JPS62286539A - Phosphate ion adsorbent and its preparation - Google Patents

Phosphate ion adsorbent and its preparation

Info

Publication number
JPS62286539A
JPS62286539A JP12922586A JP12922586A JPS62286539A JP S62286539 A JPS62286539 A JP S62286539A JP 12922586 A JP12922586 A JP 12922586A JP 12922586 A JP12922586 A JP 12922586A JP S62286539 A JPS62286539 A JP S62286539A
Authority
JP
Japan
Prior art keywords
activated carbon
adsorbent
phosphate ion
hydrated
lanthanide
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Pending
Application number
JP12922586A
Other languages
Japanese (ja)
Inventor
Kenji Motojima
本島 健次
Naoyuki Sugii
杉井 直行
Hiroshi Takeda
広 武田
Togo Asami
淺見 藤吾
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.)
JOHOKU KAGAKU KOGYO KK
Daiichi Kigenso Kagaku Kogyo Co Ltd
Original Assignee
JOHOKU KAGAKU KOGYO KK
Daiichi Kigenso Kagaku Kogyo Co Ltd
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 JOHOKU KAGAKU KOGYO KK, Daiichi Kigenso Kagaku Kogyo Co Ltd filed Critical JOHOKU KAGAKU KOGYO KK
Priority to JP12922586A priority Critical patent/JPS62286539A/en
Publication of JPS62286539A publication Critical patent/JPS62286539A/en
Pending legal-status Critical Current

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

Abstract

PURPOSE:To increase the adsorbing capacity of a phosphate ion at pH1-6, by preparing a phosphate ion adsorbent by supporting one or more kind of hydrated oxide of one or more kind of a metal selected from Ti, Zr, Sn, and lanthanide by activated carbon. CONSTITUTION:Activated carbon is impregnated with an aqueous solution of a soluble salt of one or more kind of a metal selected from Ti, Zr, Sn and lanthanide. Subsequently, the impregnated activated carbon is dried and the aforementioned soluble salt is converted to hydrated oxide through the reaction with ammonia or NaOH to prepare a phosphate ion adsorbent. It is pref. to further age the aforementioned hydrated oxide at 70-150 deg.C and the wt. ratio of the hydrated metal oxide to activated carbon is pref. set to 0.05-0.8. As the soluble metal salt, TiCl4, Ti(SO4)2, ZrOCl2, ZrO(NO3)2, SnCl, LCl3 and LNO3 (L is lanthanide) is pref.

Description

【発明の詳細な説明】 〔産業上の利用分野〕 本発明は、リン酸イオン吸着剤およびその製造方法に関
する口 〔従来の技術〕 現在、内陸湖沼を始めとする閉鎖性水域の富栄養化現象
は重大な社会問題となっている。
[Detailed Description of the Invention] [Industrial Application Field] The present invention relates to a phosphate ion adsorbent and a method for producing the same [Prior Art] At present, the eutrophication phenomenon of closed water bodies including inland lakes and marshes has become a serious social problem.

この現象の原因の一つはリン酸イオンの流入であり、周
辺諸施設よりの廃水中のリン酸イオンの除去低減は早急
に解決しなければならない重要事項である。
One of the causes of this phenomenon is the influx of phosphate ions, and reducing the removal of phosphate ions from wastewater from surrounding facilities is an important issue that must be resolved immediately.

ところで、現行の廃水中のリン酸イオンの除去法は、ア
ルミニウム塩、鉄塩などを廃水中に投入し、それらの金
属の水和酸化物にリン酸イオンを吸着させ【沈殿せしめ
るいわゆる凝集沈殿法であるが、この手法では本質的に
多量のスラッジを生じ、その処理が必要となり、満足し
うる方法とはいえない。
By the way, the current method for removing phosphate ions from wastewater is the so-called coagulation-sedimentation method, in which aluminum salts, iron salts, etc. are added to the wastewater, and the hydrated oxides of these metals adsorb and precipitate the phosphate ions. However, this method essentially generates a large amount of sludge, which requires treatment, and is not a satisfactory method.

