JP2003112044A - In-water dephosphorizing agent, dephosphorizing method using the same and method of manufacturing fertilizer - Google Patents

In-water dephosphorizing agent, dephosphorizing method using the same and method of manufacturing fertilizer

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Publication number
JP2003112044A
JP2003112044A JP2001308962A JP2001308962A JP2003112044A JP 2003112044 A JP2003112044 A JP 2003112044A JP 2001308962 A JP2001308962 A JP 2001308962A JP 2001308962 A JP2001308962 A JP 2001308962A JP 2003112044 A JP2003112044 A JP 2003112044A
Authority
JP
Japan
Prior art keywords
dephosphorizing
underwater
mass
dephosphorization
parts
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
Application number
JP2001308962A
Other languages
Japanese (ja)
Other versions
JP2003112044A5 (en
JP3895961B2 (en
Inventor
Norimichi Kawashima
徳道 川島
Naoyuki Kato
直行 加藤
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.)
Ekomu Kk
Toin Gakuen
Original Assignee
Ekomu Kk
Toin Gakuen
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 Ekomu Kk, Toin Gakuen filed Critical Ekomu Kk
Priority to JP2001308962A priority Critical patent/JP3895961B2/en
Publication of JP2003112044A publication Critical patent/JP2003112044A/en
Publication of JP2003112044A5 publication Critical patent/JP2003112044A5/ja
Application granted granted Critical
Publication of JP3895961B2 publication Critical patent/JP3895961B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

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  • Fertilizers (AREA)
  • Water Treatment By Sorption (AREA)
  • Solid-Sorbent Or Filter-Aiding Compositions (AREA)

Abstract

PROBLEM TO BE SOLVED: To provide a dephosphorizing agent which can efficiently dephosphorize in water, is easily dispersible in water when the agent is charged into rivers, lakes, ponds or impounding reservoirs, is easily recoverable and recyclable after phosphorus adsorption, and a dephosphorizing method using the same. SOLUTION: This underwater dephosphorizing material is formed by providing the surface of a ligneous base material with a coating layer of a dephosphorizable composition prepared by compounding (B) 2 to 150 parts by mass hydraulic binder and (C) a calcium feeding material of an amount not exceeding 150 parts by mass as desired with (A) 100 parts apatite formable material. This underwater dephosphorizing material is charged into a phosphorus-containing aqueous solution and after the phosphorus is sufficiently adsorbed thereto, the phosphorus is separated and recovered from the inside of the aqueous solution.

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、河川、湖沼、海
水、生活排水、産業排水に含まれ、環境汚染の原因とな
っているリンを効率よく除去し、浄化するための水中脱
リン材及びそれを用いた脱リン方法及び使用済の水中脱
リン材を肥料原料として有効利用する方法にに関するも
のである。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to an underwater dephosphorization material for efficiently removing and purifying phosphorus contained in rivers, lakes, seawater, domestic wastewater, and industrial wastewater, which causes environmental pollution. The present invention relates to a dephosphorization method using the same and a method for effectively using used underwater dephosphorization material as a fertilizer raw material.

【0002】[0002]

【従来の技術】工場や家庭から排出される排水中のリン
は、河川、湖沼、海水の富栄養化の原因となり、環境破
壊を引き起すことから、これの除去、回収は大きな社会
問題となっている。また、公園、山林、住宅、建設現場
からの廃棄木材の処理も社会問題となっている。
2. Description of the Related Art Phosphorus contained in wastewater discharged from factories and households causes eutrophication of rivers, lakes and seawater and causes environmental damage. Therefore, removal and recovery of phosphorus becomes a major social problem. ing. In addition, the treatment of waste wood from parks, forests, houses and construction sites has become a social issue.

