JP2004089760A - Highly selective dephosphorizing agent and method for producing the same - Google Patents
Highly selective dephosphorizing agent and method for producing the same Download PDFInfo
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Abstract
【課題】水に溶存しているリンとその他の陰イオンとの選択係数を高め、他の陰イオンの存在下においても、リンの除去率が選択的に高い脱リン剤を提供する。
【解決手段】一般式
MII 1−xMIII x(OH)2An− y・mH2O
(MIIは二価金属の中から選ばれた少なくとも1種、MIIIは三価金属の中から選ばれた少なくとも1種、An−はn価の陰イオン、x、y及びmは、0<x≦0.67、0<y≦1、0≦m≦2)
で表わされる複合金属水酸化物の結晶の加熱処理物を有効成分とし、かつ水に溶存しているリンの硫酸イオンに対する選択係数が5以上である高選択性脱リン剤とする。
【選択図】 なしAn object of the present invention is to provide a dephosphorizing agent which enhances the selectivity between phosphorus dissolved in water and other anions and selectively removes phosphorus even in the presence of other anions.
A general formula M II 1-x M III x (OH) 2 A n- y · mH 2 O
(M II is at least one selected from divalent metals, M III is at least one selected from among trivalent metal, A n-n-valent anion, x, y and m are 0 <x ≦ 0.67, 0 <y ≦ 1, 0 ≦ m ≦ 2)
The heat-treated product of the crystal of the composite metal hydroxide represented by the formula (1) is used as an active ingredient, and a highly selective dephosphorizing agent having a selectivity of 5 or more for phosphorus ions dissolved in water.
[Selection diagram] None
Description
【0001】
【発明の属する技術分野】
本発明は、河川、湖沼、海水、上下水道に含まれ汚染源となっているリンを効率よく除去し、浄化するための脱リン剤及びその製造方法に関するものである。
【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。
【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2001−9470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)、ハイドロタルサイト類を有効成分とした脱リン剤(特開2000−24658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2000マイクロモー/cm以上に調整して接触脱リンする方法(特開平3−207489号公報)、二価金属と三価金属とを含む複合金属水酸化物にリン含有排水を接触させてリン成分を吸着し、次いでリン成分を吸着したリン吸着剤をアルカリ金属塩又はアルカリ土類金属塩の水溶液で処理して再生する方法(特開平11−57695号公報)などが知られている。
【0004】
しかしながら、これらの脱リン剤や脱リン方法は、他の陰イオン、特に硫酸イオンが共存するとリンの除去率が低下し、海水域などで実際に富栄養化を完全に阻止することはできなかった。
【0005】
【発明が解決しようとする課題】
本発明は、このような事情のもとで、水に溶存しているリンとその他の陰イオンとの選択係数を高め、他の陰イオンの存在下においても、リンの除去率が選択的に高い脱リン剤を提供することを目的としてなされたものである。
【0006】
【課題を解決するための手段】
本発明者らは、他の陰イオンと共存していても高い選択率によりリンを選択的に除去しうる脱リン剤を開発するために鋭意研究を重ねた結果、所定の組成の再結晶性複合金属水酸化物、すなわち所定の組成の複合金属水酸化物の結晶の加熱処理物において、リンの硫酸イオンに対する選択係数が5以上になるように調整することによりその目的を達成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。
【0007】
すなわち、本発明は、一般式
MII 1−xMIII x(OH)2An− y・mH2O (I)
(式中のMIIは二価金属の中から選ばれた少なくとも1種、MIIIは三価金属の中から選ばれた少なくとも1種、An−はn価の陰イオンを示し、x、y及びmは、0<x≦0.67、0<y≦1、0≦m≦2を満足する数である)
で表わされる複合金属水酸化物の結晶の加熱処理物を有効成分とし、かつ水に溶存しているリンの硫酸イオンに対する選択係数が5以上であることを特徴とする高選択性脱リン剤、及び二価金属の水溶性化合物と三価金属の水溶性化合物を含む水溶液に、無機酸又は有機酸の水溶性塩と水酸化アルカリの混合水溶液を滴下したのち、0〜90℃の温度に保って反応させ、一般式
MII 1−xMIII x(OH)2An− y・mH2O (I)
(式中のMIIは二価金属の中から選ばれた少なくとも1種、MIIIは三価金属の中から選ばれた少なくとも1種、An−はn価の陰イオンを示し、x、y及びmは、0<x≦0.67、0<y≦1、0≦m≦2を満足する数である)
で表わされる複合金属水酸化物の結晶の沈殿を生成させ、あるいは二価金属の水溶性化合物と二価マンガンの水溶性化合物を含む水溶液に、無機酸又は有機酸の水溶性塩と水酸化アルカリの混合水溶液を滴下したのち、酸化条件下、0〜90℃の温度に保って反応させ、一般式
MII 1−xMn(III)x(OH)2An− y・mH2O (II)
(式中のMII、An−、x、y及びmは前記と同じ意味をもつ)
で表わされる複合金属水酸化物の結晶の沈殿を生成させ、次いで、この沈殿を分別し、200〜500℃において加熱処理することを特徴とする脱リン剤の製造方法を提供するものである。
【0008】
【発明の実施の形態】
