JP2007161967A - Scavenging/detecting agent for high-valence metal ion - Google Patents

Scavenging/detecting agent for high-valence metal ion Download PDF

Info

Publication number
JP2007161967A
JP2007161967A JP2005363924A JP2005363924A JP2007161967A JP 2007161967 A JP2007161967 A JP 2007161967A JP 2005363924 A JP2005363924 A JP 2005363924A JP 2005363924 A JP2005363924 A JP 2005363924A JP 2007161967 A JP2007161967 A JP 2007161967A
Authority
JP
Japan
Prior art keywords
metal ions
cellulose
valence
dfb
collection
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
JP2005363924A
Other languages
Japanese (ja)
Other versions
JP5249500B2 (en
Inventor
Toshio Igarashi
淑郎 五十嵐
Yoshitaka Takagai
慶隆 高貝
Michio Butsugan
道男 佛願
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.)
Ibaraki University NUC
Fukushima University NUC
Resonac Corp
Original Assignee
Hitachi Chemical Co Ltd
Ibaraki University NUC
Fukushima University NUC
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 Hitachi Chemical Co Ltd, Ibaraki University NUC, Fukushima University NUC filed Critical Hitachi Chemical Co Ltd
Priority to JP2005363924A priority Critical patent/JP5249500B2/en
Publication of JP2007161967A publication Critical patent/JP2007161967A/en
Application granted granted Critical
Publication of JP5249500B2 publication Critical patent/JP5249500B2/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Landscapes

  • Solid-Sorbent Or Filter-Aiding Compositions (AREA)

Abstract

<P>PROBLEM TO BE SOLVED: To provide a scavenging/detecting agent capable of efficiently and selectively scavenging high-valence metal ions of ≥3 in valence contained in a medium and enabling the ions to be easily detected and their concentration to be measured. <P>SOLUTION: The scavenging/detecting agent for metal ions of ≥3 in valence is provided, being such that a hydroxamic acid group-bearing compound is introduced into a carrier. <P>COPYRIGHT: (C)2007,JPO&INPIT

Description

本発明は、高原子価金属イオンを捕集・検出する捕集、検出剤に関するものである。さらに詳しくは、ヒドロキサム酸基を担体に導入し、例えば、バナジウム、鉄、チタン等の高原子価金属イオンを高価な分析機器を使用することなく、容易に捕集・検出できる捕集・検出剤に関するものである。   The present invention relates to a collection and detection agent for collecting and detecting high-valent metal ions. More specifically, a collecting / detecting agent that introduces a hydroxamic acid group into a carrier and can easily collect / detect high-valent metal ions such as vanadium, iron, and titanium without using an expensive analytical instrument. It is about.

河川や廃水等に含まれるカルシウム、マグネシウム、マンガン、鉄、銅、亜鉛等の金属イオンの除去あるいは有益金属イオンの捕捉にはイオン交換樹脂が広く利用されているが、低濃度の金属イオンを選択的に吸着する効果は必ずしも満足し得るものとは言えない。   Ion exchange resins are widely used to remove metal ions such as calcium, magnesium, manganese, iron, copper, and zinc contained in rivers and wastewater, or to capture beneficial metal ions. Select low-concentration metal ions. The effect of adsorption is not necessarily satisfactory.

一方、重金属イオンとの間で、キレートを形成してこれらを選択的に捕捉する性質を持ったキレート樹脂は、水処理分野での銅、亜鉛、ニッケル、コバルト、バナジウム等重金属イオンの除去や捕捉などに利用されている。その構造は、ジビニルベンゼン等の架橋剤によって形成された剛直な三次元構造の担体に、イミノジ酢酸、エチレンジアミン二酢酸、エチレンジアミン三酢酸、チオグリコール酸、チオリンゴ酸、リン酸等が導入されたものが一般的である。また、キレート樹脂に吸着された金属イオンの検出、濃度測定は、吸着金属を強酸、キレート剤、有機溶媒等で溶出し、その後、吸光光度計、蛍光分光器、原子吸光光度計などの高価な分析機器により行われることが多い。   On the other hand, chelate resins that have the property of selectively capturing these by forming chelates with heavy metal ions remove and capture heavy metal ions such as copper, zinc, nickel, cobalt, and vanadium in the water treatment field. It is used for such as. The structure is such that iminodiacetic acid, ethylenediaminediacetic acid, ethylenediaminetriacetic acid, thioglycolic acid, thiomalic acid, phosphoric acid, etc. are introduced into a rigid three-dimensional carrier formed by a crosslinking agent such as divinylbenzene. It is common. In addition, the detection and concentration measurement of metal ions adsorbed on the chelate resin are performed by eluting the adsorbed metal with a strong acid, a chelating agent, an organic solvent, etc. Often done with analytical instruments.