【0003】そのため、これまで多種多様の水中脱リン
剤や水中脱リン方法が提案されている。すなわち、水中
脱リン剤としては、例えば石灰質原料、ケイ酸質原料及
びゼオライトの反応生成物からなる脱リン材(特開20
01−9470号公報)、アロフェンを主成分とする物
質を成形し、300〜600℃で焼成してなる除去材
(特開平3−68445号公報)、産業廃棄物を溶融処
理して得たスラグを微粉砕し、その中の酸化カルシウム
をアルカリ処理して除去し、多孔状化したリン除去用無
機吸着材(特開昭63−39632号公報)、流動床ボ
イラーから排出される灰を主成分とする脱リン材(特開
平5−261378号公報)などが知られているし、ま
た水中脱リン方法としては、例えば、酸化アルミニウム
及び酸化ナトリウムを含む活性アルミナに海水を接触さ
せる海水の脱リン方法(特開平6−328067号公
報)、アンモニウムイオンを含有するリン酸塩排水にマ
グネシウムイオンを添加し、次いでpH値を8以上に調
整したのち、リン酸マグネシウムアンモニウム含有粒状
物の充填層に通し、排水中のリンをリン酸マグネシウム
アンモニウム粒子として上記粒状物の表面層に析出させ
る方法(特開昭63−200888号公報)、リンを含
む水溶液をカルシウムイオンの存在下で、リン除去能力
を有する粒状物と接触させる際に、この水溶液中に塩類
溶液を添加して液の電気伝導度を2000i□/cm以
上に調整して接触脱リンする方法(特開平3−2074
89号公報)などが知られている。
Therefore, various kinds of underwater dephosphorizing agents and underwater dephosphorizing methods have been proposed so far. That is, as the dephosphorizing agent in water, for example, a dephosphorizing agent composed of a reaction product of a calcareous raw material, a siliceous raw material, and zeolite (Japanese Patent Application Laid-Open No. 20-200200).
No. 01-9470), a removal material formed by molding a substance containing allophane as a main component, and firing it at 300 to 600 ° C. (JP-A-3-68445), and slag obtained by melting industrial waste. Is finely pulverized, and calcium oxide therein is treated with an alkali to remove it, and a porous inorganic adsorbent for phosphorus removal (Japanese Patent Laid-Open No. 63-39632) and ash discharged from a fluidized-bed boiler are main components. And a dephosphorizing material (Japanese Patent Application Laid-Open No. 5-261378) for example, and as a dephosphorizing method in water, for example, dephosphorizing seawater by contacting seawater with activated alumina containing aluminum oxide and sodium oxide. Method (Japanese Patent Laid-Open No. 6-328067), magnesium ions are added to phosphate wastewater containing ammonium ions, and then the pH value is adjusted to 8 or more, and then phosphate A method in which phosphorus in wastewater is deposited as magnesium ammonium phosphate particles on the surface layer of the above-mentioned granules by passing through a packed bed of the nesium-ammonium-containing granules (JP-A-63-200888), an aqueous solution containing phosphorus is calcium ion. In the presence of the above, when contacting with a granular material having a phosphorus removing ability, a salt solution is added to this aqueous solution to adjust the electric conductivity of the solution to 2000 i □ / cm or more and catalytic dephosphorization is performed. Kaihei 3-2074
No. 89) is known.

【0004】しかしながら、これらの脱リン剤や脱リン
方法は、二次公害を発生させる、生産量の少ない物質を
用いる必要がある、特殊な設備を必要とする、除去効率
が低いなどの問題点を有し、大量のリン含有水溶液を処
理するには、まだ十分に満足しうるものとはいえない。
However, these dephosphorizing agents and dephosphorizing methods have problems that secondary pollution occurs, it is necessary to use a substance with a small production amount, special equipment is required, and the removal efficiency is low. Therefore, it is not yet sufficiently satisfactory to treat a large amount of phosphorus-containing aqueous solution.

【0005】本発明者らは、このような従来の脱リン剤
及び脱リン方法の欠点を改良するために、先に(A)ア
パタイト形成性物質100質量部、(B)水硬性バイン
ダー3〜100質量部及び(C)水性樹脂エマルション
2〜50質量部及び所望に応じ150質量部を超えない
量の(D)カルシウム供給物質を含有する水中脱リン剤
組成物及びこれを用いる水中脱リン方法を提案した。し
かしながら、この水中脱リン剤は、河川、湖沼などに投
入し、リンの除去を行った後で、回収することが困難
で、使い捨てにならざるを得ないので、おのずから利用
分野が制限されるのを免れない。
In order to improve the disadvantages of such conventional dephosphorizing agents and dephosphorizing methods, the present inventors have first (A) 100 parts by mass of an apatite-forming substance, and (B) a hydraulic binder 3 to 3. In-water dephosphorization composition containing 100 parts by mass and (C) 2 to 50 parts by mass of aqueous resin emulsion and optionally (D) calcium-providing substance in an amount not exceeding 150 parts by mass, and in-water dephosphorization method using the same Proposed. However, this dephosphorizing agent in water is difficult to collect after it is put into rivers, lakes and marshes to remove phosphorus, and it must be thrown away. I cannot escape.

【0006】[0006]

【発明が解決しようとする課題】本発明は、水中におい
て効率よく脱リンすることができ、しかも河川、湖沼、
貯水池などに投入したときに、全面にわたって分散しや
すく、かつリン吸着後、容易に回収、再利用が可能な脱
リン材及びそれを用いた脱リン方法を提供することを目
的としてなされたものである。
DISCLOSURE OF THE INVENTION The present invention is capable of efficiently dephosphorizing in water, and can be used in rivers, lakes and marshes.
The purpose of the present invention is to provide a dephosphorization material and a dephosphorization method using the same that can be easily dispersed over the entire surface when it is put into a reservoir, etc., and can be easily recovered and reused after phosphorus adsorption. is there.

【0007】[0007]

【課題を解決するための手段】本発明者らは、水中のリ
ンを効率よく除去することができ、しかも安全に取り扱
いうる脱リン剤を開発するために鋭意研究を重ねた結
果、リン酸カルシウム系セラミックス上にヒドロキシア
パタイトが晶析する現象に着目し、先に従来の脱リン剤
とは全く異なった作用機序の新規な脱リン剤を提案した
が、さらに研究を重ね、この脱リン剤を木質基材表面に
担持させることにより、河川、湖沼、貯水池などに投入
したときに、容易に分布し、かつリン吸着後簡単に回収
しうること、及びこの回収後の脱リン材は、容易に肥料
化しうることを見出し、この知見に基づいて本発明をな
すに至った。
DISCLOSURE OF THE INVENTION The inventors of the present invention have conducted extensive studies to develop a dephosphorizing agent which can efficiently remove phosphorus in water and can be handled safely. As a result, calcium phosphate-based ceramics have been obtained. Focusing on the phenomenon that hydroxyapatite crystallizes above, we proposed a new dephosphorizer with a mechanism of action completely different from that of conventional dephosphorizers. By loading it on the surface of the base material, it can be easily distributed when it is thrown into rivers, lakes, reservoirs, etc., and can be easily recovered after phosphorus adsorption, and the dephosphorized material after this recovery is easily fertilizer. The present invention has been completed based on this finding.

