JP2001271067A - Method for improving soil of volcanic soil - Google Patents
Method for improving soil of volcanic soilInfo
- Publication number
- JP2001271067A JP2001271067A JP2000084813A JP2000084813A JP2001271067A JP 2001271067 A JP2001271067 A JP 2001271067A JP 2000084813 A JP2000084813 A JP 2000084813A JP 2000084813 A JP2000084813 A JP 2000084813A JP 2001271067 A JP2001271067 A JP 2001271067A
- Authority
- JP
- Japan
- Prior art keywords
- soil
- volcanic
- ash
- sewage sludge
- 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
Links
Classifications
-
- C—CHEMISTRY; METALLURGY
- C05—FERTILISERS; MANUFACTURE THEREOF
- C05D—INORGANIC FERTILISERS NOT COVERED BY SUBCLASSES C05B, C05C; FERTILISERS PRODUCING CARBON DIOXIDE
- C05D9/00—Other inorganic fertilisers
Landscapes
- Chemical & Material Sciences (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Inorganic Chemistry (AREA)
- Organic Chemistry (AREA)
- Soil Conditioners And Soil-Stabilizing Materials (AREA)
- Fertilizers (AREA)
- Cultivation Of Plants (AREA)
- Processing Of Solid Wastes (AREA)
- Treatment Of Sludge (AREA)
Abstract
Description
【0001】[0001]
【発明の属する技術分野】我が国は世界有数の火山国で
あり、火山噴出物が堆積した火山性土壌が全国に広く分
布している。火山性土壌は火山灰、火山レキ、軽石およ
びこれらの風化物などから形成されており、この土壌
は、植物の養分であるアンモニア、カリウム、カルシウ
ム、マグネシウムなどの陽イオンを保持する能力が極め
て低く、肥沃度が劣悪なものが多い。本発明では、従
来、廃棄物扱いされ、今後、発生量の増加が予測される
炉内脱硫方式流動床石炭ボイラー灰と下水汚泥の造粒物
によって、火山性土壌の改良を行い、植物の生育に適し
た改良土壌を提供するものである。BACKGROUND OF THE INVENTION Japan is one of the world's leading volcanic countries, and the volcanic soil on which volcanic products are deposited is widely distributed throughout the country. Volcanic soil is formed from volcanic ash, volcanic rubble, pumice and their weathered materials, etc., and this soil has extremely low ability to retain cations such as ammonia, potassium, calcium, magnesium, which are the nutrients of plants, Many have poor fertility. In the present invention, the volcanic soil is improved by the in-furnace desulfurization type fluidized bed coal boiler ash and sewage sludge, which are conventionally treated as waste and the amount of generation is expected to increase in the future. The purpose of the present invention is to provide an improved soil suitable for soil.
【0002】[0002]
【従来の技術】火山性土壌は火山灰、火山レキ、軽石お
よびこれらの風化物などから形成されているが、この土
壌は植物の養分であるアンモニア、カリウム、カルシウム、
マグネシウムなどの陽イオンを保持する能力効力が極め
て低く、植物の生育には適していない。すなわち、硫安
などの肥料を施用して土壌の肥沃度を高めようとして
も、土壌の陽イオン保持力が弱いため、用水、灌漑水、雨
水などで養分である陽イオンが簡単に流出してしまう。2. Description of the Related Art Volcanic soils are formed from volcanic ash, volcanic rocks, pumice stones and their weathered materials. This soil is composed of ammonia, potassium, calcium,
The ability to retain cations such as magnesium is extremely low and is not suitable for plant growth. In other words, even if fertilizers such as ammonium sulfate are applied to increase the fertility of the soil, the cations, which are nutrients, can easily flow out of the water, irrigation water, rainwater, etc. due to the weak cation retention of the soil. .