しかし、上記のイオン交換樹脂やキレート樹脂は、吸着対象となる金属イオンを含む試料溶液が弱酸性〜中性である場合において効率的に対象金属イオンを吸着するものであり、pH2以上の強酸下において、特に原子価が3以上の高原子価金属イオンを効率良く選択的に吸着することは困難であった。   However, the above ion exchange resin or chelate resin is one that efficiently adsorbs target metal ions when the sample solution containing the metal ions to be adsorbed is weakly acidic to neutral, and has a pH of 2 or higher. In particular, it is difficult to efficiently and selectively adsorb high-valent metal ions having a valence of 3 or more.

また、従来のキレート樹脂の大半は、上記したようにジビニルベンゼン等の架橋剤によって形成された剛直な三次元構造の担体を有するビーズ状の樹脂であるため、疎水性が高く、樹脂内部への金属イオンや再生剤の拡散速度が遅く、処理効率に問題がある。   In addition, most of the conventional chelate resins are bead-like resins having a rigid three-dimensional structure formed by a cross-linking agent such as divinylbenzene as described above. The diffusion rate of metal ions and regenerants is slow and there is a problem in processing efficiency.

更に、キレート樹脂に吸着された金属イオンの検出、濃度測定は、上記の通りであるため、コストや分析時間がかかる等の問題があった。
特開2000−73043号公報 特開平9−127092号公報 特開平8−295966号公報
Furthermore, since detection and concentration measurement of metal ions adsorbed on the chelate resin are as described above, there are problems such as cost and analysis time.
JP 2000-73043 A JP-A-9-127092 JP-A-8-295966

本発明は、媒体中に含まれる原子価が3以上の高原子価金属イオンを効率良く選択的に捕集し、かつ容易にその検出、濃度測定を行うことができる捕集・検出剤を提供することを目的とするものである。   The present invention provides a collection / detection agent capable of efficiently and selectively collecting high-valence metal ions having a valence of 3 or more contained in a medium, and easily detecting and measuring the concentration thereof. It is intended to do.

本発明者らは、ヒドロキサム酸基を有する化合物を導入した担体を捕集・検出剤として用いることで、媒体中に含まれる高原子価金属イオンを容易に捕集・検出できることを見出し、本発明を為すに至った。   The present inventors have found that a high-valent metal ion contained in a medium can be easily collected and detected by using a carrier into which a compound having a hydroxamic acid group is introduced as a collecting and detecting agent. I came to do it.

すなわち、本発明は、下記(1)〜(5)に記載の事項をその特徴とするものである。   That is, the present invention is characterized by the following items (1) to (5).

(1)ヒドロキサム酸基を有する化合物を担体に導入してなる原子価3以上の金属イオンの捕集・検出剤。   (1) An agent for collecting and detecting metal ions having a valence of 3 or more, wherein a compound having a hydroxamic acid group is introduced into a carrier.

(2)前記担体がセルロースである上記(1)記載の捕集・検出剤。   (2) The collection / detection agent according to (1), wherein the carrier is cellulose.

(3)捕集・検出対象の金属イオンを含む溶液のpHが2以下である上記(1)または(2)記載の捕集・検出剤。   (3) The collection / detection agent according to (1) or (2) above, wherein the pH of the solution containing the metal ions to be collected / detected is 2 or less.

(4)捕集・検出対象の金属イオンがバナジウムイオンである上記(1)〜(3)いずれかに記載の捕集・検出剤。   (4) The collection / detection agent according to any one of (1) to (3), wherein the metal ion to be collected / detected is vanadium ion.

(5)前記ヒドロキサム酸基を有する化合物がデスフェリオキサミンB(DFB)である上記(1)〜(4)いずれかに記載の捕集・検出剤。   (5) The collection / detection agent according to any one of (1) to (4), wherein the compound having a hydroxamic acid group is desferrioxamine B (DFB).

本発明によれば、媒体中に含まれる原子価が3以上の高原子価金属イオンを効率良く選択的に捕集し、かつ容易にその検出、濃度測定を行うことができる捕集・検出剤を提供することが可能となる。   According to the present invention, a collection / detection agent capable of efficiently and selectively collecting a high-valence metal ion having a valence of 3 or more contained in a medium and easily detecting and measuring the concentration thereof. Can be provided.

以下、本発明の実施形態を詳細に説明する。   Hereinafter, embodiments of the present invention will be described in detail.

