JP5002096B2 - Recycled fertilizer and soil conditioner - Google Patents
Recycled fertilizer and soil conditioner Download PDFInfo
- Publication number
- JP5002096B2 JP5002096B2 JP2001243342A JP2001243342A JP5002096B2 JP 5002096 B2 JP5002096 B2 JP 5002096B2 JP 2001243342 A JP2001243342 A JP 2001243342A JP 2001243342 A JP2001243342 A JP 2001243342A JP 5002096 B2 JP5002096 B2 JP 5002096B2
- Authority
- JP
- Japan
- Prior art keywords
- asbestos
- fertilizer
- waste
- soil conditioner
- melting
- 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
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Landscapes
- Processing Of Solid Wastes (AREA)
- Soil Conditioners And Soil-Stabilizing Materials (AREA)
- Fertilizers (AREA)
Description
【0001】
【発明の属する技術分野】
本発明は、アスベストを含有する無機系建材の廃棄物を熔融して、アスベストを不在化したリサイクル肥料兼土壌改良材を得るものである。
【0002】
【従来の技術】
クリソタイルを代表とするアスベストを含有する建材は30年以上に亘り、住宅及び非住宅の建物の屋根材や壁材として多く使われており、特にその廃棄物については未だに有効な処理法が確立されていなかった。
【0003】
例えば、アスベスト建材の廃棄物処理方法としては、大きな塊のままで最終処理する等の処理が行われているにすぎない。
【0004】
【発明が解決しようとする課題】
アスベストを含む建材は有効な処理方法がないままに放置され、具体的かつ有効かつ有益な処理方法が望まれている。
【0005】
一方では、イネ科植物、特にイネのケイ化細胞を増加させ、耐病、耐虫性、耐倒伏性などを高める有用な肥料としてけい酸質肥料が注目され、また、酸性雨等の影響を受けた土壌を改良するためのアルカリ分の補給が可能な肥料や土壌改良材が要求されている。
【0006】
【課題を解決するための手段】
本発明ではアスベストを含有する無機系建材の廃棄物を熔融することにより、アスベストを不在化し、該廃棄物に含まれるケイ酸やマグネシウム等を利用し、けい酸質のリサイクル肥料、兼けい酸とアルカリ分を補給する土壌改良材を得る。
【0007】
【発明の実施の形態】
本発明に用いるアスベストを含有する無機系建材は、セメント及びケイ酸カルシウムの少なくとも一つとアスベストとから、主に構成される無機系建材で、ニッケル、クロム、チタン等の有害な成分をほとんど含まないものであり、例えば、平型彩色スレート、波型スレート、スレート、ケイ酸カルシウム板、スラグせっこう板、窯業系サイディングなどである。また、これらは主に取り替えや建て替えに伴って発生するアスベスト含有の屋根材や壁材の廃棄物を前提にしているが、当然、使用されずに廃棄されるものも含まれる。
【0008】
一般的に、アスベストを単独で熔融するには1500℃以上の加熱温度が必要であり、従来の炉を用いてアスベストを熔融することは困難であるが、熔融助剤等を用いることでアスベストの熔融温度を下げることができる。
【0009】
本発明では、アスベストを含有する無機系建材の廃棄物を熔融させるものであり、該廃棄物には熔融助剤となるケイ酸化合物あるいはアルカリ土金属等が含まれている場合が多いので、1500℃以下で熔融することも可能である。また、含まれる熔融助剤が少ない場合には、他に熔融助剤、例えばガラス廃材等を加えることで熔融温度を下げることも可能である。
【0010】
もちろん、熔融温度の設定は燃料コスト、作業性、設備等を考慮して決定されるものである。熔融の方法としては種々あるが、外熱式電気炉、アーク炉、高周波加熱炉に代表される電気炉、平炉に代表される燃焼ガス炉等である。しかし、燃料コスト等を考慮すれば、廃棄物をある程度の大きさに破砕してから熔融してもよい。
【0011】
熔融に要する時間は特に限定しないが、少なくとも建材廃棄物に含まれるアスベストが熔融していればよく、建材廃棄物の大きさ、重ね方、化学成分等により決定されるものである。
【0012】
熔融後は水等を用いて急冷または徐冷する、例えば、水を用いて急冷すると熔融体が水砕されて粒状体が得られるので、後工程となる粉砕、破砕等を省略することも可能である。もちろん、徐冷後に後工程で粉砕、破砕等してもよいし、必要に応じて、次の工程で粒度を調整するために粉砕、破砕等や造粒等をおこなってもよい。
【0013】
得られた熔融体にはアスベストが不在であり、また、可溶性けい酸とアルカリ分は普通肥料の公定規格のけい酸質肥料に適合するものであり、さらにマグネシウム成分である苦土も含まれている。
【0014】
また、例えば石灰分が必要であれば生石灰、消石灰等の少なくとも一つを添加して調整することが可能であり、さらに他の肥料の有効成分を添加することも可能である、特に、造粒の過程で添加して造粒物とするのも良い。
【0015】
(実施例)
アスベスト含有建材廃棄物(商品名コロニアル:表1組成)を1000℃で15分間焼成し、次にピンミルで粉砕し、その粉砕物約50gを、約1500℃で30分間加熱し、熔融後、直ぐに水に入れて急冷し、その急速冷却熔融物の水分除去後にポットミルにて4時間かけて粉砕した。得られた粉状体を肥料分析すると、表1に示すように、アルカリ分35.2%、可溶性けい酸26.2%であり、けい酸質肥料として公定規格に適合する数値であった。また、可溶性苦土が6.2%なので、可溶性苦土を保証した混合石灰肥料としても適合する数値である。