【0003】この火山性土壌の改良方法としては、植物
養分の陽イオンの保持力を増大させる方法として、従来か
ら天然ゼオライト系土壌改良材が用いられている。最近
では人工ゼオライトを土壌改良材として用いる例があ
る。また、ベントナイト系土壌改良材も用いられてい
る。As a method for improving the volcanic soil, a natural zeolite-based soil improving material has been conventionally used as a method for increasing cation retention of plant nutrients. Recently, there is an example in which artificial zeolite is used as a soil conditioner. In addition, bentonite soil conditioners are also used.
【0004】天然ゼオライト系土壌改良材では、天然ゼ
オライトが有効成分となっており、地力増進法で土壌改
良資材として認められているものである。天然に産出す
るこのゼオライトは陽イオン交換容量(CEC)が130〜150m
eq/100g程度である。このCECに起因する陽イオン保持力
によって、肥料養分である陽イオンの流出を防止でき、施
肥効果を高めるものである。しかし、この天然ゼオライ
トは原石を採掘・粉砕、場合によっては焼成して製造す
るものであるため、高価となる欠点がある。[0004] Natural zeolite-based soil improving materials are natural zeolite as an active ingredient, and are recognized as soil improving materials by the soil enhancement method. This naturally occurring zeolite has a cation exchange capacity (CEC) of 130-150 m
It is about eq / 100g. The cation holding power caused by the CEC can prevent the cations, which are fertilizer nutrients, from flowing out and enhance the fertilizing effect. However, since this natural zeolite is produced by mining and pulverizing a raw ore and, in some cases, firing it, it has a disadvantage of being expensive.
【0005】人工ゼオライトは特開昭59-86687号公報に
記載のように、石炭灰に水酸化ナトリウム水溶液を加
え、加熱反応させゼオライトを合成するものであり、土
壌改良材としての効果は天然ゼオライトに比較して高
い。CEC値は高く、250meq/100g程度である。しかし、こ
の人工ゼオライトはゼオライト合成反応を進めるため、
化学薬品である水酸化ナトリウムを使用するので天然ゼ
オライトよりも更に高価となる欠点がある。[0005] As described in JP-A-59-86687, an artificial zeolite is one in which an aqueous solution of sodium hydroxide is added to coal ash to cause a heat reaction to synthesize zeolite. Higher than. The CEC value is high, around 250meq / 100g. However, this artificial zeolite promotes the zeolite synthesis reaction,
The disadvantage is that the use of the chemical sodium hydroxide is more expensive than natural zeolites.
【0006】ベントナイト系土壌改良材は、天然に産出
するベントナイトを有効成分とするものであり、ベント
ナイトの膨潤性を利用して、水に溶けている陽イオンな
どの養分を保持し、施肥効果を高める。しかし、採掘・
粉砕の製造工程が必要で、これも高価となる。また、ベ
ントナイト系土壌改良材を多用すると、土壌の透水性が
悪化する欠点もある。[0006] Bentonite soil amendments contain naturally occurring bentonite as an active ingredient, and utilize the swelling properties of bentonite to retain nutrients such as cations dissolved in water and improve the fertilizing effect. Enhance. However, mining
A pulverizing manufacturing process is required, which is also expensive. Further, when the bentonite-based soil conditioner is frequently used, there is a disadvantage that the water permeability of the soil is deteriorated.
【0007】また、上記の従来の技術である土壌改良材
は、いずれも肥料ではなく、施肥効果を高める資材であ
り、この土壌改良材とは別に肥料そのものを施す必要が
ある。[0007] Further, the above-mentioned conventional soil improving materials are not fertilizers but materials for enhancing the fertilizing effect, and it is necessary to apply fertilizers separately from the soil improving materials.
【0008】以上のように、全国に広く分布する火山性
土壌を安価に、植物の生育に適した土壌に改良する方法
の開発が強く望まれている。As described above, development of a method for improving volcanic soil widely distributed throughout the country at low cost into soil suitable for plant growth is strongly desired.