本発明の一般式(I)中における二価金属MIIとしては、例えばMg、Zn、Cu(II)、Co(II)、Ni(II)などを挙げることができるが、特に好ましいのは、Mg、Zn及びCo(II)である。また、三価金属MIIIとしては、Al、Mn(III)、Fe(III)、Co(III)を挙げることができるが、特に好ましいのはMn及びAlである。このMII及びMIIIは、それぞれ単独の金属であってもよいし、また2種以上の金属の複合でもよい。
【0009】
次に、一般式(I)中の陰イオンAn−は、イオン交換性を有することが必要であり、例えば炭酸イオン、硫酸イオン、ハロゲンイオン、水酸化物イオンなどが挙げられる。この中で水酸化物イオンが特に好ましく、また加熱処理により容易に水酸化物イオンに変わるという点で炭酸イオン、炭酸水素イオンが好ましい。
【0010】
本発明の脱リン剤においては、従来の脱リン剤がリン酸と金属との反応に基づくものであるのに対し、イオン交換に基づく点で明らかに異なっている。しかも、このイオン交換は、炭酸イオン、ハロゲンイオン、硝酸イオン、硫酸イオンが共存していてもリン酸の電離体のみと選択的に行われる。
【0011】
次に、一般式(I)中のxは、0よりも大きく0.67以下の範囲の数であり、mは0と2との間の範囲の数であることが必要である。
そして、陰イオンAn−の量yは、Mn、Coなどの遷移金属を含む場合、原子価が単一でないため、このyは理論値(x/n)に対し、約30%の許容範囲を有している。特に好ましいのは、xが0.33付近でmが0≦m≦2の範囲内にあるものである。
【0012】
本発明の脱リン剤は、一般式(I)の組成を有する複合金属水酸化物の結晶の加熱処理物を有効成分とするものであって、かつ水に溶存しているリンの硫酸イオンに対する選択係数が5以上であることが必要である。この加熱処理物は、結晶構造を維持できず、層構造が崩れるが、リンを吸着すると層構造が回復するという特徴を有する。このもののリンに対する高い選択性は脱リン剤の層間の空隙により発現すると考えられる。すなわち、本発明の脱リン剤においては、層構造が乱れ、この空隙の大きさ(4〜6Å)がリン酸イオンの大きさに一致するためであると考えられる。
この空隙の大きさは、X線回折により求められる層間間隙dとは異なり、直接求めることはできず、選択吸着性などから間接的に求められるものである。そして、同じd値を示す物質でも、構成元素の種類、加熱処理条件により、この大きさは変化する。
【0013】
したがって、本発明において、一般式(I)中の組成の複合金属水酸化物の結晶を熱処理して、所定の選択係数を有するものを得るには、先ず好適な組成をもつ複合金属水酸化物の結晶を調製することが必要である。このような組成としては、例えば一般式(I)におけるMIIIが、Mn、Al又はAlとCoの複合で、MIIがMg、Ni、Zn又はCoとZnの複合のものを挙げることができる。
【0014】
そして、このような組成をもつ複合金属水酸化物の結晶の例としては、一般式
Mg1−xMnx(OH)2(HCO3)y・mH2O (III)
Zn1−xAlx(OH)2(HCO3)y・mH2O (IV)
(Co,Zn)1−x(Co,Al)x(OH)2(HCO3)y・mH2O(V)
及び
Ni1−xMnx(OH)2(HCO3)y・mH2O (VI)
(ただし、各式中のx、y及びmは前記と同じ意味をもつ)
で表わされるものを挙げることができる。
なお、上記の(Co,Zn)及び(Co,Al)は二価金属Zn及び三価金属Alの一部がそれぞれCoで置換されていることを意味する。Mn、Coなどの遷移金属を含む場合、原子価が単一でないため、yの値は理論値(x/n)と必ずしも一致しない。したがって、yの値は0〜1の範囲内で許容される。
【0015】
このような組成の複合金属水酸化物の結晶の炭酸水素塩は200〜500℃、好ましくは250〜350℃の範囲の温度で加熱することにより、脱炭酸反応が進行し、水酸化物型に変化する。そして、金属成分としてMn、Co、Feが含まれる場合、これらは複数の原子価を有するため、温度、雰囲気及び反応時間などを適切に制御して、必要な構成及び有効層空隙をもつものとすることが必要である。
【0016】
本発明方法において、原料として用いる二価金属の水溶性化合物及び三価金属の水溶性化合物としては、Mn、Mg、Zn、Co、Ni、Fe、Alなどの金属のハロゲン化物、硝酸塩、硫酸塩、炭酸塩などを挙げることができる。そのほか、所望ならば水酸化マグネシウム、水酸化アルミニウム、水酸化鉄のような水酸化物を用いることもできる。
【0017】
次に、前記一般式(I)中の陰イオンAn−の供給源となる無機酸又は有機酸の水溶性塩としては、炭酸、硫酸、塩酸、硝酸のような無機酸又はシュウ酸、酢酸、クエン酸、乳酸などの有機酸のアルカリ金属塩、アルカリ土類金属塩、アンモニウム塩などが用いられるが、特に好ましいのはアルカリ金属炭酸塩、アルカリ金属炭酸水素塩、例えば炭酸ナトリウム、炭酸カリウム、炭酸水素ナトリウム、炭酸水素カリウムである。また、これと混合して用いられる水酸化アルカリとしては、アルカリ金属やアンモニウムの水酸化物、例えば水酸化ナトリウム、水酸化カリウム、水酸化アンモニウムなどがある。
この無機酸又は有機酸の水溶性塩と水酸化アルカリの混合水溶液は、二価金属及び三価金属化合物に対し、約1〜40倍モルの割合で用いられる。
【0018】
三価金属の水溶性化合物の代りに、二価のマンガンの水溶性化合物を用いた場合は、これと無機酸又は有機酸の水溶性塩と水酸化アルカリの混合水溶液を滴下したのち、酸化条件下、例えば特に雰囲気を制御しない大気下、0〜90℃の温度においてゆっくり反応させることにより、一般式
MII 1−xMn(III)x(OH)2An− y・mH2O (II)
(式中のAn−はn価の陰イオンを示し、MII、x、y及びmは前記と同じ意味をもつ)
で表わされる複合金属水酸化物の結晶の沈殿を生成させることができる。
【0019】
このようにして調製された二価金属の水溶性化合物と三価金属の水溶性化合物に無機酸又は有機酸の水溶性塩と水酸化アルカリの混合水溶液を滴下したのち、次に0〜90℃の温度において反応させる。この反応は、通常かきまぜながら1〜5時間行われる。この反応により、前記一般式(I)で表わされる複合金属水酸化物の結晶が沈殿してくるので、これをろ過又は遠心分離により分取し、中性になるまで水洗したのち、風乾することにより、複合金属水酸化物の結晶が粉末として得られる。
【0020】
この粉末は、X線構造解析、組成分析、各金属の価数分析及びTG−TDA分析の質量減少から、一般式(I)で表わされる組成を有するハイドロタルサイトであることが分る。
【0021】
次に、この複合金属酸化物の結晶を、電気炉中に入れ、200〜500℃、好ましくは250〜350℃の温度において2〜10時間加熱処理する。この加熱処理により組成中の陰イオンが脱離するとともに、層構造が再配列し、水に溶存しているリンの硫酸イオンに対する選択係数が5以上の高選択性脱リン剤が得られる。
【0022】