【0008】すなわち、本発明は、(A)アパタイト形
成性物質100質量部に対し、(B)水硬性バインダー
2〜150質量部及び所望により150質量部を超えな
い量の(C)カルシウム供給物質を配合した脱リン性組
成物の被覆層を、木質基材表面に設けたことを特徴とす
る水中脱リン材、この水中脱リン材をリン含有水溶液に
投入し、それに十分にリンを吸着させたのち、水溶液中
より分離、回収する水中脱リン方法、及び回収した水中
脱リン材をそのままで又は粉砕し、肥料化処理する肥料
の製造方法を提供するものである。
That is, the present invention relates to (A) 100 parts by mass of an apatite-forming substance, (B) 2 to 150 parts by mass of a hydraulic binder, and optionally (C) a calcium supplying substance in an amount not exceeding 150 parts by mass. A coating layer of a dephosphorizing composition containing a water-based dephosphorizing material, characterized in that it is provided on the surface of a wood base material, this in-water dephosphorizing material is put into a phosphorus-containing aqueous solution to sufficiently adsorb phosphorus. After that, the present invention provides an underwater dephosphorization method for separating and recovering from an aqueous solution, and a method for producing a fertilizer for treating the recovered underwater dephosphorization material as it is or by pulverizing it.

【0009】[0009]

【発明の実施の形態】次に添付図面に従って本発明を説
明する。図1は本発明の水中脱リン材の構造を示す断面
図であって、このものは、木質基材1とその表面に設け
られた脱リン性組成物の被覆層2から構成されている。
この木質基材1としては、樹木の剪定や伐採により生じ
た大小の枝や建築廃材のような廃棄物を裁断又は粉砕し
て作成した木材チップや鋸屑、木粉などの木材粉末をバ
インダーで固めて調製した成形粒体が用いられる。これ
らの木質基材1は水面への散布、リン吸着後の回収の取
り扱いの容易さなどを考慮して、縦、横5〜100m
m、好ましくは10〜50mm、厚さ0.5〜20m
m、好ましくは2〜5mmの寸法に加工するのが好まし
い。
DETAILED DESCRIPTION OF THE INVENTION The present invention will be described below with reference to the accompanying drawings. FIG. 1 is a cross-sectional view showing the structure of the underwater dephosphorization material of the present invention, which comprises a wood base material 1 and a coating layer 2 of the dephosphorization composition provided on the surface thereof.
As the wood-based material 1, wood powder such as wood chips, sawdust, and wood powder produced by cutting or crushing wastes such as large and small branches and construction waste generated by pruning and felling of trees is hardened with a binder. Molded granules prepared by the above method are used. These wood base materials 1 are 5 to 100 m in length and width in consideration of spraying on the water surface and easy handling of recovery after phosphorus adsorption.
m, preferably 10 to 50 mm, thickness 0.5 to 20 m
It is preferable to process to a size of m, preferably 2 to 5 mm.

【0010】次に、この木質基材表面に被覆2を形成す
るための脱リン性組成物は、(A)アパタイト形成性物
質、(B)水硬性バインダー及び所望により用いられる
(C)カルシウム供給物質から構成される。
Next, the dephosphorization composition for forming the coating 2 on the surface of the wooden base material is (A) an apatite-forming substance, (B) a hydraulic binder, and (C) calcium supply optionally used. Composed of substances.

【0011】この(A)成分のアパタイト形成性物質と
しては、Ca3(PO42のような不溶性リン酸化合物
を主体とするものが用いられるが、廃陶土として未利用
のまま投棄されている廃ボーンアッシュや廃ボーンチャ
イナを用いるのがよい。このアパタイト形成性物質とし
ては、α‐リン酸カルシウム、β‐リン酸三カルシウム
のほかに、リン酸四カルシウムCa4(PO42、リン
酸水素カルシウム二水和物CaHPO4・2H2O、リン
酸水素カルシウム無水物CaHPO4、リン酸二水素カ
ルシウム−水和物Ca(H2PO4)・H2Oなどを主体
としたものを用いることができる。通常、アパタイト形
成性物質としては、ボーンチャイナを用いるのが好まし
いが、これは少なくとも10質量%、好ましくは30〜
60質量%のリン濃度で不溶性リン酸化合物を含有す
る。このアパタイト形成性物質は、通常平均粒径5〜1
00μm、好ましくは10〜50μmの粉末として用い
られる。
As the apatite-forming substance of the component (A), a substance mainly composed of an insoluble phosphoric acid compound such as Ca 3 (PO 4 ) 2 is used, but it is discarded as unused pottery clay without being used. It is better to use abandoned bone ash or abandoned bone china. Examples of the apatite-forming substance include α-calcium phosphate, β-tricalcium phosphate, tetracalcium phosphate Ca 4 (PO 4 ) 2 , calcium hydrogen phosphate dihydrate CaHPO 4 .2H 2 O, and phosphorus. It is possible to use those mainly containing calcium hydrogen hydride anhydrous CaHPO 4 , calcium dihydrogen phosphate hydrate Ca (H 2 PO 4 ) H 2 O, and the like. Usually, as the apatite-forming substance, it is preferable to use bone china, which is at least 10% by mass, preferably 30 to 30% by mass.
It contains an insoluble phosphate compound at a phosphorus concentration of 60% by weight. This apatite-forming substance usually has an average particle size of 5 to 1
It is used as a powder of 00 μm, preferably 10 to 50 μm.