本発明の捕集・検出剤は、担体にヒドロキサム酸基を有する化合物を導入してなるものであることをその特徴とし、特に、チタン(IV)、バナジウム(V)、鉄(III)、モリブデン(VI)、ニオブ(V)、タンタル(V)、ジルコニウム(IV)等の原子価3以上の高原子価金属イオンを効率良く選択的に捕集し、かつ容易にその検出、濃度測定を行うことができるものである。   The collection / detection agent of the present invention is characterized in that a compound having a hydroxamic acid group is introduced into a carrier, and in particular, titanium (IV), vanadium (V), iron (III), molybdenum. Efficiently and selectively collects high-valence metal ions having a valence of 3 or more such as (VI), niobium (V), tantalum (V), zirconium (IV), etc., and easily detects and measures the concentration. It is something that can be done.

ヒドロキサム酸基は、高原子価金属イオンをシデロホア構造でとらえるため、pH2以下の強酸性下でも安定な巻きつき型の錯体を形成し、高原子価金属イオンを捕集できる。また、ヒドロキサム酸基は、高原子価金属イオンを捕集すると発色する特性を持っているので発色の強度により濃度が分かるという特長がある。ヒドロキサム酸基を有する化合物としては、アセトヒドロキサム酸、サリチルヒドロキサム酸、ベンゾヒドロキサム酸、アミノベンゾジヒドロキサム酸、デスフェリオキサミンB(DFB)等が挙げられる。シデロホア構造を取りやすくするために、1分子中に3個以上のヒドロキサム酸基を有するDFBが好ましく、担体への導入を容易にするために、末端にHを持つDFBがさらに好ましい。 Since the hydroxamic acid group captures a high-valent metal ion with a siderophore structure, it can form a stable wound-type complex even under strong acidity of pH 2 or lower, and can collect the high-valent metal ion. In addition, hydroxamic acid groups have the property of developing color when high-valent metal ions are collected, and thus have a feature that the concentration can be determined by the intensity of color development. Examples of the compound having a hydroxamic acid group include acetohydroxamic acid, salicylhydroxamic acid, benzohydroxamic acid, aminobenzodihydroxamic acid, desferrioxamine B (DFB), and the like. In order to facilitate the formation of a siderophore structure, a DFB having three or more hydroxamic acid groups in one molecule is preferable, and in order to facilitate introduction into a carrier, a DFB having a terminal H 3 N + is more preferable.

下記に好ましいDFBの構造を示す。

Figure 2007161967
A preferred DFB structure is shown below.
Figure 2007161967

担体としては、例えば、スチレン−ジビニルベンゼン、アクリレート、メタクリレート、ポリビニルアルコール、セルロース等、試料溶媒に溶解しないものならいずれでもよく、またこれに限定するものではない。しかし、金属イオンは水溶液試料に溶解していることが多いので、好ましくは親水性のアクリレート、メタクリレート、ポリビニルアルコール、セルロース等が好ましい。綿状や粉末状の分離剤、ろ紙、メンブラン化、試験紙などの形状に加工しやすい点からセルロースが特に好ましい。   As the carrier, for example, styrene-divinylbenzene, acrylate, methacrylate, polyvinyl alcohol, cellulose and the like which are not soluble in the sample solvent may be used, and the carrier is not limited thereto. However, since metal ions are often dissolved in an aqueous solution sample, hydrophilic acrylate, methacrylate, polyvinyl alcohol, cellulose and the like are preferable. Cellulose is particularly preferred because it can be easily processed into a cotton-like or powder-like separating agent, filter paper, membrane, test paper and the like.

次に、本発明の捕集・検出剤の作製方法を示す。ここでは、担体としてセルロースのろ紙を用い、ヒドロキサム酸基を有する化合物として上記DFBを用いた場合を示すが、本発明はこれに限定されるものではない。また、セルロースに対する一般的な化学修飾は、反応性の容易さから、酢酸セルロースやニトロセルロースなどの反応性の高いセルロース誘導体が利用されるが、これらのセルロース誘導体は、純粋なセルロースと化学的・物理的な物性が全く異なるため、紙、試験紙、インディケーター紙としての役割を果たさない。そこで、ここでは特にセルロースの特性を保持したまま、上記DFBを結合させる合成法を示す。すなわち、セルロースの水酸基の一部をクロライド化し、そのハロゲン化された部分にのみにDFBを導入する方法である。   Next, a method for producing the collection / detection agent of the present invention will be described. Here, a case where cellulose filter paper is used as a carrier and the above DFB is used as a compound having a hydroxamic acid group is shown, but the present invention is not limited thereto. In addition, for general chemical modification to cellulose, highly reactive cellulose derivatives such as cellulose acetate and nitrocellulose are used because of their easy reactivity. These cellulose derivatives are chemically and purely cellulose. Since physical properties are completely different, it does not serve as paper, test paper, or indicator paper. Therefore, here, a synthesis method in which the DFB is bonded while maintaining the characteristics of cellulose in particular will be shown. That is, this is a method in which a part of the hydroxyl group of cellulose is chlorinated and DFB is introduced only into the halogenated part.