【表1】
【0016】
【発明の効果】
本願発明によれば、▲1▼アスベスト含有建材廃棄物を容易にリサイクルできる、▲2▼健康に有害であると言われているアスベストを不在化できる、▲3▼廃棄物を肥料や土壌改良材としてリサイクルできるので需要が莫大である、▲4▼肥料としては、けい酸質肥料だけでなく、混合石灰肥料として可溶性苦土も保証することもできる、等々の特徴、効果がある。[0001]
BACKGROUND OF THE INVENTION
The present invention is to obtain a recycled fertilizer and soil improving material in which asbestos is absent by melting inorganic building material waste containing asbestos.
[0002]
[Prior art]
Building materials containing asbestos, such as chrysotile, have been widely used as roofing and wall materials for residential and non-residential buildings for over 30 years. In particular, effective treatment methods for waste have been established. It wasn't.
[0003]
For example, as a waste disposal method for asbestos building materials, a process such as a final process is merely performed in a large lump.
[0004]
[Problems to be solved by the invention]
Building materials containing asbestos are left without an effective treatment method, and a concrete, effective and useful treatment method is desired.
[0005]
On the other hand, siliceous fertilizers are attracting attention as useful fertilizers that increase the silicic cells of rice plants, especially rice, and increase disease resistance, insect resistance, lodging resistance, etc., and are also affected by acid rain. There is a demand for fertilizers and soil amendments that can be replenished with alkali to improve soil.
[0006]
[Means for Solving the Problems]
In the present invention, asbestos is made absent by melting waste of inorganic building materials containing asbestos, and silicic acid, magnesium, etc. contained in the waste are used, silicic acid recycled fertilizer , and silicic acid. Obtain a soil amendment that replenishes alkalinity.
[0007]
DETAILED DESCRIPTION OF THE INVENTION
Inorganic building materials containing asbestos used in the present invention, the at least one and asbestos cement and calcium silicate, mainly constituted inorganic building materials, containing little nickel, chromium, harmful components such as titanium For example, flat color slate, corrugated slate, slate, calcium silicate board, slag gypsum board, ceramic siding, etc. Moreover, although these presuppose the asbestos-containing roof material and wall material waste which generate | occur | produce mainly with replacement | exchange or rebuilding, naturally the thing discarded without being used is also included.
[0008]
In general, in order to melt asbestos alone, a heating temperature of 1500 ° C. or higher is necessary, and it is difficult to melt asbestos using a conventional furnace. The melting temperature can be lowered.