一方、チタン、ジルコニウム、スズあるいはランタニド
などの金属の水和酸化物は陰イオン交換性を持っており
、特にリン酸イオンに対する吸着性が強いことから、こ
れらの金属の水和酸化物を用いる吸着剤の開発が試みら
れている口しかし、上記金属の水和酸化物は一般にゲル
状であり、濾過処理あるいはリン酸イオンの吸脱着処理
は容易ではないりこの対策として、たとえば適出量の第
一鉄塩を加えておき、含水マグネタイトと共にチタン、
ジルコニウム等の水和酸化物を共沈させ、乾燥後ポリエ
ステルあるいはポリウレタン樹脂を用いて造粒した吸着
剤が開発されている[特開昭56−118734および
57−50543、並びに玉突、矢野、骨内 全国都市
清掃研究発表会論文集(1986−2)参照]nLかし
ながら、この吸着剤の製法はかならずしも簡単でなく、
また高分子を用いて造粒しているため、一部の水和金属
酸化物の表面が樹脂に被われ、そのリン酸イオン吸着能
が損われるものと考えられる。
On the other hand, hydrated oxides of metals such as titanium, zirconium, tin, or lanthanides have anion exchange properties and have particularly strong adsorption properties for phosphate ions, so adsorption using hydrated oxides of these metals is difficult. However, the hydrated oxides of the metals mentioned above are generally in the form of a gel, and filtration or adsorption/desorption of phosphate ions is not easy. Add iron salt, and add titanium along with hydrated magnetite.
Adsorbents have been developed in which hydrated oxides such as zirconium are co-precipitated, dried and then granulated using polyester or polyurethane resin [JP-A-56-118734 and 57-50543, and Tamatsuki, Yano and Hone. (Refer to Proceedings of the National Urban Cleaning Research Conference (1986-2)) However, the manufacturing method for this adsorbent is not necessarily easy;
Furthermore, since the granules are granulated using a polymer, it is thought that some of the surface of the hydrated metal oxide is covered with the resin, which impairs its ability to adsorb phosphate ions.

〔発明が解決しようとする問題点〕[Problem that the invention seeks to solve]

本発明者らは、リン酸イオン吸着後のスラ・ンジの発生
がなく、比軟的に容易に製造することのできるリン酸イ
オン吸着剤を開発するべく鋭意検討を進め几結果、本発
明を完成するに至っtものである。
The present inventors have carried out extensive studies to develop a phosphate ion adsorbent that does not generate sludge after adsorbing phosphate ions and can be easily manufactured in a relatively soft manner.As a result, the present invention has been developed. It is almost complete.

〔問題点を解決するための手段〕[Means for solving problems]

本発明によれば、チタン、ジルコニウム、スズおよびラ
ンタニドから選ばれる少くともlF!の金属の水和酸化
物を活性炭に担持せしめてなるリン酸イオン吸着剤が提
供される、 本発明者は、即ち、チタン、ジルコニウム、スズま友は
ランタニドの水和酸化物を、きわめて大きな吸着表面°
を持っている活性炭の細孔内に沈着させ、所望により熟
成して安定「ヒリン酸イオンの吸脱着に耐え得る吸着剤
の開発に成功したものである。本発明の吸着剤において
は、水和金属酸化物の活性炭に対する重量比は0.05
〜0.8であるのが好ましい口 本発明の吸着剤は、本質的には活性炭と同等であり、粒
状、破砕状あるいは粉末状などその粒度あるいは形状は
多様のものが製造でき、外観は活性炭そのもので、機械
的強度も大きく、耐酸性かつ耐アルカリ性で、リン酸イ
オンの吸着、脱着を繰り返し行なうことができ、また固
定床、流動床など通常の工業的吸着装置の使用条件を充
分光たすことができる。しかして、リン酸の吸脱着性能
は過去に存在した吸着剤のいずれよりも優れており、ま
几その製造も簡単である。
According to the invention, at least 1F! selected from titanium, zirconium, tin and lanthanides! The present inventor provides a phosphate ion adsorbent comprising hydrated oxides of metals supported on activated carbon. surface °
We have succeeded in developing an adsorbent that can withstand the adsorption and desorption of hyrate ions. The weight ratio of metal oxide to activated carbon is 0.05
The adsorbent of the present invention is essentially equivalent to activated carbon, and can be produced in various particle sizes or shapes such as granules, crushed or powdered, and has an appearance similar to that of activated carbon. As such, it has great mechanical strength, is acid resistant and alkali resistant, and can repeatedly adsorb and desorb phosphate ions, and is fully compatible with the operating conditions of regular industrial adsorption equipment such as fixed beds and fluidized beds. can be done. Therefore, the adsorption and desorption performance of phosphoric acid is superior to any of the previously existing adsorbents, and the manufacture of the adsorbent is simple.