まず、セルロースの水酸基の一部をクロライド化するために、ろ紙(セルロース)をバイアルに入れ、溶媒を加えて十分に浸した後、塩化チオニルを加えて反応させる。ろ紙(セルロース)と塩化チオニル量比は、セルロース1gに対し、塩化チオニル6.17×10−4mol(セルロース中のグルコースユニット量)であることが望ましく、それより多い場合も、少ない場合も高原子価金属イオンの捕集量、特にバナジウムの捕集量が減少する傾向にある。ろ紙を浸す溶媒は、特に限定しないが、セルロースになじんで、塩化チオニルをよく溶解することからジメチルホルムアミド(DMF)が望ましく、溶媒量は、20〜200mlの範囲であることが望ましい。また、クロライド化の反応条件は、80〜100℃で、1〜3時間反応させることが望ましい。反応温度が80℃未満であると、クロライド化が不十分となる恐れがあり、100℃を超えると副反応が起き易くなる。また、反応時間が1時間未満の場合は、クロライド化が不十分となる恐れがあり、一方、3時間を超えてもクロライドの導入量はあまり変化しない。 First, in order to chlorinate a part of the hydroxyl groups of cellulose, filter paper (cellulose) is put in a vial, and after adding a solvent and sufficiently immersed, thionyl chloride is added and reacted. The ratio of the amount of filter paper (cellulose) and thionyl chloride is desirably 6.17 × 10 −4 mol of thionyl chloride (the amount of glucose units in cellulose) with respect to 1 g of cellulose. There is a tendency for the amount of valence metal ions collected, particularly the amount of vanadium collected, to decrease. The solvent in which the filter paper is soaked is not particularly limited, but dimethylformamide (DMF) is desirable because it is familiar with cellulose and dissolves thionyl chloride well, and the amount of solvent is desirably in the range of 20 to 200 ml. The reaction conditions for the chlorination are desirably 80 to 100 ° C. and the reaction is preferably performed for 1 to 3 hours. If the reaction temperature is less than 80 ° C., there is a risk that the chlorination will be insufficient, and if it exceeds 100 ° C., side reactions tend to occur. On the other hand, if the reaction time is less than 1 hour, the formation of chloride may be insufficient. On the other hand, even if the reaction time exceeds 3 hours, the amount of chloride introduced does not change much.

上記のようにしてろ紙をクロライド化した後に、すぐDFBを反応させても良いが、その導入率を高くするには、予めヨウ化ナトリウムでクロルを置換しておくことが望ましい。この場合、上記で得たろ紙を取り出し、アセトンで十分に洗浄した後、これを、ヨウ化ナトリウム3.0×10−5〜3.0×10−3mol(/セルロース1g)がアセトンに溶解した溶液中に3時間以上浸し、置換反応を行う。アセトンの量は10〜100mlであることが望ましい。また、反応温度は、室温付近が良く、より高温条件ではアセトンが揮発してしまう恐れがある。 Although the DFB may be reacted immediately after the filter paper is chlorinated as described above, in order to increase the introduction rate, it is desirable to substitute chloro with sodium iodide in advance. In this case, extraction of filter paper obtained above, was thoroughly washed with acetone, dissolved this, sodium iodide 3.0 × 10 -5 ~3.0 × 10 -3 mol (/ cellulose 1g) is acetone Immerse it in the solution for 3 hours or more to perform the substitution reaction. The amount of acetone is desirably 10 to 100 ml. The reaction temperature is preferably near room temperature, and acetone may volatilize under higher temperature conditions.

一方、別バイアルに、DFBを溶媒に加えて加熱し、完全にDFBを溶解させる。ここで用いる溶媒はピリジン等の塩基性溶媒であることが望ましく、DMF、ジメチルスルホキシド(DMSO)では反応が進行しない。DFB濃度は6.17×10−4mol(/セルロース1g)以上必要で、6.17×10−4mol(/セルロース1g)に満たない場合は高原子価金属イオンの捕集量、特にバナジウムの捕集量が減少する傾向にある。 Meanwhile, in a separate vial, DFB is added to the solvent and heated to completely dissolve the DFB. The solvent used here is preferably a basic solvent such as pyridine, and the reaction does not proceed with DMF or dimethyl sulfoxide (DMSO). DFB concentration required 6.17 × 10 -4 mol (/ cellulose 1g) above, 6.17 × 10 -4 mol (/ cellulose 1g) collection amount of high-valence metal ions if less than, in particular vanadium There is a tendency for the amount of collected to decrease.