【0009】[0009]
【発明が解決しようとする課題】本発明は、従来、廃棄
物扱いされている炉内脱硫方式流動床石炭ボイラー灰と
下水汚泥の有効利用を図ると同時に、保肥力が殆どない
火山灰土壌に施用し、植物の生育に適した土壌改良方法
を安価に提供するものである。DISCLOSURE OF THE INVENTION The present invention aims at effectively utilizing in-furnace desulfurization type fluidized bed coal boiler ash and sewage sludge which are conventionally treated as waste, and at the same time, is applied to volcanic ash soil which has almost no fertilizing capacity. In addition, the present invention provides an inexpensive soil improvement method suitable for plant growth.
【0010】[0010]
【課題を解決するための手段】本発明者らは、火山性土
壌の改良方法について、鋭意検討した結果、炉内脱硫方
式流動床石炭ボイラー灰と下水汚泥を造粒した有機性肥
料あるいは土壌改良材を、火山性土壌に適用することに
より、肥沃な土壌に改良できることを見出し、本発明を
完成するに至った。Means for Solving the Problems The present inventors have conducted intensive studies on a method for improving volcanic soil, and as a result, have found that an organic fertilizer obtained by granulating desulfurization type fluid bed coal boiler ash and sewage sludge in a furnace or soil improvement. It has been found that by applying the timber to a volcanic soil, it can be improved to a fertile soil, and the present invention has been completed.
【0011】[0011]
【発明の実施の形態】本発明の炉内脱硫方式流動床石炭
ボイラー、下水汚泥、火山性土壌について説明する。DESCRIPTION OF THE PREFERRED EMBODIMENTS The in-furnace desulfurization type fluidized bed coal boiler, sewage sludge and volcanic soil of the present invention will be described.
【0012】流動床石炭ボイラーは、ベッド材と呼ばれ
る細かい粒子と燃料である微粉石炭が高速の燃焼ガス中
に流動した状態で運転される方式のボイラーである。こ
の方式では、燃焼室部に細粒の石灰石を供給することで
燃焼ガスの脱硫を行なうことができる。その反応を次に
示す。これが炉内脱硫方式流動床石炭ボイラーである。 燃料中のイオウ分の燃焼: S + O2 → SO2 石灰石の生石灰への反応: CaCO3 → CaO + CO2 脱硫反応 : CaO + SO2 1/2O2 → CaSO4 下水汚泥は、人糞、尿の処理施設で発生する汚泥であ
り、初沈汚泥、活性汚泥、混合汚泥及びこれらの消化汚
泥である。真空脱水濾過、加圧濾過、遠心分離脱水、ベ
ルトプレス脱水、スクリュウプレス脱水、多重円盤型脱
水などの汚泥の脱水処理型式の制約は特にない。A fluidized-bed coal boiler is a boiler operated in a state where fine particles called a bed material and fine coal which is a fuel flow in a high-speed combustion gas. In this method, the combustion gas can be desulfurized by supplying fine limestone to the combustion chamber. The reaction is shown below. This is an in-furnace desulfurization type fluidized bed coal boiler. Combustion of sulfur in fuel: S + O 2 → SO 2 Reaction of limestone to quicklime: CaCO 3 → CaO + CO 2 desulfurization reaction: CaO + SO 2 1/2 O 2 → CaSO 4 It is sludge generated in a urine treatment facility, and is primary sludge, activated sludge, mixed sludge and digestion sludge of these. There is no particular restriction on the sludge dewatering treatment type such as vacuum dewatering filtration, pressure filtration, centrifugal dewatering, belt press dewatering, screw press dewatering, and multiple disk dewatering.