本発明の吸着剤は、概略、次の手法で製造することがで
きる0即ち、チタン、ジルコニウム、スズおよびランタ
ニドから選ばれる金属の可溶性基、例えばTICt4 
、TI (804)2 p Zr0Ct2 、ZrC2
41Zr(NO3)!  、Zr0(SQ、)、Zr0
(CH3COO)、。
The adsorbents of the present invention generally include soluble groups of metals selected from titanium, zirconium, tin and lanthanides, such as TICt4, which can be produced by the following method.
, TI (804)2 p Zr0Ct2 , ZrC2
41Zr (NO3)! , Zr0(SQ, ), Zr0
(CH3COO),.

5nCt4やランタニドの塩化物または硝酸塩などを用
い、それらの単独もしくは二種以上の混合物の水溶液を
調製する。溶液の濃度は、用いる塩の浴解度(もよるが
、0.2〜2.0モル濃度が適当である。しかし、この
濃度については厳密である必要はなく、また尿溶液中で
金属が加水分解するのを防ぐために多少の無機酸もしく
は有機塩を添加しておいても差し支えない0之だし、こ
のような酸を過剰に加えておくことは後の操作にとって
有利ではない。
Using 5nCt4, lanthanide chloride or nitrate, etc., an aqueous solution of these alone or a mixture of two or more is prepared. The concentration of the solution depends on the bath solubility of the salt used (0.2 to 2.0 molar concentration is appropriate. However, this concentration does not need to be strict, and metals in the urine solution are Although it is acceptable to add some inorganic acid or organic salt to prevent hydrolysis, it is not advantageous for subsequent operations to add an excess of such acid.

この溶液1tに対しほぼ1〜1.3 kfの割合で乾燥
した活性炭を加え、混和して活性炭に溶液を吸着せしめ
る口溶液と活性炭との混和割合は必ずしもこの値でなく
ともよいが、活性炭の割合が大きいときは吸着が不、均
一と゛なる危険があり、溶液量が多いときは乾燥の操作
に特開を要して不経済である口 溶液を吸着した活性炭を混和しながら、幸外線加熱など
で水分を除く0この場合、加熱温度は90℃前後、水分
の除去率は加えた水の70チ程度を目標とするが、いず
れの条件も厳密である必要はない。ただし、この乾燥処
理で吸着させた塩が多量に活性炭粒の表面ににじみ出て
晶出するような乾燥条件は好ましくない0 次いで、活性炭をアンモニアガス雰囲気中に放置してア
ンモニアガスを吸収させ、活性炭の細孔内にあらかじめ
吸蔵せしめておいた金属の水和酸化物を形成せしめる0 かくして、活性炭細孔内に生成せしめ友金属の水和酸化
物は容易には活性炭より溶出することはない。なお、本
操作では、具体的には活性炭を胃いt密閉容器内にアン
モニアガスを導入するのがよいが、簡単には容器内の一
隅に濃アンモニア水を置くといった方法でも目的を達成
しうる。
Add dry activated carbon at a rate of approximately 1 to 1.3 kf to 1 ton of this solution and mix to make the activated carbon adsorb the solution.The mixing ratio of the solution and activated carbon does not necessarily have to be this value, but the activated carbon If the ratio is large, there is a risk that the adsorption will be insufficient or uniform, and if the amount of solution is large, the drying operation will require a special patent application, making it uneconomical. In this case, the heating temperature is about 90° C., and the moisture removal rate is targeted to be about 70 degrees of the added water, but neither condition needs to be strict. However, drying conditions where a large amount of the salt adsorbed in this drying process oozes out and crystallizes on the surface of the activated carbon particles are unfavorable.Next, the activated carbon is left in an ammonia gas atmosphere to absorb ammonia gas. Thus, the hydrated oxides of metals that have been occluded in advance in the pores of the activated carbon are not easily eluted from the activated carbon. In this operation, it is better to introduce ammonia gas into a sealed container while smothering the activated carbon, but the purpose can also be achieved simply by placing concentrated ammonia water in one corner of the container. .