ついで、上記DFB・ピリジン溶液に、ヨウ化ナトリウムで処理したろ紙を添加し、80〜100℃で、2.5〜12時間攪拌する。その後、DFBが導入されたセルロースろ紙をメタノールで十分に洗浄し、乾燥する。乾燥は、20〜40℃で8〜24時間行うことが望ましい。   Next, filter paper treated with sodium iodide is added to the DFB / pyridine solution, and the mixture is stirred at 80 to 100 ° C. for 2.5 to 12 hours. Thereafter, the cellulose filter paper into which DFB is introduced is thoroughly washed with methanol and dried. The drying is desirably performed at 20 to 40 ° C. for 8 to 24 hours.

上記した方法に従えば、原子価が3以上の高原子価金属イオンを効率良く選択的に捕集し、容易に検出できる捕集・検出剤を作製することができ、特に、バナジウムをpH2以下の強酸性下においても捕集・検出できる捕集・検出剤を作製することができる。   According to the above method, a high-valence metal ion having a valence of 3 or more can be efficiently and selectively collected, and a collection / detection agent that can be easily detected can be produced. It is possible to produce a collection / detection agent that can be collected / detected even under strong acidity.

以下、実施例により本発明の捕集・検出剤とその使用方法について具体的に説明するが、当該実施例によって本発明が制限されるものではない。   EXAMPLES Hereinafter, although the collection / detection agent of the present invention and the method of using the same will be described in detail with reference to examples, the present invention is not limited to the examples.

(実施例1)
<捕集・検出剤の作製>
ろ紙(セルロース)1gをバイアルに入れ、DMF50mlを加えて十分に浸し、塩化チオニル6.17×10−4molを加えて90℃で2時間反応させた。次に、クロライド化したろ紙を取り出し、アセトンで十分に洗浄した後、これを再びバイアルに入れて、ヨウ化ナトリウム1×10−4molが溶解したアセトン50mlに30℃で4時間浸した。一方、別バイアルにおいて、DFB6.17×10−4molをピリジン50mlに加えて完全にDFBを溶解させた。ついで、DFB・ピリジン溶液に、ヨウ化ナトリウムで処理したろ紙を添加し、90℃で3時間反応させた後、ろ紙を取り出し、メタノールで十分に洗浄し風乾することで、DFBが導入されたセルロースろ紙(捕集・検出剤)を作製した。
Example 1
<Production of collection / detection agent>
Put filter paper (cellulose) 1 g in a vial, fully immersed added 50 ml of DMF, was added thionyl chloride 6.17 × 10 -4 mol to 2 hours at 90 ° C.. Next, the chlorinated filter paper was taken out and thoroughly washed with acetone, and then again put in a vial and immersed in 50 ml of acetone in which 1 × 10 −4 mol of sodium iodide was dissolved at 30 ° C. for 4 hours. On the other hand, in another vial, 6.17 × 10 −4 mol of DFB was added to 50 ml of pyridine to completely dissolve DFB. Next, filter paper treated with sodium iodide is added to the DFB / pyridine solution, and after reacting at 90 ° C. for 3 hours, the filter paper is taken out, thoroughly washed with methanol, and air-dried, so that DFB is introduced into the cellulose. A filter paper (collecting / detecting agent) was prepared.

<評価>
原子価が3以上の高原子価金属イオン(バナジウムイオン)を含むサンプル溶液として、市販されている飲料用ミネラルウォーターを使用した。
<Evaluation>
Commercially available mineral water for beverages was used as a sample solution containing a high-valence metal ion (vanadium ion) having a valence of 3 or more.