【0013】火山性土壌とは、火山レキ、火山灰、軽石
及びこれらの風化物が主体となって堆積している土壌を
いう。炉内脱硫方式流動床石炭ボイラー灰と下水汚泥と
の混合造粒物の粒子径は、土壌改良材としての施用作業
性の観点から、20mm以下が好ましい。[0013] Volcanic soil refers to volcanic rock, volcanic ash, pumice, and soils mainly composed of these weathered materials. The particle size of the mixed granulated product of the in-furnace desulfurization type fluidized bed coal boiler ash and sewage sludge is preferably 20 mm or less from the viewpoint of application workability as a soil improvement material.
【0014】[0014]
【実施例】以下、本発明を実施例で詳細に説明する。火
山灰土壌としては、図1に示す植物の生育に不適な地層
である原野を選定した。この地点は、近くに火山と海岸
があり、地表から約5m以上の深さでは、砂を主成分と
する層と火山噴出物層が交互に層を成している。地表か
ら5m深さまでは、極く薄い表層土(0.1〜0.5m程度)、そ
の下に、直近の火山噴火による降下軽石層が形成されて
いる(0.5〜2.0m程度)。The present invention will be described below in detail with reference to examples. As the volcanic ash soil, a wilderness which is an unsuitable stratum for plant growth shown in FIG. 1 was selected. At this point, there are volcanoes and coasts nearby, and at a depth of about 5 m or more from the surface, layers composed mainly of sand and layers of volcanic products are formed alternately. At a depth of 5 m below the surface, a very thin surface soil (approximately 0.1-0.5 m) is formed underneath, and a pumice fall layer due to a recent volcanic eruption is formed (approximately 0.5-2.0 m).
【0015】生石灰を4%以上含有する炉内脱硫方式流動
床石炭ボイラー灰と水分45%の乾燥下水汚泥(北海道A市
下水処理場から入手した活性汚泥処理後の下水汚泥)と
を固形重量比1000:100で十分の混合後、水を重量比で40
0加え、逆流式高速造粒機で造粒し、粒子径1.0〜9.0mm
のものを得た。これを実施例で使用した。Fluid bed coal boiler ash containing 4% or more quicklime in a furnace and dry sewage sludge having a moisture content of 45% (activated sewage sludge obtained from sewage treatment plant in A city, Hokkaido A) After mixing well at 1000: 100, water is added at a weight ratio of 40
0 Addition, granulation with backflow high-speed granulator, particle size 1.0-9.0mm
Got something. This was used in the examples.
【0016】実施例1では、図1に示した火山灰土壌の
上に3mの厚さで造粒物をブルドーザーで堆積させた。そ
の構造を図2に示した。実施例2では、図1の火山灰土
壌を1mの深さで剥がし、これと上記の造粒物3m深さ分を
土木工事用スタビライザーで混合し、剥がした部分へ戻
した。その構造を図3に示した。In Example 1, a granulated material having a thickness of 3 m was deposited on the volcanic ash soil shown in FIG. 1 with a bulldozer. Its structure is shown in FIG. In Example 2, the volcanic ash soil shown in FIG. 1 was peeled off at a depth of 1 m, and the above-mentioned granulated material at a depth of 3 m was mixed with a civil engineering stabilizer and returned to the peeled off portion. The structure is shown in FIG.
【0017】実施例3では、図1の火山灰土壌を1m深さ
で剥がし、これと上記の造粒物1m深さ分とを十分の混合
し、剥がした部分へ戻した。次いで、その1m深さ分を剥
がし、造粒物と混合後、剥がした部分へ戻した。最後に
この作業をもう一度繰り返し、表層ほど造粒物含量が多
い構造とした。図4に構造を示した。In Example 3, the volcanic ash soil shown in FIG. 1 was peeled off at a depth of 1 m, and this was thoroughly mixed with the above-mentioned granulated material at a depth of 1 m, and returned to the peeled portion. Next, the 1 m depth was peeled off, mixed with the granulated material, and returned to the peeled portion. Finally, this operation was repeated once more to obtain a structure in which the surface layer had a higher content of granules. FIG. 4 shows the structure.
