JP2007001835A - Phosphorus adsorbent - Google Patents

Phosphorus adsorbent Download PDF

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JP2007001835A
JP2007001835A JP2005186084A JP2005186084A JP2007001835A JP 2007001835 A JP2007001835 A JP 2007001835A JP 2005186084 A JP2005186084 A JP 2005186084A JP 2005186084 A JP2005186084 A JP 2005186084A JP 2007001835 A JP2007001835 A JP 2007001835A
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phosphorus
aqueous solution
adsorbent
general formula
adsorption
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JP4576560B2 (en
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Mitsunari Sonoda
晃成 苑田
Ramesh Chitorakaa
ラメシュ チトラカー
Satoko Tetsuka
聡子 手束
Koji Sakane
幸治 坂根
Takahiro Hirotsu
孝弘 廣津
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National Institute of Advanced Industrial Science and Technology AIST
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Abstract

<P>PROBLEM TO BE SOLVED: To provide a technology to remove or recover phosphorus in water efficiently. <P>SOLUTION: A method for removing phosphorus in a phosphorus-containing waste water by using a phosphorus adsorbent which is represented by general formula (1): Fe(OH)<SB>m</SB>(SO<SB>4</SB>)<SB>n</SB>lH<SB>2</SB>O (wherein, 2≤m<3; 0<n≤0.5; 0≤l≤0.5) or its hydrate formed in an aqueous solution is provided. <P>COPYRIGHT: (C)2007,JPO&INPIT

Description

本発明は、リンを吸着する化合物、リン吸着剤及びそれらの製造方法、リンの除去ないし回収方法に関する。   The present invention relates to a compound that adsorbs phosphorus, a phosphorus adsorbent, a method for producing them, and a method for removing or recovering phosphorus.

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、これを除去・回収する技術開発が求められている。   Phosphorus in wastewater discharged from factories and households causes eutrophication of rivers, lakes, and seawater, and causes environmental destruction. Therefore, technology development to remove and recover this has been required.

これまでに種々のリン吸着剤が提案されているが(特許文献1〜3)、それらのリン吸着能は不十分であるか、或いは、リン吸着剤の製造コストが高く実用的でないなどの問題があった。さらに、海水などの塩濃度の高い排水ではリン吸着能が低下する傾向があり、海水などの塩濃度の高い排水に於いても優れたリン吸着能を有するリン吸着剤が求められている。
特開2004−89760 特開2005−28247 特開平7−60261号公報
Various phosphorus adsorbents have been proposed so far (Patent Documents 1 to 3), but their phosphorus adsorption capacity is insufficient, or the production cost of the phosphorus adsorbent is high and not practical. was there. Furthermore, phosphorus adsorption capacity tends to decrease in wastewater with a high salt concentration such as seawater, and a phosphorus adsorbent having an excellent phosphorus adsorption capacity is required even in wastewater with a high salt concentration such as seawater.
JP2004-89760 JP 2005-28247 A Japanese Patent Laid-Open No. 7-60261

本発明は、水中のリンを効率よく除去ないし回収する技術を提供することを目的とする。   An object of the present invention is to provide a technique for efficiently removing or recovering phosphorus in water.

本発明者らは、上記課題に鑑み検討を重ねた結果、硫酸鉄(II)と硫酸鉄(III)を溶かした水溶液に塩基を加えて中性からアルカリ性とし、得られる鉄化合物が優れたリン吸着能を有することを見出した。   As a result of repeated studies in view of the above problems, the present inventors have made a basic to alkaline solution by adding a base to an aqueous solution in which iron (II) sulfate and iron (III) are dissolved. It has been found that it has an adsorption capacity.

本発明は、以下の化合物、リン吸着剤及びそれらの製造法、排水からのリンの除去方法に関する。   The present invention relates to the following compounds, phosphorus adsorbents and methods for producing them, and methods for removing phosphorus from waste water.

1. 式:
Fe(OH)2.6(SO)0.2
で表される化合物および水溶液中で形成されるその水和物
2. 一般式(1):
Fe(OH)(SO)・lHO (1)
(式中、2≦m<3、0<n≦0.5、0≦l≦0.5である。)
で表されるリン吸着剤および水溶液中で形成されるその水和物。
1. formula:
Fe (OH) 2.6 (SO 4 ) 0.2
And the hydrate formed in an aqueous solution. General formula (1):
Fe (OH) m (SO 4 ) n · lH 2 O (1)
(In the formula, 2 ≦ m <3, 0 <n ≦ 0.5, 0 ≦ l ≦ 0.5.)
And a hydrate formed in an aqueous solution.