このようにして得られる本発明の脱リン剤は、リン溶存水溶液中において、塩化物イオン、硝酸イオン、硫酸イオン、炭酸イオンなど、通常リンの吸着を阻害すると考えられている陰イオンが共存してもリンを選択的に高い効率で吸着することができる。
【0023】
【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が、本発明はこれらの例によって何ら限定されるものではない。
なお、各例中における脱リン剤についての、水に溶存しているリンの硫酸イオンに対する選択係数は次のようにして求めた。
【0024】
炭酸イオン、塩化物イオン、硝酸イオン、リン酸二水素イオン、硫酸イオン(いずれもナトリウム塩として用いる)の等モル量(0.02mmol)混合溶液で、混合陰イオン吸着実験を行い、溶液中のイオン種の減少量から各陰イオンの吸着容量を求め、リン酸二水素イオンの吸着容量を分子に、他の陰イオンの吸着容量を分母とした比をとり、脱リン剤の水中における各種陰イオンに対する溶存したリンの選択係数とした。
【0025】
実施例1
塩化マンガン(II)1質量部と塩化マグネシウム3質量部とを含む水溶液に、水酸化ナトリウム80質量部と炭酸ナトリウム40質量部を含む水溶液を撹拌しながら滴下し、60℃で2時間反応させ、沈殿物を得た。次いで、この沈殿物を遠心分離し、中性になるまで水洗したのち、風乾した。生成物を粉末X線構造解析、組成分析、マンガンの価数分析した結果、Mg0.75Mn0.25(OH)2(HCO3)0.25・mH2O型のハイドロタルサイトと同定された。また、TG−TDA分析の質量減少から、mの値は、1から2の間であることが分った。
【0026】
この試料を300℃の電気炉の中で4時間加熱することにより脱リン剤を製造し、陰イオン吸着性能を以下の方法で測定した。すなわち、この試料0.1gに対して0.02mmolの炭酸イオン、塩化物イオン、硝酸イオン、リン酸二水素イオン、硫酸イオン(いずれもナトリウム塩)を加え、混合陰イオン吸着実験を27℃で3日間行ったのち、溶液を陰イオンクロマトグラフィで分析したところ、添加したリン酸二水素イオンの99%が吸着したのに対し、硫酸イオンの吸着は9%であった。すなわち、脱リン剤の水中における硫酸イオンに対する溶存したリンの選択係数は11であった。また、リン酸単独での飽和吸着容量を測定したところ、1.4mmol/gであった。
【0027】
実施例2
塩化アルミニウム1質量部と塩化亜鉛3質量部を含む水溶液に、水酸化ナトリウム80質量部と炭酸ナトリウム40質量部とを含む水溶液を撹拌しながら滴下し、60℃で2時間反応させ、沈殿物を得た。この沈殿物を遠心分離し、中性になるまで水洗したのち、風乾した。生成物を粉末X線構造解析、組成分析した結果、Zn0.75Al0.25(OH)2(HCO3)0.25・mH2O型のハイドロタルサイトと同定された。また、TG−TDA分析の質量減少から、mの値は1から2の間にあることが分った。
【0028】
次に、この生成物を300℃の電気炉の中で4時間加熱することにより脱リン剤を製造し、このものの陰イオン吸着性能を以下の方法で測定した。すなわち、この脱リン剤0.1gに対して0.02mmolの炭酸イオン、塩化物イオン、硝酸イオン、リン酸二水素イオン、硫酸イオン(いずれもナトリウム塩)を加え、混合陰イオン吸着実験を27℃で3日間行ったのち、溶液を陰イオンクロマトグラフィで分析した。リン酸二水素イオンが73%吸着したのに対し、硫酸イオンの吸着は6%であった。したがって、この脱リン剤の水中における硫酸イオンに対する溶存したリンの選択係数は13であった。また、リン酸単独での飽和吸着容量を測定したところ、1.2mmol/gであった。
【0029】
実施例3
塩化アルミニウム1質量部と塩化コバルト(II)1.5質量部と塩化亜鉛1.5質量部とを含む水溶液に、炭酸ナトリウム40質量部を含む水溶液を撹拌しながら滴下したのち、水酸化ナトリウム水溶液でpHを9に調整した。この混合物を80℃で4時間反応させ、沈殿物を得た。次に、この沈殿物を遠心分離し、中性になるまで水洗したのち、40℃で1日乾燥した。この生成物を粉末X線構造解析した結果、ハイドロタルサイトと同定された。また、また、TG−TDA分析の質量減少から、mの値は1から2の間であることが分った。
【0030】
次に、この生成物を300℃の電気炉の中で4時間加熱することにより、脱リン剤を製造し、陰イオン吸着性能を以下の方法で測定した。すなわち、この脱リン剤0.1gに対して0.02mmolの炭酸イオン、塩化物イオン、硝酸イオン、リン酸二水素イオン、硫酸イオン(いずれもナトリウム塩)を加え、混合陰イオン吸着実験を27℃で3日間行ったのち、液を陰イオンクロマトグラフィで分析した。その結果、リン酸二水素イオンが91%吸着したのに対し、硫酸イオンの吸着は2%であった。したがって、この脱リン剤の水中における硫酸イオンに対する溶存したリンの選択係数は55であった。また、リン酸単独での飽和吸着容量を測定したところ、0.6mmol/gであった。
【0031】
実施例4
塩化マンガン(II)1質量部と塩化ニッケル3質量部とを含む水溶液に、水酸化ナトリウム80質量部と炭酸ナトリウム40質量部を含む水溶液を撹拌しながら滴下し、60℃で2時間反応させ、沈殿物を得た。この沈殿物を遠心分離し、中性になるまで水洗し、風乾した。このようにして得た生成物を粉末X線構造解析、組成分析、マンガンの価数分析した結果、Ni0.75Mn0.25(OH)2(HCO3)0.25・mH2O型のハイドロタルサイトであると同定された。また、TG−TDA分析の質量減少から、mの値は1から2の間であることが分った。
【0032】
この生成物を300℃の電気炉の中で4時間加熱することにより脱リン剤を製造し、陰イオン吸着性能を以下の方法で測定した。すなわち、この脱リン剤0.1gに対して0.02mmolの炭酸イオン、塩化物イオン、硝酸イオン、リン酸二水素イオン、硫酸イオン(いずれもナトリウム塩)を加え、混合陰イオン吸着実験を27℃で3日間行ったのち、溶液を陰イオンクロマトグラフィで分析したところ、リン酸二水素イオンが24%吸着したのに対し、硫酸イオンの吸着は4%であった。したがって、この脱リン剤の水中における硫酸イオンに対する溶存したリンの選択係数は6であった。また、リン酸単独での飽和吸着容量を測定したところ、0.16mmol/gであった。
【0033】
比較例
市販のMg0.75Al0.25(OH)2(HCO3)0.25型のハイドロタルサイトを300℃の電気炉の中で4時間加熱したものを脱リン剤とし、陰イオン吸着性能を以下の方法で測定した。この脱リン剤0.1gに対して0.02mmolの炭酸イオン、塩化物イオン、硝酸イオン、リン酸二水素イオン、硫酸イオン(いずれもナトリウム塩)を加え、混合陰イオン吸着実験を27℃で3日間行ったのち、溶液を陰イオンクロマトグラフィで分析したところ、添加したリン酸二水素イオンが80%吸着したのに対し、硫酸イオンが36%、塩化物イオンは13%、硝酸イオンが10%吸着され、これらは主に炭酸イオンとイオン交換していた。また、リン酸単独での飽和吸着容量を測定したところ、1.1mmol/gであった。また、この脱リン剤の水中における硫酸イオンに対する溶存したリンの選択係数はおよそ2であった。