【0012】次に、(B)成分の水硬性バインダーとし
ては、ポルトランドセメント、アルミナセメント、特殊
セメント、高炉スラグセメント、フライアッシュセメン
トなどのケイ素及びカルシウムを含有する水により硬化
しうる無機バインダーが用いられる。この水硬性バイン
ダーとしては、特にpH値の低いものが好ましい。この
水硬性バインダーは、通常、平均粒径5〜50μm、好
ましくは10〜30μmの粉末として用いられる。成形
体のpHとしては、7.5〜10、好ましくは7.8〜
9.5の範囲がよい。この(B)成分は、(A)成分1
00質量部当り2〜150質量部、好ましくは5〜50
質量部の割合で用いられる。
Next, as the hydraulic binder of the component (B), an inorganic binder containing silicon and calcium, such as Portland cement, alumina cement, special cement, blast furnace slag cement and fly ash cement, which can be hardened by water, is used. To be As the hydraulic binder, one having a low pH value is particularly preferable. This hydraulic binder is usually used as a powder having an average particle size of 5 to 50 μm, preferably 10 to 30 μm. The pH of the molded product is 7.5 to 10, preferably 7.8 to
A range of 9.5 is good. This (B) component is (A) component 1
2 to 150 parts by mass, preferably 5 to 50 parts by mass per 00 parts by mass
It is used in a proportion of parts by mass.

【0013】また、本発明で用いる脱リン性組成物に
は、セメントによる成形性を高め、バインダーとして耐
アルカリ性、耐水性を付与するために、所望に応じ水硬
性バインダーに水性樹脂エマルションを含有させること
ができる。この水性樹脂エマルションとしては、水性ラ
テックス、アクリルエマルション、エチレン−酢酸ビニ
ルエマルション、酢酸ビニル−アクリルエマルション、
ポリウレタンエマルション、エポキシエマルション、シ
リコーンエマルション、パウダーエマルションなどを単
独で又は2種以上混合して用いる。これらはいずれもよ
く知られているものであり、市販品として容易に入手し
うる。この水性樹脂エマルションには、アニオン性及び
カチオン性のものがあるが、いずれも固形分濃度30〜
60質量%のものが好ましい。
In addition, the dephosphorizing composition used in the present invention may contain an aqueous resin emulsion in the hydraulic binder, if desired, in order to enhance the moldability by cement and impart alkali resistance and water resistance as a binder. be able to. As this aqueous resin emulsion, aqueous latex, acrylic emulsion, ethylene-vinyl acetate emulsion, vinyl acetate-acrylic emulsion,
A polyurethane emulsion, an epoxy emulsion, a silicone emulsion, a powder emulsion, etc. may be used alone or in admixture of two or more. All of these are well known and can be easily obtained as commercial products. This water-based resin emulsion includes anionic and cationic ones.
It is preferably 60% by mass.

【0014】この水性樹脂エマルションを用いるのは、
木質基材の含水率に対する影響が少ない上に、有機溶剤
系エマルションを用いると、環境や衛生に悪影響を与え
るし、無溶剤では混合性が悪くなるのに対し、作業性が
よく、セメントとの混合が容易なためである。このエマ
ルションは、有機溶剤や可塑剤を用いる必要がなく、か
つ分子量が大きく耐水性を発揮するものが好ましい。そ
して、これを添加することにより成形性及び強度を向上
させることができるが、あまり多く添加するとリン酸成
分やアルカリ成分が皮膜化され、シールされて、所要の
効果を奏しなくなるため、固形分100質量部当り2〜
50質量部(固形分換算)にする必要がある。好ましい
割合は4〜20質量部であるが、使用に際しては、必要
に応じ、適宜希釈することもできる。
The use of this aqueous resin emulsion is
In addition to having little effect on the water content of the wood-based material, using an organic solvent-based emulsion adversely affects the environment and hygiene, and without solvent, mixing is poor, while workability is good, This is because mixing is easy. It is preferable that this emulsion does not need to use an organic solvent or a plasticizer, has a large molecular weight, and exhibits water resistance. Formability and strength can be improved by adding this, but if too much is added, the phosphoric acid component and the alkaline component will be formed into a film and sealed, and the desired effect will not be achieved. 2 to 2 parts by mass
It should be 50 parts by mass (solid content conversion). The preferred ratio is 4 to 20 parts by mass, but when used, it may be appropriately diluted if necessary.