3. 一般式(1):
Fe(OH)(SO)・lHO (1)
(式中、2≦m<3、0<n≦0.5、0≦l≦0.5である。)
で表される化合物および水溶液中で形成されるその水和物のリン吸着のための使用。
3. General formula (1):
Fe (OH) m (SO 4 ) n · lH 2 O (1)
(In the formula, 2 ≦ m <3, 0 <n ≦ 0.5, 0 ≦ l ≦ 0.5.)
And the use for adsorption of phosphorus of the hydrate formed in an aqueous solution.

4. FeSOとFe(SO)を含む混合水溶液に塩基を加えて中性からアルカリ性にして沈殿を生じさせることを特徴とする一般式(1):
Fe(OH)(SO)・lHO (1)
(式中、2≦m<3、0<n≦0.5、0≦l≦0.5である。)
で表される化合物および水溶液中で形成されるその水和物の製造方法。
4). A general formula (1) characterized in that a base is added to a mixed aqueous solution containing FeSO 4 and Fe 2 (SO 4 ) 3 to produce a precipitate from neutral to alkaline.
Fe (OH) m (SO 4 ) n · lH 2 O (1)
(In the formula, 2 ≦ m <3, 0 <n ≦ 0.5, 0 ≦ l ≦ 0.5.)
And a method for producing the hydrate formed in an aqueous solution.

5. 項2に記載のリン吸着剤を使用してリン含有廃水を処理することを特徴とする、リンの除去方法。   5. Item 3. A method for removing phosphorus, comprising treating phosphorus-containing wastewater using the phosphorus adsorbent according to Item 2.

本発明によれば安価な硫酸鉄原料を使用し、高いリン吸着能を有するリン吸着剤を得ることができる。   According to the present invention, an inexpensive iron sulfate raw material can be used to obtain a phosphorus adsorbent having high phosphorus adsorption ability.

本発明のリン吸着剤は、海水などの高塩濃度のリン含有排水においても効率よくリンを吸着除去することが可能である。   The phosphorus adsorbent of the present invention can efficiently adsorb and remove phosphorus even in high-salt phosphorus-containing wastewater such as seawater.

本明細書において、リン吸着剤としては、以下の一般式(1):
Fe(OH)(SO)・lHO (1)
(式中、2≦m<3、0<n≦0.5、0≦l≦0.5である。)
で表される化合物および水溶液中で形成されるその水和物を使用することができる。
In the present specification, as the phosphorus adsorbent, the following general formula (1):
Fe (OH) m (SO 4 ) n · lH 2 O (1)
(In the formula, 2 ≦ m <3, 0 <n ≦ 0.5, 0 ≦ l ≦ 0.5.)
And the hydrates formed in aqueous solutions can be used.

mは、2以上3未満、好ましくは2.2〜2.8,より好ましくは2.5〜2.7、特に好ましくは約2.6である。   m is 2 or more and less than 3, preferably 2.2 to 2.8, more preferably 2.5 to 2.7, and particularly preferably about 2.6.

nは、0より大きく0.5以下、好ましくは0.1〜0.4,より好ましくは0.15〜0.25、特に好ましくは約0.2である。
lは、0以上0.5以下、好ましくは0〜0.4,より好ましくは0.05〜0.20、特に好ましくは約0.1である。
n is larger than 0 and 0.5 or less, preferably 0.1 to 0.4, more preferably 0.15 to 0.25, and particularly preferably about 0.2.
l is 0 or more and 0.5 or less, preferably 0 to 0.4, more preferably 0.05 to 0.20, and particularly preferably about 0.1.

mが約2.6、nが約0.20である一般式(1)の化合物は、特にリン吸着能が優れているため好ましい。   A compound of the general formula (1) in which m is about 2.6 and n is about 0.20 is particularly preferable because of its excellent phosphorus adsorption ability.

本明細書において、吸着されるリンとしては、リン酸ないしリン酸解離物が好ましく例示されるが、亜リン酸又はそのイオンなども吸着することができる。   In the present specification, preferred examples of phosphorus adsorbed include phosphoric acid and phosphoric acid dissociated products, but phosphorous acid or ions thereof can also be adsorbed.