まず、前処理として、サンプル溶液500mLに塩酸を数滴加えた後、蒸発により10mL以下まで濃縮し、さらにこの溶液に塩酸を加えて、塩酸濃度が0.1molL−1になるように調整し、全量を10mLとした(50倍濃縮、pH2)。ついで、この濃縮溶液に上記で作製したDFB−ろ紙(捕集・検出剤)を室温(25℃)で5分間浸した後、これを取り出し、DFB−ろ紙に捕集されたバナジウムイオン濃度を反射分光計を用いて測定した(測定波長:480nm、測定径:3×3mm、使用機器:日立製作所製200−20型)。その結果、捕集されたバナジウムの濃度は2.5ppmであった。また、同時に目視による比色測定でその濃度を評価したところ、2.5ppmとなり、反射分光計の測定値と一致した。なお、反射分光計による濃度測定では、バナジウムイオンの濃度が0、0.5、1、2.5、5、10ppmの溶液に浸漬して取り出した各DFB−ろ紙の吸光度を予め測定し作成した検量線と試料ろ紙の吸光度とからその濃度を算出した。また、比色測定では、上記と同様にして得た各DFB−ろ紙の色を基準とし、これと試料ろ紙の色を目視で比較し判定した。 First, as a pretreatment, several drops of hydrochloric acid were added to 500 mL of the sample solution, and then concentrated to 10 mL or less by evaporation. Further, hydrochloric acid was added to this solution to adjust the hydrochloric acid concentration to 0.1 mol L −1 , The total volume was 10 mL (50-fold concentration, pH 2). Next, the DFB-filter paper (collecting / detecting agent) prepared above was immersed in this concentrated solution for 5 minutes at room temperature (25 ° C.), then taken out, and the vanadium ion concentration collected on the DFB-filter paper was reflected. Measurement was performed using a spectrometer (measurement wavelength: 480 nm, measurement diameter: 3 × 3 mm, equipment used: Hitachi Model 200-20). As a result, the concentration of the collected vanadium was 2.5 ppm. Moreover, when the density | concentration was evaluated by the colorimetric measurement by visual observation simultaneously, it became 2.5 ppm and corresponded with the measured value of a reflection spectrometer. In addition, in the density | concentration measurement by a reflection spectrometer, the light absorbency of each DFB-filter paper taken out by immersing in the solution whose vanadium ion density | concentration is 0, 0.5, 1, 2.5, 5, 10ppm was created beforehand The concentration was calculated from the calibration curve and the absorbance of the sample filter paper. Further, in the colorimetric measurement, the color of each DFB-filter paper obtained in the same manner as above was used as a reference, and this was compared with the color of the sample filter paper for judgment.

(比較例1)
イミノジ酢酸をアクリル樹脂に固定したカートリッジ(Inertsep ME1;ジーエルサイエンス社製)に、実施例1で用いたものと同じ濃縮溶液をカートリッジに通液後、超純水20mlで洗浄し、1N硝酸1ml(pH1以下)で溶出した。ついで、原子吸光光度法により溶出液中のバナジウムイオンの濃度を測定したところ、検出されなかった。
(Comparative Example 1)
The same concentrated solution used in Example 1 was passed through a cartridge in which iminodiacetic acid was fixed to an acrylic resin (Inertsep ME1; manufactured by GL Sciences Inc.), then washed with 20 ml of ultrapure water, and 1 ml of 1N nitric acid ( elution at pH 1 or less). Subsequently, when the concentration of vanadium ion in the eluate was measured by atomic absorption spectrophotometry, it was not detected.

Claims (5)

ヒドロキサム酸基を有する化合物を担体に導入してなる原子価3以上の金属イオンの捕集・検出剤。   An agent for collecting and detecting metal ions having a valence of 3 or more, wherein a compound having a hydroxamic acid group is introduced into a carrier. 前記担体がセルロースである請求項1記載の捕集・検出剤。   The collection / detection agent according to claim 1, wherein the carrier is cellulose. 捕集・検出対象の金属イオンを含む溶液のpHが2以下である請求項1または2記載の捕集・検出剤。   The collection / detection agent according to claim 1 or 2, wherein the pH of the solution containing the metal ions to be collected / detected is 2 or less. 捕集・検出対象の金属イオンがバナジウムイオンである請求項1〜3いずれか1項に記載の捕集・検出剤。   The collection / detection agent according to claim 1, wherein the metal ions to be collected / detected are vanadium ions. 前記ヒドロキサム酸基を有する化合物がデスフェリオキサミンB(DFB)である請求項1〜4いずれか1項に記載の捕集・検出剤。   The collection / detection agent according to claim 1, wherein the compound having a hydroxamic acid group is desferrioxamine B (DFB).
JP2005363924A 2005-12-16 2005-12-16 Metal ion detection method Active JP5249500B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP2005363924A JP5249500B2 (en) 2005-12-16 2005-12-16 Metal ion detection method

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP2005363924A JP5249500B2 (en) 2005-12-16 2005-12-16 Metal ion detection method

Related Child Applications (1)

Application Number Title Priority Date Filing Date
JP2013012918A Division JP5610410B2 (en) 2013-01-28 2013-01-28 Agent for collecting and detecting high-valent metal ions

Publications (2)

