JP6399003B2 - Sample solution preparation method - Google Patents
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Description
本発明は、試料液の調製方法に関するものである。 The present invention relates to a method for preparing a sample solution.
従来、溶液サンプル中に含まれる元素の元素分析方法として、誘導結合プラズマ(ICP)発光分光分析法(以下、「ICP」という。)が使用されている。 Conventionally, inductively coupled plasma (ICP) emission spectroscopy (hereinafter referred to as “ICP”) has been used as an elemental analysis method for elements contained in solution samples.
ICPは、様々な気体を用いて発生させることができるが、特にArガスを用いたICP(ICP−AES)は広く使用されるようになっている。 ICP can be generated using various gases, and in particular, ICP using Ar gas (ICP-AES) is widely used.
図3は、一般的なICP分析装置においてプラズマを発生させるプラズマトーチを示したものである。図3に示すように、プラズマトーチ10に、予めArガス20を流しておき、高周波誘電コイル40に高周波電流を流すことで、プラズマが発生する。そして、プラズマトーチ10内に霧化された溶液試料30が導入され、プラズマ炎内で励起され、基底状態に戻る際に出されるスペクトルが分光器(図示せず。)で検出される。
FIG. 3 shows a plasma torch for generating plasma in a general ICP analyzer. As shown in FIG. 3, plasma is generated by flowing
ここで、溶液試料30中に溶媒の一部又は全部として揮発性の高い有機溶媒が含まれていると、溶液試料30がプラズマトーチに到達するまでの間に、有機溶媒が気化し、プラズマトーチ10内のガス流量が不安定化し、プラズマの不安定化や失火につながり、延いては測定精度の悪化等の原因になる。
Here, if the
そこで、分析手段としてICP装置を備えた液体クロマトグラフにおいて、カラムの出口から排出されてICP装置に導入される試料液に対して、ICP装置に導入される直前に、プラズマを安定に維持する溶媒を試料液に混合させて試料液を希釈させる方法が報告されている(例えば、特許文献1参照)。 Therefore, in a liquid chromatograph equipped with an ICP device as an analysis means, a solvent that stably maintains plasma immediately before being introduced into the ICP device with respect to the sample solution discharged from the column outlet and introduced into the ICP device. A method for diluting a sample solution by mixing the sample solution with a sample solution has been reported (for example, see Patent Document 1).
ところで、分析対象の溶液に含まれる微量の金属元素等を分析する場合には、ICP測定用の試料液に含まれる金属元素の含有量をできる限り増加させるとともに、有機溶媒の含有量を低減させ、ICP分析に適した試料液を調製することが望まれる。 By the way, when analyzing a trace amount of metal elements contained in the solution to be analyzed, the content of the metal elements contained in the sample solution for ICP measurement is increased as much as possible, and the content of the organic solvent is reduced. It is desirable to prepare a sample solution suitable for ICP analysis.
そこで本発明では、有機溶媒を多く含む溶液についてICPにより元素分析を行う場合に、プラズマの失火や不安定化を抑えて測定精度を向上させ得る試料液の調製方法を提供する。 Therefore, the present invention provides a method for preparing a sample solution that can improve measurement accuracy by suppressing misfire and instability of plasma when elemental analysis is performed by ICP on a solution containing a large amount of an organic solvent.
上記の目的を達成するために、本発明では、分析対象の溶液を希釈溶媒としての水で希釈して希釈液を作製し、希釈液中の有機溶媒を気化させることにより有機溶媒の含有量をICP分析可能となるまで低減させるようにした。 In order to achieve the above object, in the present invention, a solution to be analyzed is diluted with water as a diluent solvent to prepare a diluted solution, and the organic solvent content is reduced by vaporizing the organic solvent in the diluted solution. Reduced until ICP analysis is possible.
すなわち、ここに開示する方法は、有機溶媒を含む溶液中に含有される金属元素の含有量を高周波誘導結合プラズマ発光分光分析法を用いて検出するための試料液の調製方法であって、上記溶液の一部を水で希釈して希釈液を得る工程と、上記希釈液中の有機溶媒を気化させて上記試料液を得る工程とを備え、上記希釈液中の有機溶媒の上記水に対する濃度は、0.13mol/L超0.57mol/L未満であり、上記試料液中の有機溶媒の上記水に対する濃度は、0.18mol/L未満であり、上記希釈液中の有機溶媒を気化させる時間は、1日以上14日以内であることを特徴とする。 That is, the method disclosed herein is a method for preparing a sample solution for detecting the content of a metal element contained in a solution containing an organic solvent using a high-frequency inductively coupled plasma emission spectroscopy, A step of diluting a part of the solution with water to obtain a diluted solution, and a step of evaporating the organic solvent in the diluted solution to obtain the sample solution, wherein the concentration of the organic solvent in the diluted solution with respect to the water is less than 0.13 mol / L ultra 0.57 mol / L, the concentration for the aqueous organic solvent of the sample solution is 0.18 mol / L than der is, evaporate the organic solvent in the diluent The period of time is 1 day or more and 14 days or less .
高周波誘導結合プラズマ発光分光分析法を用いて溶液中に含有される微量の金属元素を検出するためには、試料液中の溶液の含有量をできる限り多くすることが望ましい。しかしながら、溶液の含有量を増加させることにより、試料液中の有機溶媒の量が増加すると、プラズマの失火や不安定化を招き、測定精度の低下につながる。 In order to detect a trace amount of metal elements contained in a solution using high-frequency inductively coupled plasma optical emission spectrometry, it is desirable to increase the content of the solution in the sample solution as much as possible. However, if the amount of the organic solvent in the sample solution is increased by increasing the content of the solution, plasma misfire or instability is caused, leading to a decrease in measurement accuracy.