リンの吸着対象としては、リン含有排水などのリン含有水溶液が挙げられる。該水溶液は、海水などのように塩類を多量に含む水溶液であってもよい。本発明のリン吸着剤は、塩濃度が高くても、有効にリンを吸着除去することができる。また、該水溶液のpHは特に限定されないが、通常2〜9程度、好ましくは3〜8.5程度、より好ましくは4〜8程度、特に好ましくは4.5〜7.5程度である。リン吸着を実施する際には、必要に応じてリン除去対象水溶液のpHを調整することができる。   Examples of phosphorus adsorption targets include phosphorus-containing aqueous solutions such as phosphorus-containing wastewater. The aqueous solution may be an aqueous solution containing a large amount of salts such as seawater. The phosphorus adsorbent of the present invention can effectively adsorb and remove phosphorus even when the salt concentration is high. The pH of the aqueous solution is not particularly limited, but is usually about 2 to 9, preferably about 3 to 8.5, more preferably about 4 to 8, and particularly preferably about 4.5 to 7.5. When carrying out phosphorus adsorption, the pH of the phosphorus removal target aqueous solution can be adjusted as necessary.

上記一般式(1)の化合物は、例えば FeSOとFe(SO)を含む混合水溶液を調製し、該水溶液のpHを攪拌ないし振盪下に塩基を加えて中性からアルカリ性にし、リン吸着性能を有する一般式(1)の化合物を沈殿させ、濾過及び乾燥して得ることができる。 The compound of the general formula (1) is prepared by preparing a mixed aqueous solution containing, for example, FeSO 4 and Fe 2 (SO 4 ) 3, and adjusting the pH of the aqueous solution to neutral to alkaline by adding a base with stirring or shaking. It can be obtained by precipitating the compound of the general formula (1) having adsorption performance, filtering and drying.

FeSOとFe(SO)を含む混合水溶液は、例えば固体状のFeSOとFe(SO)(各々水和物ないし無水物であってもよい)を水に溶かしてもよく、各々の水溶液を混合して調製してもよい。さらに、FeSOとFe(SO)の一方または両方の存在下又は非存在下にFeSOとFe(SO)の複塩を使用して調製してもよい。該混合水溶液中のFe2+とFe3+の比率(モル比)は、Fe2+:Fe3+=0.98〜0.02モル程度:0.02〜0.98モル程度、好ましくは0.98〜0.5モル程度:0.02〜0.5モル程度、より好ましくはFe2+:Fe3+=0.95〜0.7モル程度:0.05〜0.3モル程度である。 Mixing an aqueous solution containing FeSO 4 and Fe 2 (SO 4) 3, for example also solid FeSO 4 and Fe 2 (SO 4) 3 (which may be respectively hydrate or anhydride) dissolved in water It is also possible to prepare by mixing each aqueous solution. It may also prepared using double salt of FeSO 4 and Fe 2 (SO 4) one or FeSO 4 in the presence or absence of both 3 and Fe 2 (SO 4) 3. The ratio (molar ratio) between Fe 2+ and Fe 3+ in the mixed aqueous solution is as follows: Fe 2+ : Fe 3+ = 0.98 to 0.02 mol: 0.02 to 0.98 mol, preferably 0.98 to About 0.5 mol: about 0.02 to 0.5 mol, more preferably about Fe 2+ : Fe 3+ = about 0.95 to 0.7 mol: about 0.05 to 0.3 mol.

本発明は、FeSOとFe(SO)を組み合わせて使用することで、一般式(1)の化合物を得ることを特徴とし、得られた一般式(1)の化合物は、優れたリン吸着能を有する。特に、式:Fe(OH)2.5(SO)0.25で表される化合物は、リン吸着能に優れているため好ましい。 The present invention is characterized in that a compound of the general formula (1) is obtained by using a combination of FeSO 4 and Fe 2 (SO 4 ) 3 , and the obtained compound of the general formula (1) is excellent. Has phosphorus adsorption capacity. In particular, a compound represented by the formula: Fe (OH) 2.5 (SO 4 ) 0.25 is preferable because of its excellent phosphorus adsorption ability.

FeSOとFe(SO)を含む水溶液を中性からアルカリ性にするための塩基としては、水酸化ナトリウム、水酸化カリウム、水酸化リチウムなどのアルカリ金属水酸化物が好ましく例示できる。 Preferred examples of the base for making the aqueous solution containing FeSO 4 and Fe 2 (SO 4 ) 3 neutral to alkaline include alkali metal hydroxides such as sodium hydroxide, potassium hydroxide and lithium hydroxide.