Publication Number Publication Date
JP2007161967A true JP2007161967A (en) 2007-06-28
JP5249500B2 JP5249500B2 (en) 2013-07-31

Family

ID=38245236

Family Applications (1)

Application Number Title Priority Date Filing Date
JP2005363924A Active JP5249500B2 (en) 2005-12-16 2005-12-16 Metal ion detection method

Country Status (1)

Country Link
JP (1) JP5249500B2 (en)

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2008214551A (en) * 2007-03-06 2008-09-18 Hitachi Chem Co Ltd Collecting agent for high valent metal ion
JP2013523975A (en) * 2010-04-06 2013-06-17 ナルコ カンパニー Metal capture polymer
JPWO2014038191A1 (en) * 2012-09-04 2016-08-08 アトナープ株式会社 System and method for detecting metals in solution

Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5028587A (en) * 1973-07-14 1975-03-24
JPS5948085A (en) * 1982-08-20 1984-03-19 デヴオ−−ホルバイン インタ−ナショナル エヌ・ヴィ Insoluble sequestering composition
JPS60251931A (en) * 1984-05-10 1985-12-12 イエルカー・ポラート Metal ion adsorbing substance and its production
JPH08295966A (en) * 1995-04-28 1996-11-12 Japan Tobacco Inc Method for separating and recovering molybdenum and vandadium
JPH08301930A (en) * 1995-04-28 1996-11-19 Japan Tobacco Inc New chelate polymer and its production
JP2000073043A (en) * 1998-04-14 2000-03-07 Coletica Fine particle having surface hydroxamic group capable of chelating metallic ion and mixed wall of crosslinked protein and polysaccharide, its production, and its application, in particular, to cosmetic, medicine and agricultural food

Patent Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5028587A (en) * 1973-07-14 1975-03-24
JPS5948085A (en) * 1982-08-20 1984-03-19 デヴオ−−ホルバイン インタ−ナショナル エヌ・ヴィ Insoluble sequestering composition
JPS60251931A (en) * 1984-05-10 1985-12-12 イエルカー・ポラート Metal ion adsorbing substance and its production
JPH08295966A (en) * 1995-04-28 1996-11-12 Japan Tobacco Inc Method for separating and recovering molybdenum and vandadium
JPH08301930A (en) * 1995-04-28 1996-11-19 Japan Tobacco Inc New chelate polymer and its production
JP2000073043A (en) * 1998-04-14 2000-03-07 Coletica Fine particle having surface hydroxamic group capable of chelating metallic ion and mixed wall of crosslinked protein and polysaccharide, its production, and its application, in particular, to cosmetic, medicine and agricultural food

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2008214551A (en) * 2007-03-06 2008-09-18 Hitachi Chem Co Ltd Collecting agent for high valent metal ion
JP2013523975A (en) * 2010-04-06 2013-06-17 ナルコ カンパニー Metal capture polymer
JPWO2014038191A1 (en) * 2012-09-04 2016-08-08 アトナープ株式会社 System and method for detecting metals in solution