1L器内全減圧にしたのち、アンモニアガスを加圧導入
すればさらに効果的であるが、活性炭の細孔内では中和
反応が行なわれ、発熱を伴うから、多量を取り扱う際に
は発生する反応熱に留意しなければならないQしかし、
この発熱はアンモニアガスの導入量で調整することによ
り容易に制御することができるり なお、アンモニアガスの替りにアルカリ水層液を用いて
も水和酸化物を生成することができるが操作上経済的で
は碌い。
It is more effective to introduce ammonia gas under pressure after completely reducing the pressure in the 1L container, but a neutralization reaction takes place within the pores of activated carbon, which is accompanied by heat generation, which may occur when handling large quantities. Q. However, the heat of reaction must be taken into consideration.
This heat generation can be easily controlled by adjusting the amount of ammonia gas introduced.It is also possible to generate hydrated oxides by using an aqueous alkali solution instead of ammonia gas, but this is more economical in terms of operation. It's good on target.

所望により、このようにして水和金属酸fヒ物をその細
孔内に固定した活性炭全加熱して水和酸化物を熟成する
のが好ましい。この際、強熱すると脱水が進み過ぎ、リ
ン酸イオン吸着能が減殺される危険があり、常圧では8
0−100℃程度に加熱するにとどめるのが適当である
口その後水洗して、反応の結果生じ次回溶性のアンモニ
ウム塩などを除去したのち、要すれば一旦乾燥して保存
し、使用する。
If desired, it is preferable to fully heat the activated carbon in which the hydrated metal acid or arsenate has been fixed in its pores to ripen the hydrated oxide. At this time, if ignited, there is a danger that dehydration will progress too much and the phosphate ion adsorption capacity will be reduced.
It is appropriate to heat it only to about 0-100°C. Afterwards, it is washed with water to remove soluble ammonium salts generated as a result of the reaction, and if necessary, it is once dried and stored for use.

本発明のリン酸イオン吸着剤は、既に報告されているジ
ルコニウム水和酸化物全主体とし几吸着剤と同様にpH
1〜6の酸性域においてリン酸イオンの吸着能が大きく
、アルカリ側(pH>9)ではこれを離脱する0従って
、被処理水全僅かに酸性にして本吸着剤を充填したカラ
ムに通すことによりリン酸イオンを吸着せしめ、その後
アルカリ溶液でリン酸イオンを脱離回収するとともに吸
着カラムを再生することができる。
The phosphate ion adsorbent of the present invention is composed mainly of zirconium hydrated oxide, and has a pH value similar to that of previously reported zirconium hydrated oxide adsorbents.
The adsorption capacity for phosphate ions is large in the acidic range of pH 1 to 6, and it is removed on the alkaline side (pH > 9). Therefore, all of the water to be treated must be made slightly acidic and passed through the column filled with this adsorbent. The phosphate ions can be adsorbed using the alkaline solution, and then the phosphate ions can be desorbed and recovered using an alkaline solution, and the adsorption column can be regenerated.

以下、実施例を挙げ、本発明を更に説明する。The present invention will be further explained below with reference to Examples.