塩基を加えたときの水溶液のpHは通常6.5〜13程度、好ましくは6.8〜11程度、より好ましくは7.0〜10程度、さらに好ましくは7.0〜8.0程度である。アルカリは、本発明のリン酸吸着能を有する化合物を沈殿させる目的で加える。得られた沈殿物は、濾過、洗浄及び乾燥することにより目的物を得ることができる。   The pH of the aqueous solution when the base is added is usually about 6.5 to 13, preferably about 6.8 to 11, more preferably about 7.0 to 10, and further preferably about 7.0 to 8.0. . The alkali is added for the purpose of precipitating the compound having the phosphate adsorption ability of the present invention. The obtained precipitate can be obtained by filtration, washing and drying.

本発明のリン吸着剤は、造粒などの操作を行い成形体とし、カラムなどに充填し、該カラムに燐を含む排水を流すことによりリンの吸着ないし回収を行うことができる。   The phosphorus adsorbent of the present invention can be subjected to operations such as granulation to form a molded body, filled in a column or the like, and phosphorus can be adsorbed or recovered by flowing waste water containing phosphorus through the column.

以下、実施例により本発明をさらに詳細に説明するが、本発明はこれらの実施例によって何ら限定されるものではない。
実施例1
0.5M FeSO4(200mL)と0.1M Fe2(SO4)3(200mL)を混合し、攪拌下に1M NaOHを加えてpHを7〜8に調製した。生じた沈殿物を濾過し、脱イオン水で洗浄後乾燥して、Fe(OH)2.6(SO)0.2・0.1HOで表される化合物を得た。得られた化合物の化学式は、DTA−TG測定から水分量、5N塩酸に溶解し、原子吸光法によりFe含量、加圧熱水抽出/イオンクロマト法で硫酸イオンを定量することにより確認した。
EXAMPLES Hereinafter, although an Example demonstrates this invention further in detail, this invention is not limited at all by these Examples.
Example 1
0.5 M FeSO 4 (200 mL) and 0.1 M Fe 2 (SO 4 ) 3 (200 mL) were mixed, and 1 M NaOH was added with stirring to adjust the pH to 7-8. The resulting precipitate was filtered, washed with deionized water and dried to obtain a compound represented by Fe (OH) 2.6 (SO 4 ) 0.2 · 0.1H 2 O. The chemical formula of the obtained compound was confirmed by dissolving in water content and 5N hydrochloric acid from DTA-TG measurement, and quantifying the Fe content by atomic absorption method and sulfate ion by pressurized hot water extraction / ion chromatography.

また、Fe(OH)2.6(SO)0.2・0.1HOで表される化合物のXRD吸着パターンを図1に示し、DTA-TG曲線を図2に示す。さらに、FT-IRスペクトルを図3に示す。
比較例1
0.1M FeCl3 (500mL)に対し、攪拌下に0.1M NaOH (500mL)を加えてpHを8〜10に調製した。生じた沈殿物を濾過し、脱イオン水で洗浄後乾燥して、Fe(OH)で表される化合物を得た。
Further, an XRD adsorption pattern of a compound represented by Fe (OH) 2.6 (SO 4 ) 0.2 · 0.1H 2 O is shown in FIG. 1, and a DTA-TG curve is shown in FIG. Furthermore, the FT-IR spectrum is shown in FIG.
Comparative Example 1
To 0.1M FeCl 3 (500 mL), 0.1M NaOH (500 mL) was added with stirring to adjust the pH to 8-10. The resulting precipitate was filtered, washed with deionized water and dried to obtain a compound represented by Fe (OH) 3 .

得られたFe(OH)で表される化合物のXRD吸着パターンを図1に示し、DTA-TG曲線を図2に示す。さらに、FT-IRスペクトルを図3に示す。
試験例1
実施例1及び比較例1で得られた鉄化合物からなるリン吸着剤0.05gを使用し、海水2L中に0.33mg-P/gのリン酸を含む水溶液からのリンの吸着量を測定した。結果を図4に示す。
The XRD adsorption pattern of the obtained compound represented by Fe (OH) 3 is shown in FIG. 1, and the DTA-TG curve is shown in FIG. Furthermore, the FT-IR spectrum is shown in FIG.
Test example 1
Using 0.05 g of the phosphorus adsorbent composed of the iron compound obtained in Example 1 and Comparative Example 1, the amount of phosphorus adsorbed from an aqueous solution containing 0.33 mg-P / g phosphoric acid in 2 L of seawater was measured. The results are shown in FIG.