【0018】元の火山灰土壌を比較例とした。これと実
施例1〜3の改良土壌において、牧草の種子(品種はホ
クオウ)を散布し、牧草の生育試験を行い、収量を測定
した結果、実施例1〜3の改良土壌において、顕著な牧
草収量の増加を確認した。結果を表1に示した。The original volcanic ash soil was used as a comparative example. This and the improved soil of Examples 1 to 3 were sprayed with grass seeds (variety: Hokuou), and a growth test of the grass was performed. As a result, the yield was measured. An increase in yield was confirmed. The results are shown in Table 1.
【0019】[0019]
【表1】 [Table 1]
【0020】[0020]
【発明の効果】本発明の技術は、廃棄物である炉内脱硫
方式流動床石炭ボイラー灰と下水汚泥とから製造した造
粒物を火山性土壌上へ層状に堆積させるか、火山性土壌
とを混合することにより植物の生育に適した肥沃な土壌
に改良するものであり、廃棄物の有効利用による環境保
全に貢献すると同時に、農林業用の安価な土壌改良方法
を提供するという極めて価値の高い技術である。According to the technology of the present invention, the granules produced from in-furnace desulfurization type fluidized bed coal boiler ash and sewage sludge, which are wastes, are deposited in layers on volcanic soil, or To improve fertile soil suitable for plant growth by contributing to the conservation of the environment through effective use of waste, and at the same time to provide an inexpensive soil improvement method for agriculture and forestry. High technology.
【図1】 火山灰土壌の地層状況を示す図である。FIG. 1 is a diagram showing a stratum of volcanic ash soil.
【図2】 実施例1の土壌構造を示す図である。FIG. 2 is a diagram showing a soil structure of Example 1.
【図3】 実施例2の土壌構造を示す図である。FIG. 3 is a diagram showing a soil structure of Example 2.
【図4】 実施例3の土壌構造を示す図である。FIG. 4 is a view showing a soil structure according to a third embodiment.
フロントページの続き (51)Int.Cl.7 識別記号 FI テーマコート゛(参考) // B09B 3/00 ZAB B09B 3/00 301M 301 (C05G 1/00 (C05G 1/00 C05D 3:02 C05D 3:02 C05F 7:00) C05F 7:00) C09K 101:00 C09K 101:00 B09B 3/00 ZAB (72)発明者 松原 稔 北海道苫小牧市勇払143 日本製紙株式会 社勇払工場内 Fターム(参考) 2B022 AA05 BA02 BA05 BA13 BB01 DA19 4D004 AA02 AA36 AC04 BA04 BA10 CA14 CA15 CB50 4D059 AA02 AA04 AA05 AA23 BE14 BE15 BE16 BE26 BE27 BE38 BK09 CC01 CC10 DA64 4H026 AA01 AA18 4H061 AA01 AA04 CC07 CC51 FF08 GG26 GG41 HH01 LL07 Continued on the front page (51) Int.Cl. 7 Identification symbol FI Theme coat II (for reference) // B09B 3/00 ZAB B09B 3/00 301M 301 (C05G 1/00 (C05G 1/00 C05D 3:02 C05D 3: 02 C05F 7:00) C05F 7:00) C09K 101: 00 C09K 101: 00 B09B 3/00 ZAB (72) Inventor Minoru Matsubara 143 Yufutsu, Tomakomai City, Hokkaido F Term in the Yufutsu Mill of Nippon Paper Co., Ltd. (Reference) 2B022 AA05 BA02 BA05 BA13 BB01 DA19 4D004 AA02 AA36 AC04 BA04 BA10 CA14 CA15 CB50 4D059 AA02 AA04 AA05 AA23 BE14 BE15 BE16 BE26 BE27 BE38 BK09 CC01 CC10 DA64 4H026 AA01 AA18 4H061 AA01 GG04 GG07 CG07 LLCC
Claims (4)
水汚泥を混合造粒した有機性肥料あるいは土壌改良材
を、火山性土壌の上に1〜3mの厚さで堆積させ、肥料
成分に富み植物の生育に適した改良土壌を形成すること
を特徴とする土壌改良方法。1. An organic fertilizer or a soil improving material obtained by mixing and granulating an in-furnace desulfurization type fluidized bed coal boiler ash and sewage sludge in a thickness of 1 to 3 m on a volcanic soil to form a fertilizer component. A soil improvement method comprising forming an improved soil suitable for growing rich plants.
