用いた場合には、0.
1%以下の食塩含有量の場合には、水稲の生育に支障は
なく、食塩含有量が0.3%を上回ると生育に支障をき
たすことが確認された。
Example 3 To a port bottom mud having a salt content of 3.8% (dry soil), gypsum in an amount equal to that of salt and 3% of tobermorite powder per dry soil of the bottom mud were added, suctioned, dehydrated and dried. And salt content 0.15%
Got soil. The amount of fertilizer sufficient for the initial growth of turfgrass on this soil is 0.05% of nitrogen, phosphoric acid, and potassium.
Add a considerable amount of turfgrass seeds that have been sprouted in advance and cultivate 1 kg of soil
Each 30 g was mixed to obtain a turf grass restoration soil. This soil was embedded in a lawn divot and left under normal control conditions. As a result, 80% or more of the recesses were covered with turfgrass grown from the soil 2 weeks after the soil was used. In addition,
When seeds of paddy rice were used instead of seeds of turfgrass, 0.
It was confirmed that when the salt content was 1% or less, there was no hindrance to the growth of rice, and when the salt content exceeded 0.3%, the growth was hindered.

【0026】実施例4 可溶性アルミニウム50ppm および交換性マンガン90
0ppm を含む浄水場廃土に、pHが7.0になるのに必
要な量の消石灰を加えて混合し、さらに、これに芝草種
子および窒素、リン酸、カリ肥料の各成分を0.05%
相当量加えて造粒し、風乾して製品とした。これをデボ
ット埋砂の代わりに使用したところ、使用後3週間目で
良好な芝生となり、浄水場廃土に由来するアルミニウム
およびマンガンによる芝草の生育障害は認められなかっ
た。
Example 4 Soluble Aluminum 50 ppm and Exchangeable Manganese 90
To the wastewater from the water purification plant containing 0 ppm, add the necessary amount of slaked lime to reach pH 7.0, and mix it with 0.05% turfgrass seeds and nitrogen, phosphoric acid, and potassium fertilizer components.
A considerable amount was added, granulated, and air dried to obtain a product. When this was used in place of the divot burial sand, it became a good lawn 3 weeks after the use, and no growth damage of turfgrass due to aluminum and manganese derived from wastewater from the water treatment plant was observed.

【0027】[0027]

【発明の効果】本発明によれば、湖沼、港湾内の底泥、
建設残土等の産業廃土を植物生育用の培土として活用す
ることができる。このため、年々増大する産業廃土の廃
棄処理の問題を解決することができ環境改善に役立つ。
また、本発明の培土は植物種子と共に植物の初期生育を
十分に行なえる量の肥料を含有しているので、目的の場
所に使用し、水分を補給するだけで植物を容易に発芽生
育させることができ、芝生のディボットを簡易、迅速に
修復することができる。なお、種子を予め発芽させてか
ら目的の場所に使用してもよく、また水分量を加減して
発芽時期を調整することができるので、使用場所に応じ
た時期に発芽生育させることができるなどの利点を有す
る。
According to the present invention, lakes, sediments in harbors,
Industrial waste soil such as construction surplus soil can be used as soil for growing plants. Therefore, it is possible to solve the problem of waste disposal of industrial waste soil, which is increasing year by year, and to improve the environment.
Further, the soil of the present invention contains fertilizer in an amount sufficient for the initial growth of the plant together with the plant seed, so that the plant can be easily germinated and grown only by replenishing it with water at a desired place. The divot on the lawn can be easily and quickly restored. The seeds may be germinated in advance and then used in a desired place, and since the germination time can be adjusted by adjusting the water content, the seeds can be germinated and grown at a time according to the use place. Have the advantage of.

【手続補正書】[Procedure amendment]

【提出日】平成6年9月20日[Submission date] September 20, 1994

【手続補正1】[Procedure Amendment 1]

【補正対象書類名】明細書[Document name to be amended] Statement

【補正対象項目名】請求項4[Name of item to be corrected] Claim 4

【補正方法】変更[Correction method] Change

【補正内容】[Correction content]

【手続補正2】[Procedure Amendment 2]

【補正対象書類名】明細書[Document name to be amended] Statement

【補正対象項目名】0004[Correction target item name] 0004

【補正方法】変更[Correction method] Change

【補正内容】[Correction content]

【0004】[0004]