【0034】
以上の結果から、本発明の高選択性脱リン剤は、従来のものと比較して、高いリン選択性を有することが分る。
【0035】
【発明の効果】
本発明によれば、リン含有水溶液において、ハロゲンイオン、硝酸イオン、硫酸イオン、炭酸イオンなどの陰イオンが共存していても、リンを選択的に吸着しうる高選択性脱リン剤が得られるので、海水中のリンの除去に有用である。[0001]
TECHNICAL FIELD OF THE INVENTION
The present invention relates to a dephosphorizing agent for efficiently removing and purifying phosphorus, which is contained in rivers, lakes, marshes, seawater, and water and sewage, and is a pollution source, and a method for producing the same.
[0002]
[Prior art]
Phosphorus in wastewater discharged from factories and households causes eutrophication of rivers, lakes and marshes and seawater, causing environmental destruction, and its removal and recovery is a major social problem.
[0003]
Therefore, a variety of underwater dephosphorization agents and underwater dephosphorization methods have been proposed. That is, as the underwater dephosphorizing agent, for example, a dephosphorizing material composed of a reaction product of a calcareous raw material, a siliceous raw material and a zeolite (Japanese Patent Application Laid-Open No. 2001-9470), and a substance mainly composed of allophane are molded. A slag obtained by melting treatment of industrial waste and a slag obtained by melting industrial waste are pulverized, and calcium oxide in the slag is removed by alkali treatment to remove porous material. Phosphorus-removed inorganic adsorbent (JP-A-63-39632), ash discharged from a fluidized-bed boiler as a main component (JP-A-5-261378), hydrotalcites A dephosphorizing agent containing as an active ingredient (JP-A-2000-24658) and the like are known, and examples of the dephosphorizing method in water include aluminum oxide and sodium oxide. Of dewatering seawater by bringing seawater into contact with porous alumina (Japanese Patent Application Laid-Open No. 6-328067), adding magnesium ions to phosphate wastewater containing ammonium ions, adjusting the pH value to 8 or more, and then adding phosphorus A method in which phosphorus in wastewater is precipitated as magnesium ammonium phosphate particles on the surface layer of the above-mentioned granular material by passing through a packed layer of the granular material containing magnesium ammonium phosphate (Japanese Patent Application Laid-Open No. 63-200888). A method of adding a salt solution to the aqueous solution to adjust the electric conductivity of the solution to 2000 micromhos / cm or more when contacting with a granular material having a phosphorus removing ability in the presence of ions to perform contact dephosphorization. (Japanese Unexamined Patent Publication (Kokai) No. 3-207489), a phosphorous-containing wastewater is brought into contact with a composite metal hydroxide containing a divalent metal and a trivalent metal, and the Adsorbing components, then a method of reproducing the phosphorus adsorbent which has adsorbed the phosphorus component is treated with an aqueous solution of an alkali metal salt or alkaline earth metal salts (JP-A-11-57695) are known.