[0009]
In the present invention, waste of inorganic building materials containing asbestos is melted, and since the waste often contains a silicate compound or an alkaline earth metal as a melting aid, 1500 It is also possible to melt at a temperature below ℃. In addition, when the amount of the melting aid contained is small, it is possible to lower the melting temperature by adding a melting aid such as a glass waste material.
[0010]
Of course, the setting of the melting temperature is determined in consideration of fuel cost, workability, equipment, and the like. There are various melting methods, such as an external heating electric furnace, an arc furnace, an electric furnace represented by a high-frequency heating furnace, a combustion gas furnace represented by a flat furnace, and the like. However, considering the fuel cost and the like, the waste may be crushed to a certain size and then melted .
[0011]
Although the time required for melting is not particularly limited, it is sufficient that at least asbestos contained in the building material waste is melted, and is determined by the size of the building material waste, how it is stacked, chemical components, and the like.
[0012]
After melting, quench or slowly cool with water, etc. For example, when quenching with water, the melt is crushed and granulates are obtained. It is. Of course, after slow cooling, it may be pulverized, crushed or the like in a later step, and if necessary, pulverized, crushed, granulated or the like may be performed in order to adjust the particle size in the next step.
[0013]
The resulting melt is free of asbestos, soluble silicic acid and alkali content are compatible with the official silicic fertilizers of ordinary fertilizers, and also includes magnesium, which is a magnesium component. Yes.
[0014]
In addition, for example, if lime content is necessary, it is possible to adjust by adding at least one of quick lime, slaked lime, etc., and further, it is possible to add other active ingredients of fertilizer, especially granulation It may be added in the process of making a granulated product.
[0015]
(Example)
Asbestos-containing building material waste (trade name Colonial: Table 1 composition) is fired at 1000 ° C. for 15 minutes, then pulverized by a pin mill, and about 50 g of the pulverized product is heated at about 1500 ° C. for 30 minutes. The mixture was rapidly cooled in water and pulverized in a pot mill for 4 hours after removing moisture from the rapidly cooled melt. As shown in Table 1, when the obtained powder was analyzed for fertilizer, it had an alkali content of 35.2% and soluble silicic acid of 26.2%, which was a numerical value meeting the official standard as a siliceous fertilizer. Moreover, since soluble magnesia is 6.2%, it is a numerical value suitable also as mixed lime fertilizer which guaranteed soluble magnesia.
[Table 1]
[0016]
【Effect of the invention】
According to the present invention, (1) asbestos-containing building material waste can be easily recycled, (2) asbestos, which is said to be harmful to health, can be absent, (3) fertilizer and soil improver As a fertilizer, it is possible to guarantee not only siliceous fertilizer but also soluble bitter soil as a mixed lime fertilizer, and so on.
Claims (1)
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP2001243342A JP5002096B2 (en) | 2001-08-10 | 2001-08-10 | Recycled fertilizer and soil conditioner |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP2001243342A JP5002096B2 (en) | 2001-08-10 | 2001-08-10 | Recycled fertilizer and soil conditioner |
Publications (2)
Publication Number | Publication Date |
---|---|
JP2003055072A JP2003055072A (en) | 2003-02-26 |
JP5002096B2 true JP5002096B2 (en) | 2012-08-15 |
Family
ID=19073456
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
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JP2001243342A Expired - Fee Related JP5002096B2 (en) | 2001-08-10 | 2001-08-10 | Recycled fertilizer and soil conditioner |
Country Status (1)
Country | Link |
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JP (1) | JP5002096B2 (en) |
Family Cites Families (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPS62237984A (en) * | 1986-04-08 | 1987-10-17 | Meisei Kogyo Kk | Waste materials treatment for asbestos-containing substance |
JPH01270583A (en) * | 1988-04-18 | 1989-10-27 | Iida Kogyosho:Kk | Granular fertilizer and production thereof |
JPH0321387A (en) * | 1989-06-19 | 1991-01-30 | Nippon Pillar Packing Co Ltd | Antipollution treatment of waste asbestos |
-
2001
- 2001-08-10 JP JP2001243342A patent/JP5002096B2/en not_active Expired - Fee Related
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Publication number | Publication date |
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JP2003055072A (en) | 2003-02-26 |
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