【課題の解決手段】 本発明によれば、以下の構成から
なる発芽生育培土が提供される。 (1)産業廃土を培土化処理すると共に植物の初期生育
に必要な量の肥料を含有させて造粒し、乾燥した発芽生
育培土。 (2)植物の初期生育に必要な量の肥料と共に植物種子
を含有させて造粒し、乾燥した上記(1)の発芽生育培
土。 (3)湖沼や港湾の浚渫底泥、建設残土あるいは浄水場
廃土の産業廃土を培土化処理して用いた上記(1)の発
芽生育培土。 (4)強アルカリ性の産業廃土に、該廃土のリン酸吸収
係数の2〜12%相当量の過リン酸石灰ないし重過リン
酸石灰を添加することにより水素イオン濃度を低下さ
せ、リン酸を富化した土壌を用いた上記(1)の発芽生
育培土。 (5)産業廃土に石膏を添加して廃土中の塩素イオンを
置換溶脱した土壌を用いた上記(1)の発芽生育培土。 (6)産業廃土に石灰質資材ないしケイ酸質資材を添加
して廃土中の硫化鉄に起因する酸性化を防止した土壌を
用いた上記(1)の発芽生育培土。 (7)産業廃土に石灰ないしケイ酸石灰を添加し、廃土
中の金属イオンを難溶性化合物に変えて不活性化した土
壌を用いた上記(1)の発芽生育培土。 (8)培土化処理した産業廃土に炭素資材を添加して保
水性を高めた土壌を用いた上記(1)の発芽生育培土。 (9)芝の種子を含有する芝生修復用の上記(1)〜
(8)の何れかに記載の発芽生育培土。
According to the present invention, there is provided a germination growth medium having the following constitution. (1) A germinated growth medium which is obtained by subjecting industrial waste soil to soil cultivation treatment, granulating it by adding an amount of fertilizer necessary for initial growth of plants, and drying. (2) The germination growth medium of the above (1), which is obtained by containing plant seeds together with an amount of fertilizer necessary for initial growth of the plant, granulating and drying. (3) The germination and growth medium of (1) above, which is obtained by applying industrial soil to the dredged bottom mud of lakes and harbors, construction residual soil, or wastewater from water purification plants. (4) The hydrogen ion concentration is reduced by adding to the strongly alkaline industrial waste soil an amount of 2 to 12 % of the phosphate absorption coefficient of the waste soil, that is, the superphosphate or the superphosphate. The germination growth medium of the above (1) using acid-enriched soil. (5) The germination growth soil of (1) above, which uses soil in which gypsum is added to industrial waste soil to replace chloride ions in the waste soil and to be leached. (6) The germination and growth medium of the above (1) using a soil in which a calcareous material or a siliceous material is added to industrial waste soil to prevent acidification due to iron sulfide in the waste soil. (7) The germination and growth medium of (1) above, which is prepared by adding lime or lime silicate to industrial waste soil and converting metal ions in the waste soil into sparingly soluble compounds to inactivate the soil. (8) The germination growth culture medium of (1) above, which uses soil in which carbon materials are added to the industrial waste soil that has been treated for soil cultivation to improve water retention. (9) Above (1) for lawn restoration containing turf seeds
The germination growth culture medium according to any one of (8).

【手続補正3】[Procedure 3]

【補正対象書類名】明細書[Document name to be amended] Statement

【補正対象項目名】0007[Correction target item name] 0007

【補正方法】変更[Correction method] Change

【補正内容】[Correction content]

【0007】 産業廃土の具体的な培土化処理を以下に
示す。 (I)建設残土は石灰などを含み強アルカリ性を有する
場合があるが、このような強アルカリ性の産業廃土につ
いては、その水素イオン濃度(pH)を矯正する方法と
して、硫酸等の過激な薬物を使用せずに、過リン酸石灰
や重過リン酸石灰などのリン酸石灰を加え、土壌のpH
を低下させると共に必須栄養源であるリン酸を富化す
る。これらリン酸石灰の添加量は廃土のリン酸吸収係数
の2〜12%相当量が適当であり、このリン酸石灰の添
加により廃土のpHを7〜9に低下させる。培土のpH
がこの範囲であれば植物の生育に支障がない。一般に、
通常の土壌のリン酸吸収係数は1000〜1500であ
るが、建設残土などのように石灰を加えて強アルカリ処
理されたもののリン酸吸収係数は2000前後であり、
建設残土の単位重量(100kg)当たり0.2〜1.
2kg(2〜12%)の過リン酸石灰ないし重過リン酸
石灰を添加することにより、残土のpHが7〜9に矯正
される。
The concrete soil cultivation process of industrial waste soil is shown below. (I) The construction residual soil may contain lime and the like and has strong alkalinity. For such strongly alkaline industrial waste soil, as a method of correcting the hydrogen ion concentration (pH), a radical drug such as sulfuric acid is used. Without using lime, add lime phosphate such as lime superphosphate and lime superphosphate to adjust soil pH.
And enriches phosphate, which is an essential nutrient source. The addition amount of these lime phosphates is appropriately 2 to 12 % of the phosphate absorption coefficient of the waste soil, and the pH of the waste soil is reduced to 7 to 9 by the addition of the lime phosphate. PH of soil
Within this range, there is no hindrance to plant growth. In general,
The phosphoric acid absorption coefficient of normal soil is 1000 to 1500, but the phosphoric acid absorption coefficient of soil that has been treated with strong alkali such as residual soil is around 2000,
0.2-1. Per unit weight (100 kg) of construction soil.
The pH of the residual soil is corrected to 7-9 by adding 2 kg (2-12%) of lime superphosphate or lime superphosphate.