[0004]
However, these dephosphorizing agents and dephosphorization methods reduce the phosphorus removal rate when other anions, particularly sulfate ions, coexist, and cannot actually completely prevent eutrophication in seawater and the like. Was.
[0005]
[Problems to be solved by the invention]
Under such circumstances, the present invention enhances the selectivity between phosphorus dissolved in water and other anions, and even in the presence of other anions, the removal rate of phosphorus is selectively increased. The purpose is to provide a high dephosphorizing agent.
[0006]
[Means for Solving the Problems]
The present inventors have intensively studied to develop a dephosphorizing agent capable of selectively removing phosphorus with a high selectivity even when coexisting with other anions. In the composite metal hydroxide, that is, in the heat-treated product of the crystal of the composite metal hydroxide having a predetermined composition, the object can be achieved by adjusting the selectivity coefficient of phosphorus to sulfate ions to be 5 or more. The present invention has been made based on this finding.
[0007]
That is, the present invention has the general formula M II 1-x M III x (OH) 2 A n- y · mH 2 O (I)
(At least one is M II in formula selected from the divalent metal, M III is at least one selected from among trivalent metal, A n-represents an n-valent anion, x, y and m are numbers satisfying 0 <x ≦ 0.67, 0 <y ≦ 1, 0 ≦ m ≦ 2)
A highly selective dephosphorizing agent, characterized in that a heat-treated product of a crystal of a composite metal hydroxide represented by the following formula is used as an active ingredient, and the selectivity of phosphorus dissolved in water to sulfate ions is 5 or more, And a mixed aqueous solution of a water-soluble salt of an inorganic acid or an organic acid and an alkali hydroxide is dropped into an aqueous solution containing a water-soluble compound of a divalent metal and a water-soluble compound of a trivalent metal, and then kept at a temperature of 0 to 90 ° C. reacted Te, formula M II 1-x M III x (OH) 2 A n- y · mH 2 O (I)
(At least one is M II in formula selected from the divalent metal, M III is at least one selected from among trivalent metal, A n-represents an n-valent anion, x, y and m are numbers satisfying 0 <x ≦ 0.67, 0 <y ≦ 1, 0 ≦ m ≦ 2)
A precipitate of crystals of the composite metal hydroxide represented by or a water-soluble salt of an inorganic or organic acid and an alkali hydroxide are added to an aqueous solution containing a water-soluble compound of a divalent metal and a water-soluble compound of divalent manganese. After the dropwise addition of a mixed aqueous solution of the following formula, the reaction is carried out under oxidizing conditions while maintaining the temperature at 0 to 90 ° C., and the general formula M II 1-x Mn (III) x (OH) 2 An - y · mH 2 O (II )
(M II, A n-, x , y and m in the formula have the same meanings as defined above)
Wherein a precipitate of crystals of the composite metal hydroxide represented by the formula (1) is formed, and then the precipitate is separated and heat-treated at 200 to 500 ° C. to provide a method for producing a dephosphorizing agent.
[0008]
BEST MODE FOR CARRYING OUT THE INVENTION
Examples of the divalent metal M II in the general formula (I) of the present invention include Mg, Zn, Cu (II), Co (II), and Ni (II). Mg, Zn and Co (II). Examples of the trivalent metal M III include Al, Mn (III), Fe (III), and Co (III), and Mn and Al are particularly preferred. Each of M II and M III may be a single metal or a composite of two or more metals.
[0009]
Next, the anion A n- is in formula (I), it is necessary to have an ion-exchange, for example carbonate ions, sulfate ion, a halogen ion, such as a hydroxide ion. Of these, hydroxide ions are particularly preferred, and carbonate ions and hydrogen carbonate ions are preferred in that they are easily converted to hydroxide ions by heat treatment.
[0010]
The dephosphorizing agent of the present invention is clearly different from the conventional dephosphorizing agent in that it is based on the reaction between phosphoric acid and a metal, whereas it is based on ion exchange. In addition, this ion exchange is selectively performed only with the ionizer of phosphoric acid even when carbonate ions, halogen ions, nitrate ions, and sulfate ions coexist.
[0011]
Next, x in the general formula (I) is a number in a range of more than 0 and 0.67 or less, and m needs to be a number in a range between 0 and 2.
Then, the anion A n- quantities y are, Mn, when containing a transition metal such as Co, for valency is not single, the y is the theoretical value with respect to (x / n), the allowable range of about 30% have. Particularly preferred are those in which x is around 0.33 and m is in the range of 0 ≦ m ≦ 2.
[0012]
The dephosphorizing agent of the present invention contains a heat-treated product of a crystal of a composite metal hydroxide having a composition represented by the general formula (I) as an active ingredient, and reacts with sulfuric acid ions of phosphorus dissolved in water. It is necessary that the selection coefficient is 5 or more. This heat-treated product has a characteristic that the crystal structure cannot be maintained and the layer structure is broken, but the layer structure is recovered when phosphorus is adsorbed. This high selectivity for phosphorus is considered to be exhibited by voids between layers of the dephosphorizing agent. That is, it is considered that the layer structure is disordered in the dephosphorizing agent of the present invention, and the size of the void (4 to 6 °) matches the size of the phosphate ion.
Unlike the interlayer gap d determined by X-ray diffraction, the size of the void cannot be determined directly, but is determined indirectly due to selective adsorption and the like. The size of the substance having the same d value varies depending on the type of the constituent element and the heat treatment conditions.