Also Published As

Publication number Publication date
JP5249500B2 (en) 2013-07-31

Similar Documents

Publication Publication Date Title
Shahat et al. Novel nano-conjugate materials for effective arsenic (V) and phosphate capturing in aqueous media
Kenawy et al. Determination by AAS of some trace heavy metal ions in some natural and biological samples after their preconcentration using newly chemically modified chloromethylated polystyrene-PAN ion-exchanger
Oyola et al. High surface-area amidoxime-based polymer fibers co-grafted with various acid monomers yielding increased adsorption capacity for the extraction of uranium from seawater
Otero-Romaní et al. Inductively coupled plasma–optical emission spectrometry/mass spectrometry for the determination of Cu, Ni, Pb and Zn in seawater after ionic imprinted polymer based solid phase extraction
Yousefi et al. Simultaneous extraction and preconcentration of uranium and thorium in aqueous samples by new modified mesoporous silica prior to inductively coupled plasma optical emission spectrometry determination
Daşbaşı et al. Synthesis, characterization and application of a new chelating resin for solid phase extraction, preconcentration and determination of trace metals in some dairy samples by flame atomic absorption spectrometry
Hassanien et al. Synthesis and characterisation of morin-functionalised silica gel for the enrichment of some precious metal ions
Hashemi et al. Molecularly imprinted stir bar sorptive extraction coupled with atomic absorption spectrometry for trace analysis of copper in drinking water samples
Shakerian et al. Synthesis and characterisation of nano-pore antimony imprinted polymer and its use in the extraction and determination of antimony in water and fruit juice samples
Parvizi et al. Preconcentration and ultra-trace determination of hexavalent chromium ions using tailor-made polymer nanoparticles coupled with graphite furnace atomic absorption spectrometry: ultrasonic assisted-dispersive solid-phase extraction
Yilmaz et al. Determination of some trace metals by FAAS after solid-phase extraction with amberlite XAD-1180/TAN chelating resin
RU2244919C2 (en) Method of detection and method for quantitative analysis of hydrogen radicals
Naeemullah et al. Cloud point extraction and flame atomic absorption spectrometric determination of cadmium and nickel in drinking and wastewater samples
Salimi et al. Trace measurement of lead and cadmium ions in wastewater samples using a novel dithizone immobilized metal–organic framework‐based μ‐dispersive solid‐phase extraction
JP6176636B2 (en) Mesoporous silica supporting iodine ion adsorbing compound, iodine ion collector and iodine recovery method using the same
JP5249500B2 (en) Metal ion detection method
Mortada et al. Cloud point extraction for the determination of trace amounts of Pt (IV) by graphite furnace atomic absorption spectrometry
US10605799B2 (en) Systems and methods for detecting metal ion concentrations in subjects
Tokalıoğlu et al. Solid phase extraction of Cu (II), Ni (II), Pb (II), Cd (II) and Mn (II) ions with 1-(2-thiazolylazo)-2-naphthol loaded Amberlite XAD-1180
Kiptoo et al. Solid-phase extraction of Zn (II), Cu (II), Ni (II) and Pb (II) on poly (vinyl chloride) modified with 3-ferrocenyl-3-hydroxydithioacrylic acid, and their subsequent determination by electrothermal atomic absorption spectrometry
JP5610410B2 (en) Agent for collecting and detecting high-valent metal ions
Anđelković et al. Binding of cadmium to soil humic acid as a function of carboxyl group content
JP2013010082A (en) Mesoporous silica carrying compound having iodine ion adsorptivity, and iodine ion collector and method for collecting iodine using the same
Moghimi Extraction of Ni (II) on micro crystalline naphthalene modified with organic-solution-processable functionalized nano graphene
Abkenar et al. Speciation of chromium in water samples with homogeneous liquid-liquid extraction and determination by flame atomic absorption spectrometry

Legal Events

Date Code Title Description
A621 Written request for application examination

Free format text: JAPANESE INTERMEDIATE CODE: A621

Effective date: 20081113

A977 Report on retrieval

Free format text: JAPANESE INTERMEDIATE CODE: A971007

Effective date: 20111027

A131 Notification of reasons for refusal

Free format text: JAPANESE INTERMEDIATE CODE: A131

Effective date: 20111101

A521 Request for written amendment filed

Free format text: JAPANESE INTERMEDIATE CODE: A523

Effective date: 20120104

A521 Request for written amendment filed

Free format text: JAPANESE INTERMEDIATE CODE: A523

Effective date: 20120117

A02 Decision of refusal

Free format text: JAPANESE INTERMEDIATE CODE: A02

Effective date: 20121030

A521 Request for written amendment filed

Free format text: JAPANESE INTERMEDIATE CODE: A523

Effective date: 20130128

A911 Transfer to examiner for re-examination before appeal (zenchi)

Free format text: JAPANESE INTERMEDIATE CODE: A911

Effective date: 20130206

A521 Request for written amendment filed

Free format text: JAPANESE INTERMEDIATE CODE: A523

Effective date: 20130208

TRDD Decision of grant or rejection written
A01 Written decision to grant a patent or to grant a registration (utility model)

Free format text: JAPANESE INTERMEDIATE CODE: A01

Effective date: 20130319

A61 First payment of annual fees (during grant procedure)

Free format text: JAPANESE INTERMEDIATE CODE: A61

Effective date: 20130412

R150 Certificate of patent or registration of utility model

Ref document number: 5249500

Country of ref document: JP

Free format text: JAPANESE INTERMEDIATE CODE: R150

Free format text: JAPANESE INTERMEDIATE CODE: R150

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20160419

Year of fee payment: 3

R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250

R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250

R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250

R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250

R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250

R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250

R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250

S531 Written request for registration of change of domicile

Free format text: JAPANESE INTERMEDIATE CODE: R313531

S533 Written request for registration of change of name

Free format text: JAPANESE INTERMEDIATE CODE: R313533

R350 Written notification of registration of transfer

Free format text: JAPANESE INTERMEDIATE CODE: R350

R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250

S531 Written request for registration of change of domicile

Free format text: JAPANESE INTERMEDIATE CODE: R313531

R350 Written notification of registration of transfer

Free format text: JAPANESE INTERMEDIATE CODE: R350