本発明によれば、上記溶液の一部を水で希釈して希釈液を得、当該希釈液中の有機溶媒を気化させることにより、希釈液中の有機溶媒の含有量を高周波誘導結合プラズマ発光分光分析法でブランク測定可能な量にまで低減させて、上記試料液を得ることができる。これにより、試料液に含まれる分析対象の金属元素の分散状態を維持しつつその含有量を高めるとともに、高周波誘導結合プラズマ発光分光分析法において金属成分を検出可能な濃度にまで有機溶媒量を低減させ、プラズマの失火や不安定化を抑えて測定精度を向上させることができる。また、上記希釈液中の有機溶媒を気化させる時間は、1日以上14日以内である。これにより、試料液に含まれる分析対象の金属元素の含有量を高め且つその高分散状態を維持するとともに、水分量の過度の減少を抑えつつ有機溶媒量を低減させることができる。 According to the present invention, a part of the solution is diluted with water to obtain a diluted solution, and the organic solvent content in the diluted solution is vaporized, whereby the content of the organic solvent in the diluted solution is determined by high frequency inductively coupled plasma emission. The sample solution can be obtained by reducing the amount to a level capable of performing blank measurement by spectroscopic analysis. As a result, while maintaining the dispersed state of the metal element to be analyzed contained in the sample solution, the content thereof is increased, and the amount of organic solvent is reduced to a concentration at which metal components can be detected in high frequency inductively coupled plasma emission spectrometry. Measurement accuracy can be improved by suppressing plasma misfire and instability. Moreover, the time for vaporizing the organic solvent in the diluent is 1 day or more and 14 days or less. As a result, the content of the metal element to be analyzed contained in the sample liquid can be increased and the highly dispersed state can be maintained, and the amount of the organic solvent can be reduced while suppressing an excessive decrease in the amount of water.
なお、本明細書において、「ブランク測定」可能とは、試料液をICP装置に導入したときに、プラズマの失火や不安定化が起こることなく、試料液の成分の発光強度値が得られることをいい、ブランク測定可能であるときに、ICP測定可能と判定する。 In this specification, “blank measurement” is possible when the sample liquid is introduced into the ICP apparatus, and the emission intensity value of the component of the sample liquid can be obtained without causing plasma misfire or instability. When blank measurement is possible, it is determined that ICP measurement is possible.
好ましい態様では、上記試料液を得る工程では、上記希釈液に含まれる水が所定の気化速度を維持して気化する条件下で、上記希釈液中の有機溶媒を気化させるものである。 In a preferred embodiment, in the step of obtaining the sample solution, the organic solvent in the diluent is vaporized under the condition that water contained in the diluent is vaporized while maintaining a predetermined vaporization rate.
好ましい態様では、上記試料液を得る工程では、上記希釈液からの水の気化速度が5.0mg/日以上10.0mg/日以下となる条件下で、上記希釈液中の有機溶媒を気化させる。これにより、試料液に含まれる分析対象の金属元素の含有量を高め且つその高分散状態を維持するとともに、水分量の過度の減少を抑えつつ有機溶媒量を低減させることができる。 In a preferred embodiment, in the step of obtaining the sample solution, the organic solvent in the diluted solution is vaporized under the condition that the vaporization rate of water from the diluted solution is 5.0 mg / day to 10.0 mg / day. . As a result, the content of the metal element to be analyzed contained in the sample liquid can be increased and the highly dispersed state can be maintained, and the amount of the organic solvent can be reduced while suppressing an excessive decrease in the amount of water.
上記溶液は、具体的には例えば、Liイオン二次電池用の電解液、電気二重層キャパシタ用電解液などが挙げられ、好ましくはLiイオン二次電池用の電解液である。これにより、電解液中に含まれる、例えばMn、Ni、Co等の微量金属成分の含有量を精度よく測定することができる。 Specific examples of the solution include an electrolytic solution for a Li ion secondary battery and an electrolytic solution for an electric double layer capacitor, and preferably an electrolytic solution for a Li ion secondary battery. Thereby, content of trace metal components, such as Mn, Ni, Co, contained in electrolyte solution, can be measured accurately.
このとき、上記有機溶媒としては、例えば炭酸エステルなどのLiイオン二次電池用として一般的な有機溶媒を使用することができる。具体的には、例えばジメチルカーボネート(DMC)、ジエチルカーボネート(DEC)、エチルメチルカーボネート(EMC)、プロピレンカーボネート(PC)、エチレンカーボネート(EC)から選ばれる少なくとも一種であり、特に好ましくはDMC又はDECとECとの混合有機溶媒である。 At this time, as the organic solvent, for example, a general organic solvent for Li ion secondary batteries such as carbonate ester can be used. Specifically, it is at least one selected from, for example, dimethyl carbonate (DMC), diethyl carbonate (DEC), ethyl methyl carbonate (EMC), propylene carbonate (PC), and ethylene carbonate (EC), and particularly preferably DMC or DEC. It is a mixed organic solvent of EC and EC.