これと、炉内脱硫方式流動床石炭ボイラー灰と下水汚泥
を混合造粒した有機性肥料あるいは土壌改良材の1〜3
m厚さ分とを、混合後、表層を剥がした部分に堆積さ
せ、肥料成分に富み植物の生育に適した改良土壌を形成
することを特徴とする土壌改良方法。2. Peeling off 1 m from the surface layer of the volcanic soil,
And an organic fertilizer or soil improvement material obtained by mixing and granulating the fluidized-bed coal boiler ash and sewage sludge in a furnace desulfurization method.
a soil thickness of m with a thickness of m, which is then deposited on a portion where the surface layer has been peeled off to form an improved soil which is rich in fertilizer components and suitable for growing plants.
これと、炉内脱硫方式流動床石炭ボイラー灰と下水汚泥
を混合造粒した有機性肥料あるいは土壌改良材の1m厚
さ分とを、混合後、表層を剥がした部分に堆積させる。
これを1〜3回繰り返し、表層に近いほど肥料成分に富
むように工夫した植物の生育に適した改良土壌を形成す
ることを特徴とする土壌改良方法。3. Peeling off 1 m from the surface layer of the volcanic soil,
This is mixed with an in-furnace desulfurization type fluidized bed coal boiler ash and sewage sludge, which are mixed and granulated with an organic fertilizer or a soil improver having a thickness of 1 m, and then deposited on the portion where the surface layer has been peeled off.
A soil improvement method comprising repeating this one to three times to form an improved soil suitable for growing a plant devised so that the closer to the surface layer, the richer the fertilizer component is.
び又は火山レキおよび又は軽石および又はこれらの風化
物であることを特徴とする請求項1、2又は3いずれか
記載の土壌改良方法。4. The soil improvement method according to claim 1, wherein the main component of the volcanic soil is volcanic ash and / or volcanic rubble and / or pumice and / or weathered material thereof.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP2000084813A JP2001271067A (en) | 2000-03-24 | 2000-03-24 | Method for improving soil of volcanic soil |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP2000084813A JP2001271067A (en) | 2000-03-24 | 2000-03-24 | Method for improving soil of volcanic soil |
Publications (1)
Publication Number | Publication Date |
---|---|
JP2001271067A true JP2001271067A (en) | 2001-10-02 |
Family
ID=18601241
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP2000084813A Pending JP2001271067A (en) | 2000-03-24 | 2000-03-24 | Method for improving soil of volcanic soil |
Country Status (1)
Country | Link |
---|---|
JP (1) | JP2001271067A (en) |
Cited By (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN1333042C (en) * | 2005-01-21 | 2007-08-22 | 清华大学 | Use of desulfurized waste material of coal-burning smoke and method for modifying alkali soil by same |
RU2571634C2 (en) * | 2014-01-20 | 2015-12-20 | Федеральное Государственное Бюджетное Образовательное Учреждение Высшего Профессионального Образования "Чеченский Государственный Университет" | Bio-organic-mineral complex (bomc) |
CN109041627A (en) * | 2018-09-06 | 2018-12-21 | 南充市嘉陵区黄家楼优土生态种养专业合作社 | A method of it is quickly organised using Jujun grasses and sandstone soil property is transformed |
Citations (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPH04104736A (en) * | 1990-08-24 | 1992-04-07 | Electric Power Dev Co Ltd | Fly ash-containing culture medium material for plant |
-
2000
- 2000-03-24 JP JP2000084813A patent/JP2001271067A/en active Pending
Patent Citations (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPH04104736A (en) * | 1990-08-24 | 1992-04-07 | Electric Power Dev Co Ltd | Fly ash-containing culture medium material for plant |
Cited By (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN1333042C (en) * | 2005-01-21 | 2007-08-22 | 清华大学 | Use of desulfurized waste material of coal-burning smoke and method for modifying alkali soil by same |
