JP2003055072A - Recycled fertilizer and soil conditioner - Google Patents
Recycled fertilizer and soil conditionerInfo
- Publication number
- JP2003055072A JP2003055072A JP2001243342A JP2001243342A JP2003055072A JP 2003055072 A JP2003055072 A JP 2003055072A JP 2001243342 A JP2001243342 A JP 2001243342A JP 2001243342 A JP2001243342 A JP 2001243342A JP 2003055072 A JP2003055072 A JP 2003055072A
- Authority
- JP
- Japan
- Prior art keywords
- fertilizer
- asbestos
- soil conditioner
- wastes
- recycled
- 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.)
- Granted
Links
Landscapes
- Processing Of Solid Wastes (AREA)
- Soil Conditioners And Soil-Stabilizing Materials (AREA)
- Fertilizers (AREA)
Abstract
Description
【発明の詳細な説明】
【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及び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及びけ
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焼成して
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、アスベスト含有建
材廃棄物を容易にリサイクルできる、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、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、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。Description: BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method for melting a waste of an inorganic building material containing asbestos to obtain a recycled fertilizer and a soil conditioner without asbestos. It is. [0002] Asbestos-containing building materials such as chrysotile have been used as roofing materials and wall materials for residential and non-residential buildings for more than 30 years. No effective treatment has yet been established. For example, as a method for treating asbestos building material waste, only a treatment such as a final treatment of a large lump is performed. [0004] Building materials containing asbestos are left without an effective treatment method, and a concrete, effective and useful treatment method is desired. On the other hand, silicate fertilizers have attracted attention as useful fertilizers for increasing the silicidized cells of grasses, particularly rice, and increasing disease resistance, insect resistance, lodging resistance and the like. There is a need for fertilizers and soil conditioners that can replenish the alkali content to improve the affected soil. In the present invention, asbestos-containing inorganic building material waste is melted to make asbestos absent, and the silicic acid and magnesium contained in the waste are utilized. To obtain silicic acid-recycled fertilizer and a soil conditioner for replenishing silicic acid and alkali. DETAILED DESCRIPTION OF THE INVENTION The inorganic building material containing asbestos used in the present invention is an inorganic building material mainly composed of at least one of cement and calcium silicate and asbestos, and includes nickel, chromium and titanium. And almost no harmful components such as flat colored slate, corrugated slate, slate, calcium silicate board, slag gypsum board, and ceramic siding. In addition, these are premised on asbestos-containing roof and wall material waste generated mainly due to replacement or rebuilding, but naturally include those that are discarded without being used. In general, melting asbestos alone requires a heating temperature of 1500 ° C. or more, and it is difficult to melt asbestos using a conventional furnace. As a result, the melting temperature of asbestos can be lowered. In the present invention, waste of inorganic building materials containing asbestos is melted, and the waste often contains a silicate compound or an alkaline earth metal as a melting aid. Therefore, it is possible to melt at 1500 ° C. or lower. When the amount of the melting aid contained is small, it is also possible to lower the melting temperature by adding a melting aid, for example, a waste glass material. Of course, setting the melting temperature depends on the fuel cost,
It is determined in consideration of workability, equipment, and the like. There are various methods of melting, external heating electric furnace, arc furnace,
An electric furnace typified by a high-frequency heating furnace, a combustion gas furnace typified by a flat furnace, and the like. However, in consideration of fuel cost and the like, the waste may be crushed to a certain size and then fired. The time required for melting is not particularly limited, but it is sufficient that at least asbestos contained in the building material waste is melted, and is determined by the size, stacking method, chemical composition, and the like of the building material waste. After melting, the mixture is quenched or slowly cooled using water or the like. For example, when quenched using water, the melt is granulated to obtain granules. It is also possible. Of course, after slow cooling, pulverization, crushing, or the like may be performed in a subsequent step, or, if necessary, pulverization, crushing, or granulation may be performed in the next step to adjust the particle size. The obtained melt is free of asbestos, the soluble silicic acid and alkali are compatible with the silicic fertilizer of the official standard of ordinary fertilizers, and furthermore, the magnesium component, for example, include. For example, if lime is required, it can be adjusted by adding at least one of quick lime and slaked lime, and it is also possible to add an active ingredient of another fertilizer. It may be added during the granulation process to form a granulated product. (Example) Asbestos-containing building material waste (Colonial, trade name: composition in Table 1) was calcined at 1000 ° C. for 15 minutes, and then pulverized with a pin mill.
The mixture was heated at about 1500 ° C. for 30 minutes, melted, immediately put into water, rapidly cooled, and after the moisture of the rapidly cooled melt was removed, the mixture was ground in a pot mill for 4 hours. When the obtained powder was analyzed by fertilizer, as shown in Table 1, the alkali content was 35.2.
% And soluble silicic acid 26.2%, which were numerical values conforming to official standards as a siliceous fertilizer. Moreover, since soluble magnesia is 6.2%, it is a numerical value suitable as a mixed lime fertilizer that guarantees soluble magnesia. [Table 1] According to the present invention, asbestos-containing building material waste can be easily recycled, asbestos, which is said to be harmful to health, can be absent, and the waste can be used as a fertilizer or soil improvement material. The fertilizer is huge in demand because it can be recycled. The fertilizer has characteristics and effects such as not only silicate fertilizer but also soluble lime fertilizer as mixed lime fertilizer.
───────────────────────────────────────────────────── 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) // C09K 101:00 B09B 3/00 ZAB (72)発明者 高橋 隆一 山形県東根市大字蟹沢字上縄目1816番地の 12 株式会社アイジー技術研究所内 Fターム(参考) 4D004 AA31 AB10 BA02 BA04 CA04 CA14 CA29 CC13 4H026 CA01 CA03 CC06 4H061 AA01 CC13 DD14 EE42 FF07 GG23 ──────────────────────────────────────────────────続 き Continued on the front page (51) Int.Cl. 7 Identification symbol FI Theme coat ゛ (Reference) // C09K 101: 00 B09B 3/00 ZAB (72) Inventor Ryuichi Takahashi Ryoichi Takane, Yamagata Prefecture No. 1816 12 F term in IG Technical Research Institute Co., Ltd. (Reference) 4D004 AA31 AB10 BA02 BA04 CA04 CA14 CA29 CC13 4H026 CA01 CA03 CC06 4H061 AA01 CC13 DD14 EE42 FF07 GG23
Claims (1)
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
を熔融して得られることを特徴とするリサイクル肥料及
び土壌改良材。Claims: 1. A recycled fertilizer and a soil improving material obtained by melting an inorganic building material mainly composed of at least one of cement and calcium silicate and asbestos.
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 true JP2003055072A (en) | 2003-02-26 |
JP5002096B2 JP5002096B2 (en) | 2012-08-15 |
Family
ID=19073456
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP2001243342A Expired - Fee Related JP5002096B2 (en) | 2001-08-10 | 2001-08-10 | Recycled fertilizer and soil conditioner |
Country Status (1)
Country | Link |
---|---|
JP (1) | JP5002096B2 (en) |
Citations (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
Patent Citations (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 |
Also Published As
Publication number | Publication date |
---|---|
JP5002096B2 (en) | 2012-08-15 |
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