以上述べたように、本発明によると、試料液に含まれる分析対象の金属元素の分散状態を維持しつつその含有量を高めるとともに、高周波誘導結合プラズマ発光分光分析法において金属成分を検出可能な濃度にまで有機溶媒量を低減させ、プラズマの失火や不安定化を抑えて測定精度を向上させることができる。 As described above, according to the present invention, while maintaining the dispersion state of the metal element to be analyzed contained in the sample solution, the content thereof can be increased, and the metal component can be detected in the high frequency inductively coupled plasma emission spectrometry. The amount of organic solvent can be reduced to the concentration, and plasma misfire and instability can be suppressed to improve measurement accuracy.
以下、本発明の実施形態について具体的に説明する。以下の好ましい実施形態の説明は、本質的に例示に過ぎず、本発明、その適用物或いはその用途を制限することを意図するものでは全くない。 Hereinafter, embodiments of the present invention will be specifically described. The following description of the preferred embodiments is merely exemplary in nature and is in no way intended to limit the invention, its application, or its application.
<溶液について>
ICP分析対象の溶液は、分析対象の金属元素等を含み、有機溶媒を溶媒の一部又は全部とする溶液を使用することができる。具体的には例えば、Liイオン二次電池用の電解液、電気二重層キャパシタ用電解液、リチウムイオンキャパシタ用電解液、リチウムポリマー電池用電解液などが挙げられる。
<About the solution>
As the ICP analysis target solution, a solution containing a metal element or the like to be analyzed and using an organic solvent as a part or all of the solvent can be used. Specific examples include electrolytes for Li ion secondary batteries, electrolytes for electric double layer capacitors, electrolytes for lithium ion capacitors, electrolytes for lithium polymer batteries, and the like.
溶液に含まれる有機溶媒は、Liイオン二次電池用の電解液等に一般的に用いられる有機溶媒を使用することができる。具体的には例えば、ジメチルカーボネート(DMC)、ジエチルカーボネート(DEC)、エチルメチルカーボネート(EMC)、プロピレンカーボネート(PC)、エチレンカーボネート(EC)等の炭酸エステル、アセトニトリル、ベンゾニトリル、塩化メチレン、テトラヒドロフラン、ジメチルホルムアミド、ジメチルスルホキシド等が挙げられる。これらは一種でも二種以上の混合溶媒であってもよい。 As the organic solvent contained in the solution, an organic solvent generally used for an electrolyte solution for a Li ion secondary battery or the like can be used. Specifically, for example, carbonates such as dimethyl carbonate (DMC), diethyl carbonate (DEC), ethyl methyl carbonate (EMC), propylene carbonate (PC), ethylene carbonate (EC), acetonitrile, benzonitrile, methylene chloride, tetrahydrofuran , Dimethylformamide, dimethyl sulfoxide and the like. These may be one kind or a mixed solvent of two or more kinds.
分析対象の金属元素は、上記電解液等に含まれる一般的な金属元素であってよい。具体的には例えば、電解質や正極材料としてリチウムイオン二次電池等に含まれるLi、Mn、Ni、Co、Al等、その他Na、Mg、Ca、Zn、Cu、Fe、Zr、Ti等である。これにより、例えばLiイオン二次電池の劣化状態等を精度よく調べることができる。 The metal element to be analyzed may be a general metal element contained in the electrolytic solution or the like. Specifically, for example, Li, Mn, Ni, Co, Al, etc. included in the lithium ion secondary battery as an electrolyte or positive electrode material, and other Na, Mg, Ca, Zn, Cu, Fe, Zr, Ti, etc. . Thereby, for example, the deterioration state of the Li ion secondary battery can be examined with high accuracy.
<ICP分析用試料液の調製方法>
以下、ICP分析によりLiイオン二次電池用電解液中の金属元素の含有量を測定する場合を例に、本実施形態に係る試料液の調製方法を説明する。
<Preparation method of sample solution for ICP analysis>
Hereinafter, the method for preparing the sample solution according to the present embodiment will be described by taking as an example the case of measuring the content of the metal element in the electrolyte solution for Li ion secondary battery by ICP analysis.
(希釈工程)
有機溶媒1を含むLiイオン二次電池の電解液2(溶液)に含まれる金属元素の含有量を測定する場合には、以下の工程によりICP分析用試料液を調製する。
(Dilution process)
When measuring the content of the metal element contained in the electrolyte solution 2 (solution) of the Li ion secondary battery containing the organic solvent 1, a sample solution for ICP analysis is prepared by the following steps.
まず、予め容器に希釈溶媒として所定量の水3を入れておく。次に、Liイオン二次電池に使用されていた電解液2を取り出し、図1に示すように、その電解液2の一定量を電子天秤やマイクロシリンジ等で秤量する(S1)。そして、上記秤量した電解液2の一定量を上記所定量の水3を入れた容器に添加して希釈液4を作製する(S2)。
First, a predetermined amount of water 3 is previously placed in a container as a diluent solvent. Next, the
ここに、電解液2の電解質の濃度は、一般的なLiイオン二次電池に用いられる濃度であり、好ましくは0.1mol/L以上2.0mol/L以下、より好ましくは0.3mol/L以上1.7mol/L以下、特に好ましくは0.5mol/L以上1.5mol/L以下である。
Here, the concentration of the electrolyte of the
そして、水3の添加量は、分析対象の電解液2中の金属元素の分散状態を維持するとともにその含有量を高める観点から、上記電解液2の一部に含まれる上記有機溶媒量の体積比で20倍超100倍未満、好ましくは25倍以上90倍以下、特に好ましくは30倍以上80倍以下である。
And the addition amount of the water 3 is the volume of the amount of the organic solvent contained in a part of the
また、換言すると、上記希釈液中の有機溶媒の上記水に対する濃度は、好ましくは0.13mol/L超0.57mol/L未満、好ましくは0.14mol/L以上0.50mol/L以下、特に好ましくは0.15mol/L以上0.45mol/L以下である。 In other words, the concentration of the organic solvent in the diluent with respect to the water is preferably more than 0.13 mol / L and less than 0.57 mol / L, preferably 0.14 mol / L or more and 0.50 mol / L or less, particularly Preferably they are 0.15 mol / L or more and 0.45 mol / L or less.