また、実施例1で得られた鉄化合物からなるリン吸着剤のpHリン吸着能のpH依存性を図5に示し、実施例1及び比較例1で得られた鉄化合物からなるリン吸着剤の吸着等温線を図6に示す。   Moreover, the pH dependence of the pH phosphorus adsorption capacity of the phosphorus adsorbent comprising the iron compound obtained in Example 1 is shown in FIG. 5, and the phosphorus adsorbent comprising the iron compound obtained in Example 1 and Comparative Example 1 The adsorption isotherm is shown in FIG.

吸着剤のXRDパターンを示す。The XRD pattern of an adsorbent is shown. 吸着剤のDTA-TG曲線を示す。The DTA-TG curve of an adsorbent is shown. 吸着剤のFT-IRスペクトルを示す。The FT-IR spectrum of the adsorbent is shown. 吸着剤のリン酸吸着の時間依存性を示す。The time dependence of the adsorption of phosphoric acid by the adsorbent is shown. 吸着剤のリン酸吸着のpH依存性を示す。The pH dependence of the adsorption of phosphate by the adsorbent is shown. 吸着剤についての海水からのリン酸の吸着等温線を示す。The adsorption isotherm of the phosphoric acid from the seawater about an adsorbent is shown.

Claims (5)

有効成分が式:
Fe(OH)2.6(SO)0.2
で表される化合物および水溶液中で形成されるその水和物
The active ingredient is the formula:
Fe (OH) 2.6 (SO 4 ) 0.2
And the hydrates formed in aqueous solution
有効成分が一般式(1):
Fe(OH)(SO) (1)
(式中、2≦m<3、0<n≦0.5である。)
で表されるリン吸着剤および水溶液中で形成されるその水和物。
The active ingredient is general formula (1):
Fe (OH) m (SO 4 ) n (1)
(Wherein 2 ≦ m <3 and 0 <n ≦ 0.5)
And a hydrate formed in an aqueous solution.
一般式(1):
Fe(OH)(SO) (1)
(式中、2≦m<3、0<n≦0.5である。)
で表される化合物および水溶液中で形成されるその水和物のリン吸着のための使用。
General formula (1):
Fe (OH) m (SO 4 ) n (1)
(Wherein 2 ≦ m <3 and 0 <n ≦ 0.5)
And the use for adsorption of phosphorus of the hydrate formed in an aqueous solution.
FeSOとFe(SO)を含む混合水溶液に塩基を加えて中性からアルカリ性にして沈殿を生じさせることを特徴とする一般式(1):
Fe(OH)(SO) (1)
(式中、2≦m<3、0<n≦0.5である。)
で表される化合物および水溶液中で形成されるその水和物の製造方法。
General formula (1) characterized in that a base is added to a mixed aqueous solution containing FeSO 4 and Fe 2 (SO 4 ) 3 to produce a precipitate from neutral to alkaline:
Fe (OH) m (SO 4 ) n (1)
(Wherein 2 ≦ m <3 and 0 <n ≦ 0.5)
And a method for producing the hydrate formed in an aqueous solution.
請求項2に記載のリン吸着剤を使用してリン含有廃水を処理することを特徴とする、リンの除去方法。 A method for removing phosphorus, comprising treating phosphorus-containing wastewater using the phosphorus adsorbent according to claim 2.
JP2005186084A 2005-06-27 2005-06-27 Phosphorous adsorbent Expired - Fee Related JP4576560B2 (en)

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KR101356384B1 (en) 2012-11-28 2014-01-28 한국과학기술연구원 Basanite with hydroxyl group and fabricating method for the same
CN110342481A (en) * 2019-07-10 2019-10-18 贵州新东浩化工材料科技有限公司 A method of phosphoric acid is prepared with ferrophosphorus
CN110711552A (en) * 2019-11-14 2020-01-21 中国科学院北京综合研究中心 Synchronous denitrification dephosphorization oxygenation composite material and preparation method and application thereof
WO2020255956A1 (en) 2019-06-20 2020-12-24 株式会社杉田製線 Water purifying material having iron as main component, and method for manufacturing same
WO2020255957A1 (en) 2019-06-20 2020-12-24 株式会社杉田製線 Water purification material and water purification method using same

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