実施例1 塩化ジルコニルの1.6モル水溶液1t’ii!14f
iする。この水溶液中にはZrとして146?のイオン
が含まれているaこの水溶液中にヤシ穀活性炭(20X
48メツシユ)800 fを添加混合して水溶液を吸着
させる。次に、この活性炭′fr90℃で乾燥する。乾
燥終了は水の70%程度が除去された時点とする0次に
、この活性炭をアシモニア水を入れた密閉容器に入れ、
ときどき攪拌しなからyアンモニアと5時間反応させる
口反応終了後、活性炭を100℃で2時間熟成させる。
Example 1 1.6 molar aqueous solution of zirconyl chloride 1t'ii! 14f
i do This aqueous solution contains 146? Coconut grain activated carbon (20X
48 mesh) is added and mixed to adsorb the aqueous solution. Next, this activated carbon is dried at 90°C. Drying ends when about 70% of the water has been removed.Next, this activated carbon is placed in an airtight container containing Asimonia water.
After the reaction with ammonia for 5 hours with occasional stirring, the activated carbon is aged at 100° C. for 2 hours.

次いで、反応により生じ7を壇f′ヒアンモニウムを取
り除く為水洗する口水洗後、再び100℃で乾燥して吸
着剤を得九〇 実施例2 theジルコニウムの1.6モル水溶液1tを調製する
口この水溶液中にはZr として1462のイオンが含
まれている。この水溶液中にヤシ穀活性炭(20X48
メツシエ)800Fを添加混合して水溶液を吸着させる
0次に、この活性炭全90℃で乾燥する。乾燥終了は水
の70チ程度が除去されt時点とする、次に、この活性
炭に3.3モル水酸化ナトリウム水溶液ltを注加し、
混合して2時間浸漬反応させるり反応終了後、活性炭金
100℃で2時間熟成させる。次いで、反応により生じ
fctxrヒナトリウムおよび過剰の水散化ナトリウム
を取り除く為水洗液pHが中性となるまで水洗する口水
洗後、再び100℃で乾燥して吸着剤を得た口 実施例3 塩化ジルコニルの0.8モルと四塩化チタンの0.8モ
ルとの混合物の水溶液1tを調製する。この水溶液中に
はZr’として73?並びにTi として389のイオ
ンが含まれている。この水溶液中にヤシ穀活性炭(20
X48メツシユ)soorを添加混合して水溶液を吸着
させる。次に、この活性炭を90℃で乾燥する。乾燥終
了は水の70優程度が除去さネ、念時点とする0次に、
この活性炭をアンモニア水を入れ九密閉容器に入れ、時
々攪拌しながらアンモニアと5時間反応させる。反応終
了後、活性炭管100℃で2時間熟成させる・。
Next, the product 7 produced by the reaction was washed with water to remove the hyammonium. After rinsing with water, the adsorbent was dried again at 100°C to obtain an adsorbent. This aqueous solution contains 1462 ions as Zr. Coconut grain activated carbon (20X48
Messier) 800F is added and mixed to adsorb the aqueous solution. Next, this activated carbon is dried at a total temperature of 90°C. Drying is completed at time t, when approximately 70 g of water has been removed.Next, 3.3 molar aqueous sodium hydroxide solution lt is poured into the activated carbon.
The mixture was mixed and reacted by immersion for 2 hours, and after the reaction was completed, the mixture was aged on activated carbon at 100° C. for 2 hours. Next, in order to remove fctxr arsenium produced by the reaction and excess sodium dispersion, the solution was washed with water until the pH of the washing solution became neutral, and then dried again at 100° C. to obtain an adsorbent.Example 3 Chlorination 1 t of an aqueous solution of a mixture of 0.8 mol of zirconyl and 0.8 mol of titanium tetrachloride is prepared. This aqueous solution contains 73? as Zr'? In addition, 389 ions of Ti are included. Coconut grain activated carbon (20
X48 mesh) soor is added and mixed to adsorb the aqueous solution. Next, this activated carbon is dried at 90°C. At the end of drying, approximately 70% of the water has been removed.
This activated carbon was placed in a sealed container containing aqueous ammonia and allowed to react with ammonia for 5 hours with occasional stirring. After the reaction is completed, it is aged in an activated carbon tube at 100°C for 2 hours.

次いで反応により生じた塩化アンモニウムを取り除く為
水洗する◎水洗後、再び100℃で乾燥して吸着剤を得
た。
Next, the mixture was washed with water to remove ammonium chloride generated by the reaction. After washing with water, the adsorbent was dried again at 100°C to obtain an adsorbent.