(気化工程)
次に、上記希釈液4を、希釈液4に含まれる水3が所定の気化速度を維持して気化し得る条件下に置く(S3)。具体的には、水3の気化速度を維持することができればいかなる手段をとってもよいが、例えば電解液2を秤量して入れた容器として、蓋又は栓を備えた容器を用い、蓋又は栓をして、大気中、又はAr、N2等の不活性ガス下に放置する。
(Vaporization process)
Next, the diluent 4 is placed under conditions that allow the water 3 contained in the diluent 4 to vaporize while maintaining a predetermined vaporization rate (S3). Specifically, any means can be used as long as the vaporization rate of the water 3 can be maintained. For example, a container having a lid or a stopper is used as a container in which the
温度は、分析対象の電解液2中の金属元素の分散状態を維持しつつ、水分量の過度の減少を抑えるとともに有機溶媒1の含有量を効果的に低減させる観点から、好ましくは10℃〜40℃、より好ましくは15℃〜35℃、特に好ましくは20℃〜30℃である。
The temperature is preferably 10 ° C. to from the viewpoint of effectively suppressing the content of the organic solvent 1 while suppressing the excessive decrease in the water content while maintaining the dispersion state of the metal element in the
また、放置日数(気化させる時間)は、分析対象の電解液2中の金属元素の分散状態を維持しつつ、水分量の過度の減少を抑えるとともに有機溶媒1の含有量を効果的に低減させる観点から、好ましくは1日以上14日以内、より好ましくは1日以上12日以内、特に好ましくは2日以上10日以内である。
In addition, the number of days to be left (vaporization time) suppresses an excessive decrease in the amount of moisture while effectively reducing the content of the organic solvent 1 while maintaining the dispersion state of the metal element in the
希釈液4からの水の気化速度は、分析対象の電解液2中の金属元素の分散状態を維持しつつ、水分量の過度の減少を抑えるとともに有機溶媒1の含有量を効果的に低減させる観点から、好ましくは5.0mg/日以上10.0mg/日以下、より好ましくは6.0mg/日以上9.0mg/日以下、特に好ましくは7.0mg/日以上8.0mg/日である。
The evaporation rate of water from the diluent 4 suppresses an excessive decrease in the amount of water and effectively reduces the content of the organic solvent 1 while maintaining the dispersion state of the metal element in the
このように、有機溶媒1と水3とを含む混合溶液において、有機溶媒1の気化が進み、有機溶媒1の含有量が低減されるのは、水は不燃性液体であるのに対し、有機溶媒は揮発性の可燃性液体であるから、水よりも早く気化するためと考えられる。表1に後述する実施例において使用した有機溶媒の種類と沸点及び引火点を示す。 As described above, in the mixed solution containing the organic solvent 1 and the water 3, the vaporization of the organic solvent 1 proceeds and the content of the organic solvent 1 is reduced because water is an incombustible liquid, but organic Since the solvent is a volatile flammable liquid, it is thought to vaporize faster than water. Table 1 shows the types, boiling points, and flash points of organic solvents used in Examples described later.
表1に示すように、有機溶媒の沸点は水の沸点と同程度か又はそれ以上の温度であるが、引火点は水の沸点よりも低いか、又は水の沸点より高いとしても有機溶媒の沸点に比べて大幅に低い温度となっている。これにより、上述したような温度で希釈液4を放置しても、有機溶媒の気化が進み、その含有量が低減されると考えられる。 As shown in Table 1, the boiling point of the organic solvent is the same as or higher than the boiling point of water, but the flash point is lower than the boiling point of water or higher than the boiling point of water. The temperature is significantly lower than the boiling point. Thereby, even if the diluent 4 is allowed to stand at the temperature as described above, the vaporization of the organic solvent proceeds and the content thereof is considered to be reduced.
試料液5中の有機溶媒1の水3に対する濃度は、できる限り低減されることが望ましく、具体的には、好ましくは0.18mol/L未満、より好ましくは0.001mol/L以上0.18mol/L未満、特に好ましくは0.01mol/L以上0.17mol/L以下である。これにより、試料液5に含まれる分析対象の金属元素の含有量を高めるとともに、有機溶媒1の含有量を低減させてプラズマの失火や不安定化を抑えて、測定精度を向上させることができる。 The concentration of the organic solvent 1 in the sample solution 5 with respect to the water 3 is desirably reduced as much as possible. Specifically, it is preferably less than 0.18 mol / L, more preferably 0.001 mol / L or more and 0.18 mol. / L, particularly preferably 0.01 mol / L or more and 0.17 mol / L or less. As a result, the content of the metal element to be analyzed contained in the sample liquid 5 can be increased, and the content of the organic solvent 1 can be reduced to suppress plasma misfire and instability, thereby improving measurement accuracy. .
