JP2009036689A - METHOD FOR EASY ANALYSIS OF TRACE AMOUNT OF Se IN ENVIRONMENTAL WATER - Google Patents

METHOD FOR EASY ANALYSIS OF TRACE AMOUNT OF Se IN ENVIRONMENTAL WATER Download PDF

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JP2009036689A
JP2009036689A JP2007202507A JP2007202507A JP2009036689A JP 2009036689 A JP2009036689 A JP 2009036689A JP 2007202507 A JP2007202507 A JP 2007202507A JP 2007202507 A JP2007202507 A JP 2007202507A JP 2009036689 A JP2009036689 A JP 2009036689A
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water
dan
environmental water
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Tadao Inose
匡生 猪瀬
Kyoko Fujimoto
京子 藤本
Naoshi Yoshida
直志 吉田
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JFE Steel Corp
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Abstract

<P>PROBLEM TO BE SOLVED: To provide a method for easy analysis of trace amount of Se in environmental water and capable of easily, speedily, and highly accurately determining a trace amount of Se contained in environmental water, such as, clean water, various types of drainages, underground water, river water, and water eluted from soil. <P>SOLUTION: The method for easily analyzing a trace amount of Se in environmental water includes a process for diluting environmental water by pure water twenty times or more; the process for adjusting the pH of the environmental water, after the dilution; the process for adding 2,3-diaminonaphthalene (hereinafter, to be referred to as DAN) to the environmental water, after the pH adjustment; the process for forming an Se complex of DAN by heating the environmental water after the addition of DAN; the process for extracting the Se complex of DAN by an organic solvent; and the process for determining extracted Se of the Se complex of DAN in the organic solvent by using a fluorometer. <P>COPYRIGHT: (C)2009,JPO&INPIT

Description

本発明は、上水、各種排水、地下水、河川水、土壌溶出水などの環境水中に含まれる微量Se(セレン)の簡易分析方法に関する。   The present invention relates to a simple analysis method for trace amounts of Se (selenium) contained in environmental water such as clean water, various wastewaters, ground water, river water, and soil elution water.

水道水などの上水、各種排水、地下水、河川水、土壌溶出水など環境水に対しては、人の健康に関わる水質基準に基づき、各種溶質元素の濃度が規定されている。   For environmental water such as tap water, tap water, various wastewater, groundwater, river water, and soil elution water, the concentration of various solute elements is defined based on water quality standards related to human health.

Seもその一つであり、種々の方法、例えば、JIS K 0102に規定されている3,3-ジアミノベンジジン吸光光度法、水素化物発生原子吸光法および水素化物発生ICP発光分光分析法などや非特許文献1に記載されているボルタンメトリー法などの電気化学的測定法により、その定量が行われている。
T. Ishiyama and T. Tanaka; Anal. Chem.,68(1996)3789
Se is one of them, and various methods such as 3,3-diaminobenzidine absorptiometry, hydride generation atomic absorption method and hydride generation ICP emission spectroscopy as defined in JIS K 0102 The quantification is performed by an electrochemical measurement method such as a voltammetry method described in Patent Document 1.
T. Ishiyama and T. Tanaka; Anal. Chem., 68 (1996) 3789

しかしながら、3,3-ジアミノベンジジン吸光光度法は、比較的簡便な方法であるが、分析感度が低く、微量濃度の分析には不向きであり、水素化物発生原子吸光法や水素化物発生ICP発光分光分析法は、分析感度が高く、微量濃度の分析に適した方法であるが、ガス配管や排気ダクトなど大掛かりな付帯設備を必要とするばかりか、煩雑な試料の前処理操作も必要となる。また、ボルタンメトリー法は、簡便、迅速な分析方法であるが、極めて煩雑な作用電極表面のメンテナンスや測定前の試料調整が必要であるため、再現性に劣り、必ずしも高い分析精度が得られない。   However, 3,3-diaminobenzidine absorptiometry is a relatively simple method, but its analytical sensitivity is low and unsuitable for analysis of trace concentrations, and hydride generation atomic absorption or hydride generation ICP emission spectroscopy. The analytical method has high analytical sensitivity and is suitable for analyzing trace concentrations, but requires not only large incidental facilities such as gas pipes and exhaust ducts but also complicated sample pretreatment operations. In addition, the voltammetry method is a simple and rapid analysis method, but it requires extremely complicated maintenance of the working electrode surface and sample preparation before measurement, so that the reproducibility is inferior and high analysis accuracy is not always obtained.