実施例4 リン酸−ナトリウムを用いてrA 習したリン酸イオ7
500ppm ″f金含有る試験液に0.5 NHCt
もしくは0.5 N NaOHR液を加え、pHが約1
゜3.5,7,9.11または13となるように調整し
た水m液をloo+ntづつ調興した。次に、実施例1
で得られた吸着剤を粉砕して150メツシュ通過・e、
4とし、これを上記の水溶液に各400■添加しtoそ
して2時間振盪後、FMで濾過し、F液のPITならび
にリン酸イオン濃度t−測定した0このときの、吸着剤
のリン酸イオン吸着量とpHとの関係を第1表に示す。
Example 4 Phosphate ion 7 learned by rA using sodium phosphate
0.5 NHCt in the test solution containing 500 ppm "f gold
Or add 0.5 N NaOHR solution until the pH is about 1.
Aqueous solution adjusted to have a concentration of 3.5, 7, 9.11 or 13 was prepared by loo+nt. Next, Example 1
The adsorbent obtained was crushed and passed through 150 meshes.
4 and added 400μ of each to the above aqueous solution, and after shaking for 2 hours, filtered with FM, and measured the PIT and phosphate ion concentration of solution F. At this time, the phosphate ion of the adsorbent Table 1 shows the relationship between adsorption amount and pH.

第1表 0.7  500  86    1041.8   
    94    1022.8   1   i3
6    913.9   1  176    81
4.7    #   230    685.8  
 1  278    557.0    #   3
46    388.6   1  414    2
29.5   1  432    1711、l  
  #   460    1012.3    t 
  474    6実施例5 実施例1で得られた吸着剤を粉砕して150メッシシ通
過品とする0次に、リン酸−ナトリウムを用いて調製し
たリン酸イオン500 ppm を含有する水溶液1O
O1Rt(pH=5)に上記吸着剤粉末を0.2f 、
 0.4F 、0.6Pま九は0.82の黛で加えて2
時間振盪後、P紙でP遍し、戸液中のリン酸イオン濃度
fc測定した0吸着剤のリン酸イオン吸着tを測定した
結果II−第2表に示す。
Table 1 0.7 500 86 1041.8
94 1022.8 1 i3
6 913.9 1 176 81
4.7 #230 685.8
1 278 557.0 #3
46 388.6 1 414 2
29.5 1 432 1711, l
#460 1012.3t
474 6 Example 5 The adsorbent obtained in Example 1 was pulverized to obtain a 150 mesh product.Next, an aqueous solution containing 500 ppm of phosphate ions prepared using sodium phosphate was prepared.
Add the above adsorbent powder to O1Rt (pH=5) at 0.2f,
0.4F, 0.6P maku is 0.82 Mayuzumi, plus 2
After shaking for a period of time, the phosphate ion adsorption t of the adsorbent was measured, and the results are shown in Table II-2.