[0013]
Therefore, in the present invention, in order to heat-treat a crystal of the composite metal hydroxide having the composition in the general formula (I) to obtain a crystal having a predetermined selectivity, first, a composite metal hydroxide having a suitable composition It is necessary to prepare crystals of Examples of such a composition include those in which M III in the general formula (I) is Mn, Al, or a composite of Al and Co, and M II is Mg, Ni, Zn, or a composite of Co and Zn. .
[0014]
And, examples of the crystal of the composite metal hydroxide having such a composition, general formula Mg 1-x Mn x (OH ) 2 (HCO 3) y · mH 2 O (III)
Zn 1-x Al x (OH) 2 (HCO 3 ) y · mH 2 O (IV)
(Co, Zn) 1-x (Co, Al) x (OH) 2 (HCO 3 ) y · mH 2 O (V)
And Ni 1-x Mn x (OH ) 2 (HCO 3) y · mH 2 O (VI)
(However, x, y and m in each formula have the same meaning as described above.)
Can be mentioned.
The above (Co, Zn) and (Co, Al) mean that the divalent metal Zn and the trivalent metal Al are partially substituted by Co. When a transition metal such as Mn or Co is included, the value of y does not always match the theoretical value (x / n) because the valence is not single. Therefore, the value of y is allowed in the range of 0-1.
[0015]
By heating the bicarbonate of the crystal of the composite metal hydroxide having such a composition at a temperature in the range of 200 to 500 ° C., preferably 250 to 350 ° C., the decarboxylation reaction proceeds, and the compound becomes a hydroxide type. Change. When Mn, Co, and Fe are contained as metal components, these have a plurality of valences, so that the temperature, the atmosphere, the reaction time, and the like are appropriately controlled to have a necessary configuration and an effective layer void. It is necessary to.
[0016]
In the method of the present invention, the water-soluble compound of a divalent metal and the water-soluble compound of a trivalent metal used as a raw material include halides, nitrates, and sulfates of metals such as Mn, Mg, Zn, Co, Ni, Fe, and Al. , Carbonate and the like. In addition, hydroxides such as magnesium hydroxide, aluminum hydroxide and iron hydroxide can be used if desired.
[0017]
Then, as the water-soluble salts of inorganic or organic acids the anions A n- sources in the general formula (I), carbonate, sulfate, hydrochloric, inorganic acid or oxalic acid such as nitric acid, acetic acid , Citric acid, alkali metal salts of organic acids such as lactic acid, alkaline earth metal salts, ammonium salts and the like are used. Particularly preferred are alkali metal carbonates and alkali metal hydrogencarbonates, for example, sodium carbonate, potassium carbonate, Sodium bicarbonate and potassium bicarbonate. Examples of the alkali hydroxide used in combination with the above include alkali metal and ammonium hydroxides such as sodium hydroxide, potassium hydroxide, and ammonium hydroxide.
This mixed aqueous solution of a water-soluble salt of an inorganic acid or an organic acid and an alkali hydroxide is used in an amount of about 1 to 40 moles per mole of the divalent metal and trivalent metal compounds.
[0018]
When a water-soluble compound of divalent manganese is used in place of the water-soluble compound of a trivalent metal, a mixed aqueous solution of a water-soluble salt of an inorganic acid or an organic acid and an alkali hydroxide is added dropwise, and then the oxidizing conditions are applied. By reacting slowly at a temperature of 0 to 90 ° C. under, for example, an atmosphere in which the atmosphere is not particularly controlled, the general formula M II 1-x Mn (III) x (OH) 2 An - y · mH 2 O (II )
(A n− in the formula represents an n-valent anion, and M II , x, y and m have the same meaning as described above.)
The precipitate of the crystal of the composite metal hydroxide represented by
[0019]
A mixed aqueous solution of a water-soluble salt of an inorganic acid or an organic acid and an alkali hydroxide is added dropwise to the water-soluble compound of a divalent metal and the water-soluble compound of a trivalent metal prepared as described above, and then 0 to 90 ° C. At a temperature of This reaction is usually carried out for 1 to 5 hours with stirring. By this reaction, crystals of the composite metal hydroxide represented by the general formula (I) precipitate. The crystals are separated by filtration or centrifugation, washed with water until neutral, and air-dried. Thereby, crystals of the composite metal hydroxide are obtained as a powder.
[0020]
This powder is found to be hydrotalcite having a composition represented by the general formula (I) from X-ray structure analysis, composition analysis, valence analysis of each metal, and mass reduction by TG-TDA analysis.
[0021]
Next, the crystal of this composite metal oxide is placed in an electric furnace and subjected to a heat treatment at a temperature of 200 to 500 ° C., preferably 250 to 350 ° C. for 2 to 10 hours. By this heat treatment, anions in the composition are eliminated and the layer structure is rearranged, so that a highly selective dephosphorizing agent having a selectivity of 5 or more for phosphorus dissolved in water is obtained.
[0022]
The thus obtained dephosphorizing agent of the present invention coexists in a phosphorus-dissolved aqueous solution with anions such as chloride ions, nitrate ions, sulfate ions, and carbonate ions, which are generally considered to inhibit the adsorption of phosphorus. However, phosphorus can be selectively and efficiently adsorbed.
[0023]
【Example】
Next, the present invention will be described in more detail with reference to examples, but the present invention is not limited to these examples.
The selectivity of the phosphorus desorbing agent in each of the examples for the sulfate ion of phosphorus dissolved in water was determined as follows.
[0024]
A mixed anion adsorption experiment was performed using an equimolar (0.02 mmol) mixed solution of carbonate ion, chloride ion, nitrate ion, dihydrogen phosphate ion, and sulfate ion (all used as sodium salts). Calculate the adsorption capacity of each anion from the amount of reduction of the ion species, and take the ratio of the adsorption capacity of dihydrogen phosphate ion as the numerator and the adsorption capacity of other anions as the denominator. The selectivity of dissolved phosphorus for the ions was taken as the coefficient.