RU2571634C2 (en) * | 2014-01-20 | 2015-12-20 | Федеральное Государственное Бюджетное Образовательное Учреждение Высшего Профессионального Образования "Чеченский Государственный Университет" | Bio-organic-mineral complex (bomc) |
CN109041627A (en) * | 2018-09-06 | 2018-12-21 | 南充市嘉陵区黄家楼优土生态种养专业合作社 | A method of it is quickly organised using Jujun grasses and sandstone soil property is transformed |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
CN107466512B (en) | Structure and method for comprehensively treating saline-alkali soil by adopting solid wastes | |
CN107241926A (en) | A kind of method for improveing Saline Ground in Xinjiang | |
CN109608278A (en) | A kind of formula and preparation method thereof of mine material reparation | |
Korcak | Agricultural uses of coal combustion byproducts | |
Girijaveni et al. | Zeolites are emerging soil amendments for improving soil physical and chemical properties in agriculture: A review | |
KR101863044B1 (en) | Greening Soil Stabilizer and Greening Method | |
CN112624857A (en) | Ecological restoration base material for restoring mine wasteland and preparation method thereof | |
JP2001271067A (en) | Method for improving soil of volcanic soil | |
US11952319B2 (en) | Selecting and applying metal oxides and clays for plant growth | |
CN107879855A (en) | Building waste saline land greening tree planting soil conditioner | |
CN107739619A (en) | Diatomite mine tailing saline land greening tree planting soil conditioner | |
CN101525258A (en) | Soil phosphorus activator and manufacturing method thereof | |
CN108463446A (en) | Granulated fertilizer or soil conditioner and application thereof | |
CN113387751B (en) | Alkaline functional fertilizer and preparation method and application thereof | |
KR101692825B1 (en) | Artificial soil comprising dry bottom/middle ash and the manufacturing method of the same | |
JP2010137219A (en) | Saponin-containing granule or saponin-containing fired granule, and method for producing the same | |
JP3707051B2 (en) | Flooded slope greening spray material, its spraying method, flooded slope created by the method, and water supply network used in the method | |
Louhar | Zeolites: A potential source of soil amendments to improve soil properties | |
JP4387040B2 (en) | Soil improver and / or organic fertilizer and method for producing the same | |
Eteng | Temporal variations in micronutrients (Cu, Fe, Mn and Zn) mineralization as influenced by animal and plant manure-amended marginal soils, Southeastern Nigeria | |
Nayak et al. | Management of fly ash for sustainable soil health | |
US20240199503A1 (en) | Selecting and applying metal oxides and clays for plant growth | |
CN107903137A (en) | Illite tailing saline land greening tree planting soil conditioner | |
Ritchey et al. | Potential for utilizing coal combustion residues in co-utilization products | |
JP2007161975A (en) | Novel method for using pelytes of geological ages including the mesozoic jurassic period and periods prior to the same |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
A621 | Written request for application examination |
Free format text: JAPANESE INTERMEDIATE CODE: A621 Effective date: 20070228 |
|
A977 | Report on retrieval |
Free format text: JAPANESE INTERMEDIATE CODE: A971007 Effective date: 20100426 |
|
A131 | Notification of reasons for refusal |
Free format text: JAPANESE INTERMEDIATE CODE: A131 Effective date: 20100517 |
|
A02 | Decision of refusal |
Free format text: JAPANESE INTERMEDIATE CODE: A02 Effective date: 20101001 |