【0015】本発明で用いる脱リン性組成物において
は、不足量のカルシウム成分を補給するために、(C)
成分として、炭酸カルシウム、酸化カルシウム、水酸化
カルシウム、硫酸カルシウムのようなカルシウム供給物
質を配合することが必要である。このカルシウム供給物
質としては、サンゴや水産廃棄物の貝殻を粉砕して用い
ることもできる。このカルシウム成分は少ないと脱リン
効果が不十分であるし、またあまり過剰になると二次公
害の原因になるので、(A)成分100質量部当り5〜
150質量部の範囲で用いることが必要である。
In the dephosphorizing composition used in the present invention, in order to supplement the insufficient amount of calcium component, (C)
As a component, it is necessary to incorporate a calcium supplying substance such as calcium carbonate, calcium oxide, calcium hydroxide, calcium sulfate. As the calcium supplying substance, coral and shellfish of aquatic wastes can be crushed and used. If the amount of this calcium component is too small, the dephosphorization effect will be insufficient, and if it is too much, it will cause secondary pollution, so that it is 5 to 100 parts by mass of the component (A).
It is necessary to use it in the range of 150 parts by mass.

【0016】本発明の脱リン性組成物は、その中のリン
濃度が少なくとも10質量%、好ましくは30〜60質
量%の範囲になるように調製するのが好ましい。この脱
リン性組成物は、乾燥後の被覆の比重が1.1〜2.
3、好ましくは1.5〜2.0になるように調製するの
が好ましい。
The dephosphorizing composition of the present invention is preferably prepared so that the phosphorus concentration therein is at least 10% by mass, preferably 30-60% by mass. In this dephosphorization composition, the specific gravity of the coating after drying is 1.1 to 2.
It is preferable to adjust it to 3, preferably 1.5 to 2.0.

【0017】本発明の脱リン性組成物は、(A)、
(B)及び所望に応じ用いられる(C)成分を所定割合
で混合し、水を加えて混練し、木質基材表面に塗布され
る。この塗布の方法は、ドブ漬け、刷毛塗り、ローラ塗
り、吹き付けなど、固体表面に塗膜を形成する際に通常
使用される方法の中から任意に選ぶことができる。
The dephosphorizing composition of the present invention comprises (A),
The component (B) and the component (C) that is used as desired are mixed in a predetermined ratio, water is added and the mixture is kneaded, and the mixture is applied to the surface of the wooden base material. This coating method can be arbitrarily selected from the methods usually used for forming a coating film on a solid surface, such as dipping, brush coating, roller coating, and spraying.

【0018】本発明の水中脱リン材の被覆層の厚さとし
ては、通常20μm〜5.0mm、好ましくは200μ
m〜2.0mmの範囲で選ばれる。この厚さは必ずしも
全体にわたって均一にする必要はない。そして、この被
覆層の厚さを調整することにより、使用態様に応じ、水
中脱リン材の全体の比重を1.00以下、好ましくは
0.95〜1.00の範囲内で制御して水面に浮上させ
ることもできるし、また1.00よりも大きくして水中
に沈降させることもできる。
The thickness of the coating layer of the underwater dephosphorizing material of the present invention is usually 20 μm to 5.0 mm, preferably 200 μm.
It is selected in the range of m to 2.0 mm. This thickness does not necessarily have to be uniform throughout. Then, by adjusting the thickness of this coating layer, the specific gravity of the entire underwater dephosphorization material is controlled to be 1.00 or less, preferably within the range of 0.95 to 1.00, depending on the usage mode. It can be floated up to the surface or can be made larger than 1.00 and settled in water.

【0019】本発明に従い、水中の脱リンを行うには、
例えば湖沼、貯水池のようなリン成分が蓄積している水
の中に、前記した水中脱リン材を投入し、水中のリン濃
度が実質上減少するのに十分な時間放置する。この時間
は、水中のリン濃度、水の流れ状態、水中植物の繁茂状
態、水中生物の棲息状態などにより左右されるが、通常
1〜150時間である。このようにして初期濃度の1/
5ないし1/20程度、絶対濃度として1.0ppm以
下までリン濃度を減少させることができる。
According to the present invention, to perform dephosphorization in water,
For example, the above-mentioned underwater dephosphorization material is put into water in which phosphorus components are accumulated, such as lakes and reservoirs, and left for a time sufficient for the phosphorus concentration in the water to be substantially reduced. This time depends on the phosphorus concentration in the water, the flow state of the water, the overgrowth state of the underwater plants, the habitation state of the aquatic organisms, etc., but it is usually 1 to 150 hours. In this way, 1 / of the initial concentration
The phosphorus concentration can be reduced to about 5 to 1/20, or 1.0 ppm or less as an absolute concentration.

【0020】このようにして、水中のリンを十分に吸着
させたのち、水中脱リン材を回収する。この回収は、例
えば採泥機や金網などを用いて水底や水面から渫い上げ
るか、あらかじめ水中脱リン材を金属線などにより連結
しておき、一挙に引き上げるなどの方法で行うことがで
きる。回収された使用済の脱リン材は、リン成分、植物
構成成分、カルシウム成分などの有効成分を含有してい
るので、所望に応じ粉砕したのち、各種農作物の肥料と
して施すことができる。
In this way, after the phosphorus in the water is sufficiently adsorbed, the underwater dephosphorization material is recovered. This recovery can be performed by, for example, using a mud collector or a wire net to scoop up from the water bottom or the water surface, or by previously connecting the underwater dephosphorization material with a metal wire or the like and then pulling it all at once. Since the recovered used dephosphorization material contains active ingredients such as phosphorus component, plant constituent component and calcium component, it can be applied as fertilizer for various agricultural products after being crushed as desired.