<ICP分析について>
ICP分析には、市販の測定器を使用することができる。検量線法を用い、分析対象の金属元素の含有量を測定する。
<About ICP analysis>
A commercially available measuring instrument can be used for ICP analysis. Using the calibration curve method, the content of the metal element to be analyzed is measured.
本実施形態に係る試料液の調製方法によれば、試料液5に含まれる分析対象の金属元素の分散状態を維持しつつその含有量を高めるとともに、高周波誘導結合プラズマ発光分光分析法において金属元素を検出可能な濃度にまで有機溶媒1の含有量を低減させ、プラズマの失火や不安定化を抑えて測定精度を向上させることができる。 According to the method for preparing a sample solution according to the present embodiment, the content of the metal element to be analyzed contained in the sample solution 5 is increased while maintaining the dispersion state, and the metal element is used in the high frequency inductively coupled plasma emission spectrometry. Thus, the content of the organic solvent 1 can be reduced to a concentration at which it can be detected, and plasma misfire and instability can be suppressed to improve measurement accuracy.
実施例、比較例及び参考例において使用した有機溶媒を上述の表1に示す。 The organic solvents used in Examples, Comparative Examples and Reference Examples are shown in Table 1 above.
<参考例について>
参考例1〜7は、有機溶媒DMCについて、電解質を添加することなく、上記希釈液及び試料液に相当するサンプルを調製し、そのICP測定可否について検討したものである。条件及び結果を表2に示す。
<Reference examples>
In Reference Examples 1 to 7, samples corresponding to the diluted solution and the sample solution were prepared for the organic solvent DMC without adding an electrolyte, and the possibility of ICP measurement was examined. The conditions and results are shown in Table 2.
[参考例1]
まず、蓋付のポリエチレン製の容器を準備し、イオン交換水20mLを入れた。そして、表2に示すように、DMC0.050mLをマイクロシリンジを用いて計り取り、容器に入れて希釈液を作製した。そして、この希釈液について、後述するICP測定の可否を検討した。
[Reference Example 1]
First, a polyethylene container with a lid was prepared, and 20 mL of ion-exchanged water was added. And as shown in Table 2, 0.050 mL of DMC was measured using the micro syringe, and it put into the container and produced the dilution liquid. And about this dilution liquid, the possibility of the ICP measurement mentioned later was examined.
[参考例2]
DMC量を0.10mLとした以外は参考例1と同様にサンプル調製及び検討を行った。
[Reference Example 2]
Sample preparation and examination were performed in the same manner as in Reference Example 1 except that the amount of DMC was changed to 0.10 mL.
[参考例3]
DMC量を0.20mLとした以外は参考例1と同様にサンプル調製及び検討を行った。
[Reference Example 3]
Sample preparation and examination were performed in the same manner as in Reference Example 1 except that the amount of DMC was 0.20 mL.
[参考例4]
まず、蓋付のポリエチレン製の容器を準備し、イオン交換水20mLを入れた。そして、表2に示すように、DMC0.30mLをマイクロシリンジを用いて計り取り、容器に入れて希釈液を作製した。そして、この希釈液について、ICP測定の可否を検討した。
[Reference Example 4]
First, a polyethylene container with a lid was prepared, and 20 mL of ion-exchanged water was added. And as shown in Table 2, DMC0.30mL was measured using the micro syringe, and it put into the container and produced the dilution liquid. And about this dilution liquid, the possibility of ICP measurement was examined.
そして、希釈液を入れた容器の蓋を閉め、大気中に放置し、放置開始から14日目まで、毎日ICP測定可否を検討した。 And the lid | cover of the container which put the dilution liquid was closed, and it was left to stand in air | atmosphere, and it was examined whether ICP measurement was possible every day from the start of leaving to 14th day.
[参考例5]
DMC量を0.40mLとした以外は参考例4と同様にサンプル調製及び検討を行った。
[Reference Example 5]
Sample preparation and examination were performed in the same manner as in Reference Example 4 except that the amount of DMC was 0.40 mL.
[参考例6]
DMC量を0.50mLとした以外は参考例4と同様にサンプル調製及び検討を行った。
[Reference Example 6]
Sample preparation and examination were performed in the same manner as in Reference Example 4 except that the amount of DMC was 0.50 mL.
[参考例7]
DMC量を1.0mLとした以外は参考例4と同様にサンプル調製及び検討を行った。
[Reference Example 7]
Sample preparation and examination were performed in the same manner as in Reference Example 4 except that the amount of DMC was 1.0 mL.
<実施例及び比較例について>
次に、実施例1〜9及び比較例1〜3について、条件及び結果を表3に示す。
<Examples and Comparative Examples>
Next, conditions and results are shown in Table 3 for Examples 1 to 9 and Comparative Examples 1 to 3.
[実施例1]
測定試料として、ジエチルカーボネート(DEC)と、エチレンカーボネート(EC)とを3:7で混合させた有機溶媒に六フッ化リン酸リチウム(LiPF6)を1mol/Lの濃度となるように溶解させた電解液Aを用いた。また、微量金属元素の検出が可能であるか否かを確かめるため、イオン交換水に微量の金属元素として硝酸ニッケル六水和物(Ni(NO3)2・6H2O)をNiイオンの濃度が0.001mol/Lの濃度となるように溶解させた水溶液Bを準備した。なお、硝酸ニッケル六水和物(Ni(NO3)2・6H2O)を水溶液の形で準備したのは、溶解性を考慮したものである。
[Example 1]
As a measurement sample, lithium hexafluorophosphate (LiPF 6 ) was dissolved in an organic solvent in which diethyl carbonate (DEC) and ethylene carbonate (EC) were mixed at 3: 7 so as to have a concentration of 1 mol / L. The electrolytic solution A was used. Further, in order to confirm whether or not a trace metal element can be detected, nickel nitrate hexahydrate (Ni (NO 3 ) 2 .6H 2 O) is added as a trace metal element to ion-exchanged water. Aqueous solution B was prepared so as to have a concentration of 0.001 mol / L. In addition, the nickel nitrate hexahydrate (Ni (NO 3 ) 2 · 6H 2 O) was prepared in the form of an aqueous solution in consideration of solubility.