Claims (9)

【特許請求の範囲】[Claims] 【請求項1】産業廃土を培土化処理すると共に植物の初
期生育に必要な量の肥料を含有させて造粒し、乾燥した
発芽生育培土。
1. A germinated growth soil which is obtained by subjecting industrial waste soil to soil cultivation treatment, granulation containing a fertilizer in an amount necessary for initial growth of plants, and drying.
【請求項2】植物の初期生育に必要な量の肥料と共に植
物種子を含有させて造粒し、乾燥した請求項1の発芽生
育培土。
2. The germination and growth medium according to claim 1, which is obtained by incorporating plant seeds together with an amount of fertilizer required for initial plant growth, granulating and drying.
【請求項3】湖沼や港湾の浚渫底泥、建設残土あるいは
浄水場廃土の産業廃土を培土化処理して用いた請求項1
の発芽生育培土。
3. A method for cultivating industrial waste soil such as dredged mud in lakes and harbors, construction residual soil, or wastewater from water purification plants.
Germination growth soil.
【請求項4】強アルカリ性の産業廃土に、該廃土のリン
酸吸収係数の2〜6%相当量の過リン酸石灰ないし重過
リン酸石灰を添加することにより水素イオン濃度を低下
させ、リン酸を富化した土壌を用いた請求項1の発芽生
育培土。
4. The hydrogen ion concentration is reduced by adding to the strongly alkaline industrial waste soil an amount of 2-6% or so of the phosphate absorption coefficient of the waste soil, that is, superphosphate or lime biphosphate. The germination growth medium of claim 1, wherein the soil enriched with phosphoric acid is used.
【請求項5】産業廃土に石膏を添加して廃土中の塩素イ
オンを置換溶脱した土壌を用いた請求項1の発芽生育培
土。
5. The germination and growth soil according to claim 1, which uses soil in which gypsum is added to the industrial waste soil to replace chloride ions in the waste soil and to be leached.
【請求項6】産業廃土に石灰質資材ないしケイ酸質資材
を添加して廃土中の硫化鉄に起因する酸性化を防止した
土壌を用いた請求項1の発芽生育培土。
6. The germination growth soil according to claim 1, wherein a soil in which calcareous material or siliceous material is added to industrial waste soil to prevent acidification due to iron sulfide in the waste soil is used.
【請求項7】産業廃土に石灰ないしケイ酸石灰を添加
し、廃土中の金属イオンを難溶性化合物に変えて不活性
化した土壌を用いた請求項1の発芽生育培土。
7. The germination growth soil according to claim 1, wherein lime or lime silicate is added to the industrial waste soil, and the soil is inactivated by changing the metal ions in the waste soil into a sparingly soluble compound.
【請求項8】培土化処理した産業廃土に炭素資材を添加
して保水性を高めた土壌を用いた請求項1の発芽生育培
土。
8. The germination and growth medium according to claim 1, wherein a soil having an increased water retention capacity is added to the industrial waste soil which has been treated for soil cultivation.
【請求項9】芝の種子を含有する芝生修復用の請求項1
〜8の何れかに記載の発芽生育培土。
9. A lawn restoration containing turf seeds as claimed in claim 1.
The germination growth culture medium according to any one of to 8.
JP6215204A 1994-08-18 1994-08-18 Culture soil for growing germinated plant Pending JPH0860155A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP6215204A JPH0860155A (en) 1994-08-18 1994-08-18 Culture soil for growing germinated plant

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP6215204A JPH0860155A (en) 1994-08-18 1994-08-18 Culture soil for growing germinated plant

Publications (1)

Publication Number Publication Date
JPH0860155A true JPH0860155A (en) 1996-03-05

Family

ID=16668422

Family Applications (1)

Application Number Title Priority Date Filing Date
JP6215204A Pending JPH0860155A (en) 1994-08-18 1994-08-18 Culture soil for growing germinated plant

Country Status (1)

Country Link
JP (1) JPH0860155A (en)

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2006219604A (en) * 2005-02-10 2006-08-24 Ohbayashi Corp Engineering method for improving soil and soil-improving material
JP2007105036A (en) * 2005-09-13 2007-04-26 Chugoku Electric Power Co Inc:The Granular material for agricultural soil
JP2007167077A (en) * 2007-03-22 2007-07-05 Ohbayashi Corp Seedling cultivation system for reed grass

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2006219604A (en) * 2005-02-10 2006-08-24 Ohbayashi Corp Engineering method for improving soil and soil-improving material
JP2007105036A (en) * 2005-09-13 2007-04-26 Chugoku Electric Power Co Inc:The Granular material for agricultural soil
JP2007167077A (en) * 2007-03-22 2007-07-05 Ohbayashi Corp Seedling cultivation system for reed grass
JP4693063B2 (en) * 2007-03-22 2011-06-01 株式会社大林組 Reed seedling system

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