【0021】[0021]

【実施例】次に実施例により本発明をさらに詳細に説明
する。
EXAMPLES The present invention will be described in more detail with reference to examples.

【0022】参考例1 ボーンアッシュ100質量部、低pHセメント(石川産
業社製、商品名「エコセメント」、pH8.2)30質
量部、アクリルエマルション(BASFディスパージョ
ン社製、商品名「アクロナールYJ−1655D」、固
形分濃度55質量%)5質量部及びセルロース(信越化
学社製、商品名「メトローズ」)0.2質量部を混合
し、メカノミル(岡田精工社製、商品名「ラボ用粉体処
理装置」)を用い、450rpmの条件下で7分間混合
したのち、造粒し、直径13〜17mmの顆粒状の脱リ
ン性組成物を調製した。このもののリン濃度はリン酸カ
ルシウム換算で75質量%であった。
Reference Example 1 100 parts by mass of bone ash, 30 parts by mass of low pH cement (manufactured by Ishikawa Sangyo Co., Ltd., trade name "Eco-cement", pH 8.2), acrylic emulsion (manufactured by BASF Dispersion, trade name "Acronal YJ") -1655D ", solid content concentration 55 mass%) 5 parts by mass and cellulose (Shin-Etsu Chemical Co., Ltd., trade name" Metroze ") 0.2 parts by mass are mixed, and Mechanomill (Okada Seiko Co., Ltd. trade name" Laboratory powder " Using a body treatment apparatus "), the mixture was mixed for 7 minutes under the condition of 450 rpm and then granulated to prepare a granular dephosphorization composition having a diameter of 13 to 17 mm. The phosphorus concentration of this product was 75% by mass in terms of calcium phosphate.

【0023】初濃度325ppmのリン酸緩衝水溶液1
00質量部に対し、参考例1で得た顆粒状脱リン性組成
物をそれぞれ10質量部(●印)、20質量部(▲印)
及び50質量部(■印)の割合で投入し、浸漬時間と水
溶液中のリン残存量との関係を調べ、グラフとして図2
に示す。この図から明らかなように、本発明で用いる脱
リン性組成物は、水中のリンに対して顕著な脱リン効果
を示す。
Phosphate buffer aqueous solution 1 having an initial concentration of 325 ppm
To 100 parts by mass, 10 parts by mass (● mark) and 20 parts by mass (▲ mark) of the granular dephosphorization composition obtained in Reference Example 1, respectively.
And 50 parts by mass (marked with ■) were added, and the relationship between the immersion time and the residual amount of phosphorus in the aqueous solution was investigated, and a graph shown in FIG.
Shown in. As is clear from this figure, the dephosphorizing composition used in the present invention exhibits a remarkable dephosphorizing effect on phosphorus in water.

【0024】実施例1 ボーンアッシュ100質量部、低pHセメント(石川産
業社製、商品名「エコセメント」、pH8.2)30質
量部、及びセルロース(信越化学社製、商品名「メトロ
ーズ」)0.2質量部からなる粉体混合物に、水15質
量部を加えて混練し、脱リン性組成物塗布液を調製し
た。次いで、縦、横各50mm、厚さ5mmの木片チッ
プをメカノミル中に入れ、回転させながらその表面に、
前記の脱リン性組成物塗布液を吹き付け、送風乾燥する
ことにより、厚さ約0.5mmの被覆を形成させ、比重
約0.90の水面に浮上する水中脱リン材を製造した。
このもののリン酸塩濃度はリン酸カルシウム換算で75
質量%、木材チップと粉体混合物の質量比は1:1であ
った。
Example 1 100 parts by mass of bone ash, 30 parts by mass of low pH cement (manufactured by Ishikawa Sangyo Co., Ltd., trade name "Eco-cement", pH 8.2), and cellulose (manufactured by Shin-Etsu Chemical Co., Ltd., trade name "Metroze") To the powder mixture consisting of 0.2 parts by mass, 15 parts by mass of water was added and kneaded to prepare a dephosphorizing composition coating liquid. Then, put wood chips 50 mm long and 50 mm wide and 5 mm thick into the mechanomill, and while rotating, on the surface,
The above-mentioned dephosphorizing composition coating solution was sprayed and blow-dried to form a coating having a thickness of about 0.5 mm, and an underwater dephosphorizing material having a specific gravity of about 0.90 and floating on the water surface was produced.
The phosphate concentration of this product is 75 in terms of calcium phosphate.
The mass ratio of the wood chips and the powder mixture was 1: 1.