蓋付のポリエチレン製の容器を準備し、イオン交換水19.7mLを入れた。そして、表3に示すように、電解液A0.30mLと水溶液B0.30mLとを各々マイクロシリンジを用いて計り取り、容器に添加して希釈液を作製した。そして、この希釈液について、ICP測定の可否を検討した。 A polyethylene container with a lid was prepared, and 19.7 mL of ion-exchanged water was added. And as shown in Table 3, each electrolyte solution A0.30mL and aqueous solution B0.30mL were measured using the micro syringe, and it added to the container, and produced the dilution liquid. And about this dilution liquid, the possibility of ICP measurement was examined.
次に、希釈液を入れた容器の蓋を閉め、大気中に放置して8日目に、ICP測定可否を検討した。 Next, the lid of the container containing the diluted solution was closed and left in the atmosphere, and whether or not ICP measurement was possible was examined on the 8th day.
また、ICP測定可能な場合には、Li及びNi濃度(ppm)を測定した。 When ICP measurement was possible, Li and Ni concentrations (ppm) were measured.
[実施例2]
電解液A量を0.40mL、水溶液B量を0.40mL、イオン交換水量を19.6mLとした以外は、実施例1と同様に調製及び検討を行った。
[Example 2]
Preparation and examination were performed in the same manner as in Example 1 except that the amount of electrolytic solution A was 0.40 mL, the amount of aqueous solution B was 0.40 mL, and the amount of ion-exchanged water was 19.6 mL.
[実施例3]
電解液A量を0.50mL、水溶液B量を0.50mL、イオン交換水量を19.5mLとした以外は、実施例1と同様に調製及び検討を行った。
[Example 3]
Preparation and examination were performed in the same manner as in Example 1 except that the amount of electrolytic solution A was 0.50 mL, the amount of aqueous solution B was 0.50 mL, and the amount of ion-exchanged water was 19.5 mL.
[実施例4]
電解液A量を0.75mL、水溶液B量を0.75mL、イオン交換水量を29.25mLとした以外は、実施例1と同様に調製及び検討を行った。なお、大気中に放置を開始した後は、8日目に加えて12日目についてもICP測定可否を検討した。
[Example 4]
Preparation and examination were performed in the same manner as in Example 1 except that the amount of the electrolytic solution A was 0.75 mL, the amount of the aqueous solution B was 0.75 mL, and the amount of ion-exchanged water was 29.25 mL. After starting to stand in the atmosphere, whether or not ICP measurement was possible was examined on the 12th day in addition to the 8th day.
[実施例5]
電解液A量を1.00mL、水溶液B量を1.00mL、イオン交換水量を29.0mLとした以外は、実施例1と同様に調製及び検討を行った。なお、大気中に放置を開始した後は、8日目に加えて12日目についてもICP測定可否を検討した。
[Example 5]
Preparation and examination were performed in the same manner as in Example 1 except that the amount of electrolytic solution A was 1.00 mL, the amount of aqueous solution B was 1.00 mL, and the amount of ion-exchanged water was 29.0 mL. After starting to stand in the atmosphere, whether or not ICP measurement was possible was examined on the 12th day in addition to the 8th day.
[比較例1]
蓋付のポリエチレン製の容器を準備し、イオン交換水19.95mLを入れた。そして、表3に示すように、電解液A0.050mLと水溶液B0.050mLとを各々マイクロシリンジを用いて計り取り、容器に添加して希釈液を作製した。そして、この希釈液について、ICP測定の可否を検討した。結果としてICP測定可能であったため、Li及びNi濃度(ppm)を測定した。
[Comparative Example 1]
A polyethylene container with a lid was prepared, and 19.95 mL of ion-exchanged water was added. And as shown in Table 3, 0.050 mL of electrolyte solution A and 0.050 mL of aqueous solution B were each measured using the micro syringe, and it added to the container, and produced the dilution liquid. And about this dilution liquid, the possibility of ICP measurement was examined. Since ICP measurement was possible as a result, Li and Ni concentrations (ppm) were measured.
[比較例2]
電解液A量を0.10mL、水溶液B量を0.10mL、イオン交換水量を19.9mLとした以外は、比較例1と同様に調製及び検討を行った。
[Comparative Example 2]
Preparation and examination were performed in the same manner as in Comparative Example 1 except that the amount of electrolytic solution A was 0.10 mL, the amount of aqueous solution B was 0.10 mL, and the amount of ion-exchanged water was 19.9 mL.
[比較例3]
電解液A量を0.20mL、水溶液B量を0.20mL、イオン交換水量を19.8mLとした以外は、比較例1と同様に調製及び検討を行った。
[Comparative Example 3]
Preparation and examination were performed in the same manner as in Comparative Example 1 except that the amount of electrolytic solution A was 0.20 mL, the amount of aqueous solution B was 0.20 mL, and the amount of ion-exchanged water was 19.8 mL.