[0025]
Example 1
An aqueous solution containing 80 parts by mass of sodium hydroxide and 40 parts by mass of sodium carbonate was dropped into an aqueous solution containing 1 part by mass of manganese (II) chloride and 3 parts by mass of magnesium chloride while stirring, and reacted at 60 ° C. for 2 hours, A precipitate was obtained. Then, the precipitate was centrifuged, washed with water until neutral, and air-dried. As a result of powder X-ray structure analysis, composition analysis, and manganese valence analysis, the product was identified as Mg 0.75 Mn 0.25 (OH) 2 (HCO 3 ) 0.25 · mH 2 O type hydrotalcite. Was done. Further, the value of m was found to be between 1 and 2 from the mass reduction by TG-TDA analysis.
[0026]
This sample was heated in an electric furnace at 300 ° C. for 4 hours to produce a dephosphorizing agent, and the anion adsorption performance was measured by the following method. That is, 0.02 mmol of carbonate ion, chloride ion, nitrate ion, dihydrogen phosphate ion and sulfate ion (all of them are sodium salts) were added to 0.1 g of this sample, and mixed anion adsorption experiment was performed at 27 ° C. After 3 days, the solution was analyzed by anion chromatography. As a result, 99% of the added dihydrogen phosphate ion was adsorbed, whereas 9% of the sulfate ion was adsorbed. That is, the selectivity coefficient of the dissolved phosphorus with respect to the sulfate ion in the water of the dephosphorizing agent was 11. In addition, when the saturated adsorption capacity of phosphoric acid alone was measured, it was 1.4 mmol / g.
[0027]
Example 2
An aqueous solution containing 80 parts by mass of sodium hydroxide and 40 parts by mass of sodium carbonate was added dropwise to an aqueous solution containing 1 part by mass of aluminum chloride and 3 parts by mass of zinc chloride while stirring, and the mixture was reacted at 60 ° C. for 2 hours. Obtained. The precipitate was centrifuged, washed with water until neutral, and air-dried. The product was subjected to powder X-ray structure analysis and composition analysis, and as a result, was identified as Zn 0.75 Al 0.25 (OH) 2 (HCO 3 ) 0.25 · mH 2 O-type hydrotalcite. In addition, the value of m was found to be between 1 and 2 from the mass decrease by TG-TDA analysis.
[0028]
Next, this product was heated in an electric furnace at 300 ° C. for 4 hours to produce a dephosphorizing agent, and its anion adsorption performance was measured by the following method. That is, 0.02 mmol of carbonate ion, chloride ion, nitrate ion, dihydrogen phosphate ion, and sulfate ion (all of them are sodium salts) were added to 0.1 g of the dephosphorizing agent, and the mixed anion adsorption experiment was performed for 27 days. After 3 days at C, the solution was analyzed by anion chromatography. 73% of dihydrogen phosphate ions were adsorbed, while 6% of sulfate ions were adsorbed. Therefore, the selectivity of dissolved phosphorus for sulfate ions in water of this dephosphorizing agent was 13. In addition, when the saturated adsorption capacity of phosphoric acid alone was measured, it was 1.2 mmol / g.
[0029]
Example 3
An aqueous solution containing 40 parts by mass of sodium carbonate is added dropwise to an aqueous solution containing 1 part by mass of aluminum chloride, 1.5 parts by mass of cobalt (II) chloride, and 1.5 parts by mass of zinc chloride while stirring, and then an aqueous solution of sodium hydroxide is used. The pH was adjusted to 9 with. This mixture was reacted at 80 ° C. for 4 hours to obtain a precipitate. Next, the precipitate was centrifuged, washed with water until neutral, and dried at 40 ° C. for 1 day. As a result of powder X-ray structure analysis, the product was identified as hydrotalcite. Also, the value of m was found to be between 1 and 2 from the decrease in mass by TG-TDA analysis.
[0030]
Next, this product was heated in an electric furnace at 300 ° C. for 4 hours to produce a dephosphorizing agent, and the anion adsorption performance was measured by the following method. That is, 0.02 mmol of carbonate ion, chloride ion, nitrate ion, dihydrogen phosphate ion, and sulfate ion (all of them are sodium salts) were added to 0.1 g of the dephosphorizing agent, and the mixed anion adsorption experiment was performed for 27 days. After 3 days at ℃, the solution was analyzed by anion chromatography. As a result, the adsorption of dihydrogen phosphate ions was 91%, while the adsorption of sulfate ions was 2%. Therefore, the selectivity of dissolved phosphorus for sulfate ions in water of this dephosphorizing agent was 55. In addition, when the saturated adsorption capacity of phosphoric acid alone was measured, it was 0.6 mmol / g.
[0031]
Example 4
An aqueous solution containing 80 parts by mass of sodium hydroxide and 40 parts by mass of sodium carbonate was added dropwise to an aqueous solution containing 1 part by mass of manganese (II) chloride and 3 parts by mass of nickel chloride while stirring, and reacted at 60 ° C. for 2 hours, A precipitate was obtained. The precipitate was centrifuged, washed with water until neutral, and air-dried. The product thus obtained was subjected to powder X-ray structure analysis, composition analysis, and valence analysis of manganese, and as a result, Ni 0.75 Mn 0.25 (OH) 2 (HCO 3 ) 0.25 · mH 2 O type was obtained. Was identified as hydrotalcite. In addition, the value of m was found to be between 1 and 2 from the mass decrease by TG-TDA analysis.