【0025】実施例2 初濃度300ppmのリン酸緩衝水溶液100質量部に
対し、10質量%の割合で実施例1で得た水中脱リン材
を投入し、15時間放置したのち、水中脱リン材を取り
出し、リン酸緩衝水溶液のリン濃度を測定したところ、
約150ppmであった。さらに放置時間を延長して1
20時間にしたところ、リン濃度はほぼ0となった。
Example 2 To 100 parts by mass of an aqueous phosphate buffer solution having an initial concentration of 300 ppm, the dephosphorizing agent in water obtained in Example 1 was added at a ratio of 10% by mass and left for 15 hours. Was taken out and the phosphorus concentration of the phosphate buffered aqueous solution was measured,
It was about 150 ppm. In addition, extend the leaving time to 1
After 20 hours, the phosphorus concentration became almost zero.

【0026】実施例3 岐阜県長久手町込ヶ池の水(pH6.0、リン濃度1
2.7ppm)1000mlに、実施例1で得た水中脱
リン材400gを投入し、浮遊させた。7日間放置後リ
ン濃度を測定したところ0.3ppmに低下した。次い
で、この水中脱リン材を回収し、風乾後、肥料として杉
苗木の根元に施したところ、通常の腐葉土と同様の成長
を示した。
Example 3 Water in Gugagaike, Nagakute Town, Gifu Prefecture (pH 6.0, phosphorus concentration 1)
(2.7 ppm) 1000 g, 400 g of the dephosphorizing material in water obtained in Example 1 was charged and floated. When the phosphorus concentration was measured after standing for 7 days, it decreased to 0.3 ppm. Then, the dephosphorized material in water was recovered, air-dried, and then applied as a fertilizer to the roots of cedar saplings.

【0027】[0027]

【発明の効果】本発明によれば、河川、湖沼、貯水池な
どに投入したときに、全面にわたって容易に分散し、効
率よく脱リンすることができる脱リン材が得られ、しか
もこの脱リン材はリン吸着後容易に回収することがで
き、回収後粉砕し、乾燥することにより肥料として使用
しうるという利点がある。また、原料の木質基材として
は、隣接地区の伐採廃材を利用しうるので、林業廃棄物
の有効利用という点でも好適である。
EFFECTS OF THE INVENTION According to the present invention, it is possible to obtain a dephosphorization material which can be easily dispersed over the entire surface and efficiently dephosphorized when thrown into a river, a lake, a water reservoir, or the like. Has an advantage that it can be easily recovered after adsorption of phosphorus, and can be used as a fertilizer by crushing and drying after recovery. Further, as the wood base material of the raw material, the felled waste wood of the adjacent area can be used, which is also suitable from the viewpoint of effective utilization of forestry waste.

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

【図1】 本発明の水中脱リン材の断面図。FIG. 1 is a sectional view of an underwater dephosphorization material of the present invention.

【図2】 本発明で用いる脱リン性組成物の脱リン効果
を示すグラフ。
FIG. 2 is a graph showing the dephosphorization effect of the dephosphorization composition used in the present invention.

【符号の説明】[Explanation of symbols]

1 木質基材 2 脱リン性組成物被覆 1 Wood base material 2 Dephosphorization composition coating

───────────────────────────────────────────────────── フロントページの続き (72)発明者 加藤 直行 三重県四日市市南小松町2717−4 Fターム(参考) 4D024 AA05 AB12 BA11 BB07 4G066 AA17A AA47A AA49A AA66A AA73C AC07C AC12C AE20C BA20 BA38 CA41 DA07 DA08 FA03 FA26 FA28 FA40 4H061 AA01 CC02 CC03 CC04 CC05 EE43 EE64 FF06 FF08 GG13 LL07 LL26    ─────────────────────────────────────────────────── ─── Continued front page    (72) Inventor Naoyuki Kato             2717-4 Minamikomatsucho, Yokkaichi-shi, Mie Prefecture F-term (reference) 4D024 AA05 AB12 BA11 BB07                 4G066 AA17A AA47A AA49A AA66A                       AA73C AC07C AC12C AE20C                       BA20 BA38 CA41 DA07 DA08                       FA03 FA26 FA28 FA40                 4H061 AA01 CC02 CC03 CC04 CC05                       EE43 EE64 FF06 FF08 GG13                       LL07 LL26

Claims (10)