本発明は、上水、各種排水、地下水、河川水、土壌溶出水などの環境水中に含まれる微量Seを、簡便、迅速に高精度で定量できる環境水中の微量Seの簡易分析方法を提供することを目的とする。   The present invention provides a simple method for analyzing trace amounts of Se in environmental water that can be quantified easily and quickly with high accuracy in trace amounts of Se contained in environmental water such as tap water, various effluents, ground water, river water, and soil elution water. For the purpose.

この目的は、環境水を純水によって20倍以上に希釈する工程と、前記希釈後の環境水のpHを調整する工程と、前記pH調整後の環境水に2,3-ジアミノナフタレン(以下、DANと呼ぶ)を添加する工程と、前記DAN添加後の環境水を加温してDANのSe錯体を形成させる工程と、前記DANのSe錯体を有機溶媒で抽出する工程と、前記DANのSe錯体の抽出された有機溶媒中のSeを、蛍光光度計を用いて、標準添加法で定量する工程と、を有する環境水中の微量Seの簡易分析方法により達成される。   The purpose of this is to dilute environmental water 20 times or more with pure water, adjust the pH of the diluted environmental water, and add 2,3-diaminonaphthalene (hereinafter, Adding the DAN), heating the environmental water after the DAN addition to form a DAN Se complex, extracting the DAN Se complex with an organic solvent, and the DAN Se This is achieved by a simple analysis method for trace amounts of Se in environmental water having a step of quantifying Se in an organic solvent from which a complex has been extracted by a standard addition method using a fluorometer.

本発明により、上水、各種排水、地下水、河川水、土壌溶出水などの環境水中に含まれる微量Seを、簡便、迅速に高精度で定量できる。すなわち、煩雑な試料の前処理や大掛かり付帯設備が不要で、30分程度で高精度に微量Seを定量できる。また、全ての操作を1本の試験管内できるので、非常に簡便である、使用する試薬量が少ない、操作中のコンタミネーションや試料の減少もなくより高精度に測定できる、といったメリットもある。   According to the present invention, trace amounts of Se contained in environmental water such as clean water, various waste waters, ground water, river water, and soil elution water can be quantified simply and quickly with high accuracy. In other words, complicated sample pretreatment and large-scale incidental facilities are not required, and trace Se can be quantified with high accuracy in about 30 minutes. In addition, since all the operations can be performed in one test tube, there are also advantages such as being very simple, using a small amount of reagent, and measuring with higher accuracy without contamination during operation and reduction of samples.

本発明の分析方法が対象としている上水、各種排水、地下水、河川水、土壌溶出水など環境水は、分析試料として、JIS K 0102法や環告46号法などに準拠して採取される。   Environmental water such as clean water, various effluents, ground water, river water, and soil elution water, which is the subject of the analysis method of the present invention, is collected as an analysis sample in accordance with the JIS K 0102 method or the Notification No. 46 method. .

環境水は、上記方法により複数の試験管に採取し、それぞれの試験管に採取された環境水を純水で20倍以上に希釈する。これは、環境水中に共存する他の元素の影響を回避するためである。しかし、希釈率が大きすぎると、試料の量が多くなり操作が煩雑になったり、後に行われる蛍光光度測定の感度が低下するので、30〜50倍に希釈することが好ましい。   The environmental water is collected in a plurality of test tubes by the above method, and the environmental water collected in each test tube is diluted 20 times or more with pure water. This is to avoid the influence of other elements coexisting in the environmental water. However, if the dilution rate is too large, the amount of the sample increases, the operation becomes complicated, and the sensitivity of the subsequent fluorometric measurement is reduced. Therefore, it is preferable to dilute 30 to 50 times.

希釈後の試験管に、濃度既知のSe標準溶液を段階的に添加し、標準添加法用の試料を作成する。Se標準溶液の添加量は、Se量換算で5〜30ngの範囲が好ましく、少なくとも2段階、好ましくは10、20、30ngのように3段階に変えた試料を準備することが好ましい。   A Se standard solution with a known concentration is added stepwise to the diluted test tube to prepare a sample for the standard addition method. The addition amount of the Se standard solution is preferably in the range of 5 to 30 ng in terms of Se amount, and it is preferable to prepare a sample that has been changed to at least two stages, preferably three stages such as 10, 20, and 30 ng.

また、これとは別に、環境水やSe標準溶液を含まず、同量の純水のみの入った試験管を、対照試料として準備する。この対照試料は、試薬ブランクとしてゼロ点補正に用いられる。   Separately from this, a test tube containing only the same amount of pure water and not containing environmental water or Se standard solution is prepared as a control sample. This control sample is used as a reagent blank for zero point correction.