[0032]
This product was heated in an electric furnace at 300 ° C. for 4 hours to produce a dephosphorizing agent, and the anion adsorption performance was measured by the following method. That is, 0.02 mmol of carbonate ion, chloride ion, nitrate ion, dihydrogen phosphate ion, and sulfate ion (all of them are sodium salts) were added to 0.1 g of the dephosphorizing agent, and the mixed anion adsorption experiment was performed for 27 days. After 3 days at ℃, the solution was analyzed by anion chromatography. As a result, 24% of dihydrogen phosphate ion was adsorbed and 4% of sulfate ion was adsorbed. Therefore, the selectivity of dissolved phosphorus for sulfate ions in water of this dephosphorizing agent was 6. In addition, when the saturated adsorption capacity of phosphoric acid alone was measured, it was 0.16 mmol / g.
[0033]
Comparative Example A commercially available Mg 0.75 Al 0.25 (OH) 2 (HCO 3 ) 0.25 type hydrotalcite heated in an electric furnace at 300 ° C. for 4 hours was used as a dephosphorizing agent. The adsorption performance was measured by the following method. To 0.1 g of the dephosphorizing agent, 0.02 mmol of carbonate ion, chloride ion, nitrate ion, dihydrogen phosphate ion and sulfate ion (all sodium salts) were added, and the mixed anion adsorption experiment was performed at 27 ° C. After 3 days, the solution was analyzed by anion chromatography. As a result, 80% of the added dihydrogen phosphate was adsorbed, whereas 36% of sulfate, 13% of chloride and 10% of nitrate were added. Adsorbed, these were mainly ion exchanged with carbonate ions. In addition, when the saturated adsorption capacity of phosphoric acid alone was measured, it was 1.1 mmol / g. Further, the selectivity of dissolved phosphorus for sulfate ions in water of this dephosphorizing agent was about 2.
[0034]
From the above results, it can be seen that the highly selective dephosphorizing agent of the present invention has higher phosphorus selectivity than the conventional one.
[0035]
【The invention's effect】
According to the present invention, a highly selective dephosphorizing agent capable of selectively adsorbing phosphorus can be obtained even when an anion such as a halogen ion, a nitrate ion, a sulfate ion, or a carbonate ion is present in an aqueous solution containing phosphorus. Therefore, it is useful for removing phosphorus from seawater.
Claims (9)
MII 1−xMIII x(OH)2An− y・mH2O
(式中のMIIは二価金属の中から選ばれた少なくとも1種、MIIIは三価金属の中から選ばれた少なくとも1種、An−はn価の陰イオンを示し、x、y及びmは、0<x≦0.67、0<y≦1、0≦m≦2を満足する数である)
で表わされる複合金属水酸化物の結晶の加熱処理物を有効成分とし、かつ水に溶存しているリンの硫酸イオンに対する選択係数が5以上であることを特徴とする高選択性脱リン剤。Formula M II 1-x M III x (OH) 2 A n- y · mH 2 O
(At least one is M II in formula selected from the divalent metal, M III is at least one selected from among trivalent metal, A n-represents an n-valent anion, x, y and m are numbers satisfying 0 <x ≦ 0.67, 0 <y ≦ 1, 0 ≦ m ≦ 2)
A highly selective dephosphorizing agent characterized in that a heat-treated product of a crystal of a composite metal hydroxide represented by the formula (1) is used as an active ingredient, and that the selectivity of phosphorus dissolved in water to sulfate ions is 5 or more.
MII 1−xMIII x(OH)2An− y・mH2O
(式中のMIIは二価金属の中から選ばれた少なくとも1種、MIIIは三価金属の中から選ばれた少なくとも1種、An−はn価の陰イオンを示し、x、y及びmは、0<x≦0.67、0<y≦1、0≦m≦2を満足する数である)
で表わされる複合金属水酸化物の結晶の沈殿を生成させ、次いで、この沈殿を分別し、200〜500℃において加熱処理することを特徴とする脱リン剤の製造方法。A mixed aqueous solution of a water-soluble salt of an inorganic acid or an organic acid and an alkali hydroxide is dropped into an aqueous solution containing a water-soluble compound of a divalent metal and a water-soluble compound of a trivalent metal, and the temperature is maintained at 0 to 90 ° C. reacted, the general formula M II 1-x M III x (OH) 2 A n- y · mH 2 O
(At least one is M II in formula selected from the divalent metal, M III is at least one selected from among trivalent metal, A n-represents an n-valent anion, x, y and m are numbers satisfying 0 <x ≦ 0.67, 0 <y ≦ 1, 0 ≦ m ≦ 2)
A method for producing a dephosphorizing agent, comprising: forming a precipitate of a crystal of a composite metal hydroxide represented by the formula: and then separating the precipitate and performing a heat treatment at 200 to 500 ° C.
MII 1−xMn(III)x(OH)2An− y・mH2O
(式中のMIIは二価金属の中から選ばれた少なくとも1種、An−はn価の陰イオンを示し、x、y及びmは、0<x≦0.67、0<y≦1、0≦m≦2を満足する数である)
で表わされる複合金属水酸化物の結晶の沈殿を生成させ、次いで、この沈殿を分別し、200〜500℃において加熱処理することを特徴とする脱リン剤の製造方法。An aqueous solution containing a water-soluble compound of a divalent metal and a water-soluble compound of divalent manganese is dropped into a mixed aqueous solution of a water-soluble salt of an inorganic acid or an organic acid and an alkali hydroxide, and then oxidized at 0 to 90 ° C. reacted keeping the temperature, the general formula M II 1-x Mn (III ) x (OH) 2 a n- y · mH 2 O
(At least one is M II in formula selected from among the divalent metal, A n-represents an n-valent anion, x, y and m are, 0 <x ≦ 0.67,0 <y ≦ 1, 0 ≦ m ≦ 2)
A method for producing a dephosphorizing agent, comprising: forming a precipitate of a crystal of a composite metal hydroxide represented by the formula: and then separating the precipitate and performing a heat treatment at 200 to 500 ° C.
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