[実施例6]
測定試料として、ジメチルカーボネート(DMC)と、エチレンカーボネート(EC)とを3:7で混合させた有機溶媒に六フッ化リン酸リチウム(LiPF6)を1mol/Lの濃度となるように溶解させた電解液Aを用いた。また、イオン交換水に微量の金属元素として硝酸ニッケル六水和物(Ni(NO3)2・6H2O)をNiイオンの濃度が0.001mol/Lの濃度となるように溶解させた水溶液Bを準備した。
[Example 6]
As a measurement sample, lithium hexafluorophosphate (LiPF 6 ) was dissolved in an organic solvent in which dimethyl carbonate (DMC) and ethylene carbonate (EC) were mixed at 3: 7 so as to have a concentration of 1 mol / L. The electrolytic solution A was used. In addition, an aqueous solution in which nickel nitrate hexahydrate (Ni (NO 3 ) 2 .6H 2 O) is dissolved in ion exchange water as a trace amount of metal element so that the concentration of Ni ions is 0.001 mol / L. B was prepared.
蓋付のポリエチレン製の容器を準備し、イオン交換水19.5mLを入れた。そして、表3に示すように、電解液0.50mLと水溶液B0.50mLとを各々マイクロシリンジを用いて計り取り、容器に添加して希釈液を作製した。そして、この希釈液について、ICP測定の可否を検討した。 A polyethylene container with a lid was prepared, and 19.5 mL of ion-exchanged water was added. And as shown in Table 3, 0.50 mL of electrolyte solution and 0.50 mL of aqueous solution B were each measured using the micro syringe, and it added to the container, and produced the dilution liquid. And about this dilution liquid, the possibility of ICP measurement was examined.
次に、希釈液を入れた容器の蓋を閉め、大気中に放置して8日目に、ICP測定可否を検討した。 Next, the lid of the container containing the diluted solution was closed and left in the atmosphere, and whether or not ICP measurement was possible was examined on the 8th day.
また、ICP測定可能な場合には、Li及びNi濃度(ppm)を測定した。 When ICP measurement was possible, Li and Ni concentrations (ppm) were measured.
[実施例7]
電解液A量を1.25mL、水溶液B量を1.25mL、イオン交換水量を48.75mLとした以外は、実施例6と同様に調製及び検討を行った。
[Example 7]
Preparation and examination were performed in the same manner as in Example 6 except that the amount of electrolytic solution A was 1.25 mL, the amount of aqueous solution B was 1.25 mL, and the amount of ion-exchanged water was 48.75 mL.
[実施例8]
電解液A量を0.30mL、水溶液B量を0.30mL、イオン交換水量を19.7mLとした以外は、実施例6と同様に調製及び検討を行った。
[Example 8]
Preparation and examination were performed in the same manner as in Example 6 except that the amount of electrolytic solution A was 0.30 mL, the amount of aqueous solution B was 0.30 mL, and the amount of ion-exchanged water was 19.7 mL.
[実施例9]
電解液A量を0.45mL、水溶液B量を0.45mL、イオン交換水量を29.55mLとした以外は、実施例6と同様に調製及び検討を行った。
[Example 9]
Preparation and examination were performed in the same manner as in Example 6 except that the amount of electrolytic solution A was 0.45 mL, the amount of aqueous solution B was 0.45 mL, and the amount of ion-exchanged water was 29.55 mL.
<ICP測定について>
ICP発光分光分析装置(ICP−S8100、島津製作所製)を用いて、ICP測定を行った。なお、測定条件、検量線溶液の作製方法は以下の通りである。
<About ICP measurement>
ICP measurement was performed using an ICP emission spectroscopic analyzer (ICP-S8100, manufactured by Shimadzu Corporation). The measurement conditions and the calibration curve solution preparation method are as follows.
すなわち、測定条件は、高周波出力 :1.6kW、観測高さ:15cm、積分時間 :15秒×3、アルゴンガス量:冷却用16L/分、補助1.5L/分、キャリア0.7L/分、定量法:検量線法、分析波長:610.365nm(Li)、222.295nm(Ni)であった。 That is, the measurement conditions were: high frequency output: 1.6 kW, observation height: 15 cm, integration time: 15 seconds × 3, argon gas amount: 16 L / min for cooling, auxiliary 1.5 L / min, carrier 0.7 L / min Quantitative method: calibration curve method, analysis wavelength: 610.365 nm (Li), 222.295 nm (Ni).
また、検量線溶液は、以下の手順で調製した。まず、Li及びNiともに市販のICP分析用の標準液(10000μg/mL)を用い、0〜10ppmの範囲で濃度が段階的となるよう、所定量計り取ってメスフラスコに入れ、イオン交換水で100mLにメスアップして調製した。 A calibration curve solution was prepared by the following procedure. First, for both Li and Ni, a commercially available standard solution for ICP analysis (10000 μg / mL) was used, and a predetermined amount was measured so that the concentration would be stepwise in the range of 0 to 10 ppm. Prepared by measuring up to 100 mL.
上記検量線溶液の、ICP発光分光分析装置による測定結果に基づいて得られた、Li濃度及びNi濃度(単位:ppm)と、ICP測定による発光強度との関係をプロットすると、得られた検量線の相関係数Rは、いずれも0.999であり、良好な直線性を有する結果が得られた。 When the relationship between the Li concentration and Ni concentration (unit: ppm) obtained based on the measurement result of the calibration curve solution by the ICP emission spectroscopic analyzer and the emission intensity by ICP measurement is plotted, the obtained calibration curve is obtained. The correlation coefficient R of each was 0.999, and a result having good linearity was obtained.