【特許請求の範囲】[Claims] 【請求項1】 (A)アパタイト形成性物質100質量
部に対し、(B)水硬性バインダー2〜150質量部を
配合した脱リン性組成物の被覆層を、木質基材表面に設
けたことを特徴とする水中脱リン材。
1. A coating layer of a dephosphorization composition containing (A) 100 parts by mass of an apatite-forming substance and (B) 2 to 150 parts by mass of a hydraulic binder is provided on the surface of a wood base material. Underwater dephosphorization material characterized by.
【請求項2】 (A)アパタイト形成性物質100質量
部に対し、(B)水硬性バインダー2〜150質量部及
び(C)150質量部を超えない量のカルシウム供給物
質を配合した脱リン性組成物の被覆層を、木質基材表面
に設けたことを特徴とする水中脱リン材。
2. A dephosphorizing property in which (A) 100 parts by mass of an apatite-forming substance, (B) 2 to 150 parts by mass of a hydraulic binder and (C) 150 parts by mass of a calcium supplying substance are mixed. An underwater dephosphorization material, characterized in that a coating layer of the composition is provided on the surface of a wooden base material.
【請求項3】 (A)成分のアパタイト形成性物質がボ
ーンアッシュ及びボーンチャイナの中から選ばれた少な
くとも1種である請求項1又は2記載の水中脱リン材。
3. The underwater dephosphorization material according to claim 1, wherein the apatite-forming substance as the component (A) is at least one selected from bone ash and bone china.
【請求項4】 (B)成分の水硬性バインダーがポルト
ランドセメント、アルミナセメント、特殊セメント、高
炉スラグセメント及びフライアッシュセメントの中から
選ばれた少なくとも1種である請求項1、2又は3記載
の水中脱リン材。
4. The hydraulic binder as the component (B) is at least one selected from Portland cement, alumina cement, special cement, blast furnace slag cement and fly ash cement. Underwater dephosphorization material.
【請求項5】 (C)成分のカルシウム供給物質が、炭
酸カルシウム、酸化カルシウム、水酸化カルシウム、硫
酸カルシウム、貝殻及びサンゴの中から選ばれた少なく
とも1種である請求項2又は3記載の水中脱リン材。
5. The water according to claim 2 or 3, wherein the component (C) that supplies calcium is at least one selected from calcium carbonate, calcium oxide, calcium hydroxide, calcium sulfate, shells and corals. Dephosphorization material.
【請求項6】 木質基材が木材チップ及び木材粉末成形
粒体の中から選ばれた少なくとも1種である請求項1な
いし5のいずれかに記載の水中脱リン材。
6. The underwater dephosphorizing material according to claim 1, wherein the wood base material is at least one selected from wood chips and wood powder molded granules.
【請求項7】 被覆層の厚さを変えて、比重を1.00
以下に調整した請求項1ないし6のいずれかに記載の水
中脱リン材。
7. The specific gravity is changed to 1.00 by changing the thickness of the coating layer.
The underwater dephosphorization material according to any one of claims 1 to 6, which is adjusted as follows.
【請求項8】 木質基材が縦5〜100mm、横5〜1
00mm、厚さ0.5〜20mmの範囲内のサイズを有
する請求項1ないし7のいずれかに記載の水中脱リン
材。
8. A wood base material having a length of 5 to 100 mm and a width of 5 to 1
The underwater dephosphorization material according to any one of claims 1 to 7, which has a size within a range of 00 mm and a thickness of 0.5 to 20 mm.
【請求項9】 リン含有水溶液に、請求項1ないし8の
いずれかに記載の水中脱リン材を投入し、それに十分に
リンを吸着させたのち、水溶液中より分離、回収する水
中脱リン方法。
9. An in-water dephosphorization method in which the underwater dephosphorizing material according to any one of claims 1 to 8 is added to a phosphorus-containing aqueous solution to sufficiently adsorb phosphorus, and then separated and recovered from the aqueous solution. .
【請求項10】 請求項9記載の方法において、回収し
た水中脱リン材をそのままで又は粉砕して、肥料化処理
する肥料の製造方法。
10. The method for producing a fertilizer according to claim 9, wherein the recovered underwater dephosphorizing material is used as it is or is pulverized to be fertilized.
JP2001308962A 2001-10-04 2001-10-04 Underwater dephosphorization material, dephosphorization method using the same, and fertilizer production method Expired - Fee Related JP3895961B2 (en)

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Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2005350318A (en) * 2004-06-14 2005-12-22 Denki Kagaku Kogyo Kk Nitrogen fertilizer
JP2007075706A (en) * 2005-09-13 2007-03-29 Akita Prefecture Phosphorus recovering material, its producing method and its effectiveness as fertilizer
FR2985200A1 (en) * 2012-01-03 2013-07-05 Cie Financiere Et De Participations Roullier PHOSPHATE - BASED GRANULAR MATERIAL, METHOD FOR MANUFACTURING THE SAME AND USE THEREOF IN A DEVICE FOR DEPHOSPHATION OF WASTEWATER.
CN105776552A (en) * 2016-03-17 2016-07-20 北京市水科学技术研究院 Dephosphorization filler for constructed wetlands and preparation method thereof

Families Citing this family (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN107573149B (en) * 2017-09-08 2020-12-08 武汉钢铁有限公司 Greening planting soil for sponge city

Cited By (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2005350318A (en) * 2004-06-14 2005-12-22 Denki Kagaku Kogyo Kk Nitrogen fertilizer
JP4480477B2 (en) * 2004-06-14 2010-06-16 電気化学工業株式会社 Manufacturing method of granulated nitrogen fertilizer
JP2007075706A (en) * 2005-09-13 2007-03-29 Akita Prefecture Phosphorus recovering material, its producing method and its effectiveness as fertilizer
FR2985200A1 (en) * 2012-01-03 2013-07-05 Cie Financiere Et De Participations Roullier PHOSPHATE - BASED GRANULAR MATERIAL, METHOD FOR MANUFACTURING THE SAME AND USE THEREOF IN A DEVICE FOR DEPHOSPHATION OF WASTEWATER.
WO2013102729A1 (en) * 2012-01-03 2013-07-11 Compagnie Financiere Et De Participations Roullier Phosphate-based granular material, process for manufacturing same and use thereof in a device for removing phosphates from wastewaters
CN105776552A (en) * 2016-03-17 2016-07-20 北京市水科学技术研究院 Dephosphorization filler for constructed wetlands and preparation method thereof

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