Se標準溶液が段階的に添加された試験管および純水のみの試験管に、塩酸を加えてpH調整する。このとき、pHが1.0〜1.5となるようにすることが好ましい。   Adjust pH by adding hydrochloric acid to a test tube to which Se standard solution is added stepwise and a test tube containing pure water only. At this time, it is preferable to adjust the pH to 1.0 to 1.5.

pH調整された全ての試験管に、DANを一定量添加し、加温して、DANのSe錯体を形成させる。このとき、DANのSe錯体を形成するには、50℃で20分程度加温することが好ましい。   A certain amount of DAN is added to all the pH-adjusted test tubes and heated to form a DAN Se complex. At this time, in order to form a DAN Se complex, it is preferable to heat at 50 ° C. for about 20 minutes.

DANのSe錯体を形成させた全ての試験管に、例えば、シクロヘキサンやトルエンなどの有機溶媒を3ml以上添加して、DANのSe錯体を溶媒抽出する。このとき、有機溶媒の添加量は、少なすぎると、濃縮率は高くなるが、蛍光光度の測定には有機溶媒を蛍光セルに満たす十分な量確保するのが困難なため、不都合になる。フローセル使用の蛍光光度計を用いる場合では、3ml程度あれば十分に計測できる。   For example, add 3 ml or more of an organic solvent such as cyclohexane or toluene to all test tubes in which the DAN Se complex is formed, and extract the DAN Se complex by solvent. At this time, if the amount of the organic solvent added is too small, the concentration rate becomes high, but it becomes inconvenient because it is difficult to secure a sufficient amount of the organic solvent to fill the fluorescent cell for the measurement of the fluorescence. When using a fluorimeter using a flow cell, about 3 ml can be measured sufficiently.

DANのSe錯体を抽出した有機溶媒は、試験管の上部に浮遊するので、それを蛍光光度計に注入して、例えば、シクロヘキサンを有機溶媒に用いた場合は、励起波長375nmで蛍光波長520nmを測定し、標準添加法により、すなわち段階的にSe量を添加したときのSe量と蛍光光度との関係から、分析対象の水中のSe量を求める。なお、励起波長や蛍光波長は、用いる有機溶媒により適宜選択される。   The organic solvent from which the DAN Se complex is extracted floats at the top of the test tube. For example, when cyclohexane is used as the organic solvent, the excitation wavelength is 375 nm and the fluorescence wavelength is 520 nm. Measure and obtain the amount of Se in the water to be analyzed by the standard addition method, that is, from the relationship between the amount of Se when the amount of Se is added stepwise and the fluorescence intensity. The excitation wavelength and the fluorescence wavelength are appropriately selected depending on the organic solvent used.

土木材料用の4種類の無機物から環告46号法によって溶出水A、B、C、Dを、それぞれ3本の試験管に1本の試験管あたり1ml採取した。各溶出水の3本の試験管に、純水、Se標準溶液、塩酸を順次の添加し、全量が30ml、pHが1.0〜1.5、Se添加量が0、10、20ngの3種の試料を作成した。これとは別に、全量で30ml、pHが1.0〜1.5の純水と塩酸のみの入った試験管を、対照試料として、1本準備した。   Elution water A, B, C, and D were collected from each of the four types of inorganic materials for civil engineering materials according to the Notification No. 46 method in three test tubes. Purified water, Se standard solution, and hydrochloric acid are added sequentially to three test tubes of each elution water, and three types of samples with a total volume of 30 ml, pH of 1.0 to 1.5, and Se addition amounts of 0, 10, and 20 ng are added. Created. Separately, a test tube containing only 30 ml of pure water having a pH of 1.0 to 1.5 and hydrochloric acid was prepared as a control sample.

このように調整された全ての試験管に、0.1M塩酸で調整した0.2%DAN溶液を5ml添加後、50℃のアルミブロックバスで20分加熱し、DANのSe錯体を形成した。   5 ml of 0.2% DAN solution adjusted with 0.1M hydrochloric acid was added to all the test tubes prepared in this way, and then heated in an aluminum block bath at 50 ° C. for 20 minutes to form a DAN Se complex.

放冷後、シクロヘキサンを3ml添加して、DANのSe錯体を溶媒抽出した。   After allowing to cool, 3 ml of cyclohexane was added, and the Se complex of DAN was extracted with a solvent.

浮上している有機溶媒を蛍光光度計に注入し、励起波長375nmで蛍光波長520nmの光度を測定し、標準添加法により、すなわち図1(a)、(b)、(c)、(d)に示すSe量と蛍光光度との関係を求め、直線が横軸を交差する点から、溶出水A、B、C、DのSe量を定量した。   Inject the floating organic solvent into the fluorometer, measure the luminous intensity at the excitation wavelength of 375 nm and the fluorescence wavelength of 520 nm, by the standard addition method, that is, FIG. 1 (a), (b), (c), (d) The amount of Se in elution water A, B, C, and D was quantified from the point where the straight line intersects the horizontal axis.