第 2 表 0.2   500 355    730.4  、
  1228    680.6   1  100 
   670.8       8    62 実施例6 実施例1で得られた吸着剤を内径L2.3wφのガラス
管に層高10c1nとなるよう充填した口充填量は12
m(6F)となる。これにリン酸−ナトリウム音用いて
鯛製したリン酸イオンl OOppm(p)I=5)を
含む水溶液を5VIOで通液し、通過液中のリン酸イオ
ン濃度を測定し之0績果?43表に示す口 簗3表 0.5      検出ぜす 1.0     検出せず 1.58 2.08 2.5     13 3.0     19 実施例7 実施例6でリン酸イオンを吸着し次吸着剤(3tの通液
で全リン酸イオン吸着tFi252Qcであった)に3
N  NaOH水溶液50 met SV 1で通液し
、リン酸イオンを脱離させる。脱離液中のリン酸イオン
を測定し九ところ、吸着しているリン酸イオンの約98
チが脱離されてい7to次に、脱着後の吸着剤1c 0
.5 N H2804水溶液50dt−3Vl11で通
液して再生した後、実施例6と同じ条件で通液して吸着
を行なった。以下、繰り返し再生および吸着全行なっ7
tQこのときの、吸着結果を第4表に示す。
Table 2 0.2 500 355 730.4,
1228 680.6 1 100
670.8 8 62 Example 6 The adsorbent obtained in Example 1 was filled into a glass tube with an inner diameter of L2.3wφ so that the bed height was 10c1n, and the filling amount was 12
m (6F). An aqueous solution containing phosphate ions (lOOppm(p)I=5) made from sea bream using phosphate-sodium sound was passed through this at 5 VIO, and the phosphate ion concentration in the passing liquid was measured. Oral canal shown in Table 43 Table 3 0.5 Detected none 1.0 Not detected 1.58 2.08 2.5 13 3.0 19 Example 7 After adsorbing phosphate ions in Example 6, the adsorbent (Total phosphate ion adsorption tFi252Qc with 3t of liquid flowing)
Aqueous solution of N NaOH (50 met SV 1) was passed through to remove phosphate ions. We measured the phosphate ions in the desorbed solution and found that the amount of phosphate ions adsorbed was approximately 98%.
After desorption, the adsorbent 1c 0
.. After regenerating by passing a 50 dt-3Vl11 5N H2804 aqueous solution, adsorption was carried out by passing a liquid under the same conditions as in Example 6. Hereafter, repeat regeneration and adsorption 7
tQ The adsorption results at this time are shown in Table 4.

Claims (1)

【特許請求の範囲】 1、チタン、ジルコニウム、スズおよびランタニドから
選ばれる少くとも1種の金属の水和酸化物を活性炭に担
持せしめてなるリン酸イオン吸着剤。 2、水和金属酸化物の活性炭に対する重量比が0.05
〜0.8である、特許請求の範囲第1項記載の吸着剤。 3、アルカリ溶液により再生される、特許請求の範囲第
1項記載の吸着剤。 4、チタン、ジルコニウム、スズおよびランタニドから
選ばれる少くとも1種の金属の可溶性塩を水溶液として
活性炭に含浸し、これを乾燥した後、前記可溶性塩をア
ンモニアまたはNaOHと反応させて水和酸化物とする
ことからなる、リン酸イオン吸着剤の製造方法。 5、前記金属の可溶性塩がTiCl_4、Ti(SO_
4)_2、ZrOCl_2、ZrCl_4、ZrO(N
O_3)_2、ZrOSO_4、ZrO(CH_3CO
O)_2、SnCl_4、LCl_3およびLNO_3
(ここで、Lはランタニドを表す)から選ばれる、特許
請求の範囲第4項記載の方法。 6、前記水和酸化物が、次いで、70〜150℃で熟成
される、特許請求の範囲第4項記載の方法。
[Scope of Claims] 1. A phosphate ion adsorbent comprising activated carbon supporting a hydrated oxide of at least one metal selected from titanium, zirconium, tin, and lanthanide. 2. Weight ratio of hydrated metal oxide to activated carbon is 0.05
The adsorbent according to claim 1, which has a molecular weight of ˜0.8. 3. The adsorbent according to claim 1, which is regenerated by an alkaline solution. 4. Activated carbon is impregnated with an aqueous solution of a soluble salt of at least one metal selected from titanium, zirconium, tin, and lanthanide, and after drying, the soluble salt is reacted with ammonia or NaOH to form a hydrated oxide. A method for producing a phosphate ion adsorbent, comprising: 5. The soluble salts of the metals are TiCl_4, Ti(SO_
4)_2, ZrOCl_2, ZrCl_4, ZrO(N
O_3)_2, ZrOSO_4, ZrO(CH_3CO
O)_2, SnCl_4, LCl_3 and LNO_3
5. The method according to claim 4, wherein L represents a lanthanide. 6. The method of claim 4, wherein the hydrated oxide is then aged at 70-150°C.
JP12922586A 1986-06-05 1986-06-05 Phosphate ion adsorbent and its preparation Pending JPS62286539A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP12922586A JPS62286539A (en) 1986-06-05 1986-06-05 Phosphate ion adsorbent and its preparation