結果を、別途水素化物発生原子吸光法で求めたSe量とともに、表1に示す。   The results are shown in Table 1 together with the amount of Se separately determined by hydride generation atomic absorption.

本発明法で求めたSe量は、水素化物発生原子吸光法で求めたSe量とほぼ同一であり、また、分析時間も45分程度で短く、本発明法は、上水、各種排水、地下水、河川水、土壌溶出水などの環境水中に含まれる微量Seを簡便、迅速に高精度で定量できる方法であることがわかる。   The amount of Se determined by the method of the present invention is almost the same as the amount of Se determined by the hydride generation atomic absorption method, and the analysis time is as short as about 45 minutes. It can be seen that it is a simple, rapid and highly accurate method for quantifying trace Se contained in environmental water such as river water and soil elution water.

Figure 2009036689
Figure 2009036689

本発明で用いた標準添加法による定量結果を示す図である。It is a figure which shows the fixed_quantity | quantitative_assay result by the standard addition method used by this invention.

Claims (1)

環境水を、純水によって20倍以上に希釈する工程と、
前記希釈後の環境水のpHを、調整する工程と、
前記pH調整後の環境水に、2,3-ジアミノナフタレン(以下、DANと呼ぶ)を添加する工程と、
前記DAN添加後の環境水を、加温してDANのSe錯体を形成させる工程と、
前記DANのSe錯体を、有機溶媒で抽出する工程と、
前記DANのSe錯体の抽出された有機溶媒中のSeを、蛍光光度計を用いて、標準添加法で定量する工程と、
を有する環境水中の微量Seの簡易分析方法。
A step of diluting environmental water with pure water 20 times or more,
Adjusting the pH of the environmental water after dilution;
Adding 2,3-diaminonaphthalene (hereinafter referred to as DAN) to the environmental water after pH adjustment;
Heating the environmental water after the addition of DAN to form a DAN Se complex;
Extracting the Se complex of DAN with an organic solvent;
Se in the organic solvent from which the Se complex of DAN has been extracted is quantified by a standard addition method using a fluorometer,
A simple method for analyzing trace amounts of Se in environmental water.
JP2007202507A 2007-08-03 2007-08-03 METHOD FOR EASY ANALYSIS OF TRACE AMOUNT OF Se IN ENVIRONMENTAL WATER Pending JP2009036689A (en)

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Cited By (6)

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CN102621133A (en) * 2012-04-17 2012-08-01 北京师范大学 Method for detecting 1,8-diaminonaphthalene based on optical DNA (Deoxyribonucleic Acid) biosensor
CN103333676A (en) * 2013-06-18 2013-10-02 吉林大学 Selenium ion fluorescent probe, and preparation method and application thereof
CN104422672A (en) * 2013-08-21 2015-03-18 上海宝钢工业技术服务有限公司 Method for determining content of selenium in soil by adopting microwave digestion-atomic fluorescence technology
CN104931468A (en) * 2015-03-23 2015-09-23 浙江大学 Method for determining content of total selenium, inorganic selenium and organic selenium of selenium yeast
CN106323933A (en) * 2016-08-12 2017-01-11 浙江大学 Method for determining elementary selenium content
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Cited By (9)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102621133A (en) * 2012-04-17 2012-08-01 北京师范大学 Method for detecting 1,8-diaminonaphthalene based on optical DNA (Deoxyribonucleic Acid) biosensor
CN102621133B (en) * 2012-04-17 2016-08-03 北京师范大学 A kind of detection method of the 1,8-diaminonaphthalene of optically-based DNA biosensor
CN103333676A (en) * 2013-06-18 2013-10-02 吉林大学 Selenium ion fluorescent probe, and preparation method and application thereof
CN103333676B (en) * 2013-06-18 2014-12-10 吉林大学 Selenium ion fluorescent probe, and preparation method and application thereof
CN104422672A (en) * 2013-08-21 2015-03-18 上海宝钢工业技术服务有限公司 Method for determining content of selenium in soil by adopting microwave digestion-atomic fluorescence technology
CN104422672B (en) * 2013-08-21 2018-08-17 上海宝钢工业技术服务有限公司 Using the method for Se content in micro-wave digestion-In Soil With Atomic Fluorescence
CN104931468A (en) * 2015-03-23 2015-09-23 浙江大学 Method for determining content of total selenium, inorganic selenium and organic selenium of selenium yeast
CN106323933A (en) * 2016-08-12 2017-01-11 浙江大学 Method for determining elementary selenium content
CN111855847A (en) * 2020-07-08 2020-10-30 浙江大学 Method for determining total selenium content in selenium-enriched proteoglycan by high performance liquid chromatography

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