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP12922586A JPS62286539A (en) 1986-06-05 1986-06-05 Phosphate ion adsorbent and its preparation

Publications (1)

Publication Number Publication Date
JPS62286539A true JPS62286539A (en) 1987-12-12

Family

ID=15004244

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Country Status (1)

Country Link
JP (1) JPS62286539A (en)

Cited By (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
EP0686132A4 (en) * 1993-02-24 1996-03-13 Dudley John Mills Treatment of swimming pool water
KR20020043946A (en) * 2000-12-05 2002-06-12 이근석 Oxidation catalyzer, method for fabricating the same, method for recycling the same, and method for treating waste water using the same
EP1012123A4 (en) * 1997-03-26 2005-02-09 Commw Scient Andindustrial Res RENOVATION MATERIAL AND REMAINDER PROCESSES FOR SEDIMENTS
JP2008023401A (en) * 2006-07-18 2008-02-07 Nagasaki Prefecture Phosphorous adsorbent
WO2009063456A1 (en) * 2007-11-12 2009-05-22 Technion Research And Development Foundation Ltd Method for adsorption of phosphate contaminants from water solutions and its recovery
CN102910700A (en) * 2012-11-14 2013-02-06 南京大学 Method for removing phosphate in water through absorption of graphite oxide modified by zirconia
JP2013063436A (en) * 2012-11-30 2013-04-11 Nagasaki Prefecture Phosphorus removal material
JP2020506049A (en) * 2017-02-10 2020-02-27 カルゴン カーボン コーポレーション Adsorbent and manufacturing method

Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS53118281A (en) * 1977-03-25 1978-10-16 Hitachi Ltd Preparation of hydrous oxide supported on carrier
JPS56118734A (en) * 1980-02-25 1981-09-17 Takeda Chem Ind Ltd Adsorbing agent
JPS5710331A (en) * 1980-06-18 1982-01-19 Agency Of Ind Science & Technol Production of adsorbent consisting of metatitanic acid
JPS5834039A (en) * 1981-08-24 1983-02-28 Agency Of Ind Science & Technol Adsorbent containing zirconium oxide and preparation thereof

Patent Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS53118281A (en) * 1977-03-25 1978-10-16 Hitachi Ltd Preparation of hydrous oxide supported on carrier
JPS56118734A (en) * 1980-02-25 1981-09-17 Takeda Chem Ind Ltd Adsorbing agent
JPS5710331A (en) * 1980-06-18 1982-01-19 Agency Of Ind Science & Technol Production of adsorbent consisting of metatitanic acid
JPS5834039A (en) * 1981-08-24 1983-02-28 Agency Of Ind Science & Technol Adsorbent containing zirconium oxide and preparation thereof

Cited By (9)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
EP0686132A4 (en) * 1993-02-24 1996-03-13 Dudley John Mills Treatment of swimming pool water
EP1012123A4 (en) * 1997-03-26 2005-02-09 Commw Scient Andindustrial Res RENOVATION MATERIAL AND REMAINDER PROCESSES FOR SEDIMENTS
KR20020043946A (en) * 2000-12-05 2002-06-12 이근석 Oxidation catalyzer, method for fabricating the same, method for recycling the same, and method for treating waste water using the same
JP2008023401A (en) * 2006-07-18 2008-02-07 Nagasaki Prefecture Phosphorous adsorbent
WO2009063456A1 (en) * 2007-11-12 2009-05-22 Technion Research And Development Foundation Ltd Method for adsorption of phosphate contaminants from water solutions and its recovery
CN102910700A (en) * 2012-11-14 2013-02-06 南京大学 Method for removing phosphate in water through absorption of graphite oxide modified by zirconia
JP2013063436A (en) * 2012-11-30 2013-04-11 Nagasaki Prefecture Phosphorus removal material
JP2020506049A (en) * 2017-02-10 2020-02-27 カルゴン カーボン コーポレーション Adsorbent and manufacturing method
US11975305B2 (en) 2017-02-10 2024-05-07 Calgon Carbon Corporation Sorbent and method of making

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