参考例1〜7では、電解質を添加していないため、ICP測定が行えるかどうか、すなわちプラズマの失火や不安定化が起こることなくブランク測定可能かどうかを確認し、ICP測定可否の検討とした。 In Reference Examples 1 to 7, since no electrolyte was added, it was confirmed whether or not ICP measurement can be performed, that is, whether or not blank measurement is possible without causing plasma misfire or instability. .
実施例1〜9及び比較例1〜3では、プラズマの失火や不安定化が起こることなくICP測定が行えるかどうかを確認し、試料液のLi及びNi濃度(ppm)を測定した。 In Examples 1 to 9 and Comparative Examples 1 to 3, it was confirmed whether ICP measurement could be performed without causing plasma misfire or instability, and the Li and Ni concentrations (ppm) of the sample solution were measured.
<水の気化速度について>
上記参考例、実施例、及び比較例において使用した、蓋付ポリエチレン製容器について、蓋をして大気中に放置したときの1日ごとの水の気化量を検討した。
<About the vaporization speed of water>
Regarding the lidded polyethylene containers used in the above Reference Examples, Examples, and Comparative Examples, the amount of water vaporized per day when the containers were covered and left in the atmosphere was examined.
具体的には、容器中に20gの水を入れ、蓋をして大気中に放置し、1日ごとに全重量を秤量して0日目の全重量との重量差(mg)を算出した。結果を図2に示す。 Specifically, 20 g of water was put in a container, covered with a lid, left in the atmosphere, the total weight was weighed every day, and the weight difference (mg) from the total weight on the 0th day was calculated. . The results are shown in FIG.
図2から、水の気化速度(mg/日)は、7.4mg/日であった。 From FIG. 2, the water vaporization rate (mg / day) was 7.4 mg / day.
<考察>
表2に示すように、参考例1〜3において、希釈液のICP測定可否を検討すると、0日目(即日)においてICP測定は可能であった。
<Discussion>
As shown in Table 2, in Reference Examples 1 to 3, the ICP measurement was possible on the 0th day (the same day) when the ICP measurement of the diluted solution was examined.
これに対し、参考例4では2日目以降、参考例5では5日目以降、参考例6では7日目以降にICP測定可能となった。また、参考例7では、14日以内ではICP測定は不可能であった。 On the other hand, in Reference Example 4, ICP measurement can be performed after the second day, in Reference Example 5 from the fifth day, and in Reference Example 6, from the seventh day. In Reference Example 7, ICP measurement was impossible within 14 days.
以上より、参考例1〜3に示す、水に対するDMC濃度ではICPのプラズマに影響を与えず、測定可能であることが分かった。また、参考例4〜6に示す、水に対するDMC濃度ではDMCを気化させることにより、測定可能となることが分かった。 From the above, it was found that the DMC concentration in water shown in Reference Examples 1 to 3 can be measured without affecting the plasma of ICP. Moreover, it turned out that it becomes measurable by vaporizing DMC in the DMC density | concentration with respect to water shown to the reference examples 4-6.
次に、表3に示すように、比較例1〜3において、希釈液のICP測定可否を検討すると、0日目(即日)においてICP測定は可能であった。 Next, as shown in Table 3, in Comparative Examples 1 to 3, when ICP measurement of the diluted solution was examined, ICP measurement was possible on the 0th day (same day).
これに対し、実施例1〜4では8日目、実施例5では12日目にはICP測定が可能であった。また、実施例6〜9においても8日目には、ICP測定可能であった。 On the other hand, ICP measurement was possible on the 8th day in Examples 1 to 4 and on the 12th day in Example 5. In Examples 6 to 9, ICP measurement was possible on the 8th day.
比較例1〜3では、Li濃度は測定可能であったのに対し、Ni濃度についてはNiに由来するピークを確認することができなかった。 In Comparative Examples 1 to 3, although the Li concentration was measurable, no Ni-derived peak could be confirmed for the Ni concentration.
これに対し、実施例1〜9では、Ni由来のピークが確認され、Li濃度とともにNi濃度も測定可能であった。 On the other hand, in Examples 1-9, the peak derived from Ni was confirmed and Ni concentration was measurable with Li concentration.
本発明は、試料液に含まれる分析対象の金属元素の分散状態を維持しつつその含有量を高めるとともに、高周波誘導結合プラズマ発光分光分析法において金属成分を検出可能な濃度にまで有機溶媒量を低減させ、プラズマの失火や不安定化を抑えて測定精度を向上させることができるので、極めて有用である。 The present invention increases the content of a metal element to be analyzed contained in a sample solution while maintaining the dispersion state, and reduces the amount of organic solvent to a concentration at which a metal component can be detected in high frequency inductively coupled plasma emission spectrometry. The measurement accuracy can be improved by reducing the plasma misfire and instability, which is extremely useful.
1 有機溶媒
2 電解液(溶液)
3 水
4 希釈液
5 試料液
1 Organic solvent 2 Electrolytic solution (solution)
3 Water 4 Diluent 5 Sample solution
Claims (5)
上記溶液の一部を水で希釈して希釈液を得る工程と、
上記希釈液中の有機溶媒を気化させて上記試料液を得る工程と
を備え、
上記希釈液中の有機溶媒の上記水に対する濃度は、0.13mol/L超0.57mol/L未満であり、
上記試料液中の有機溶媒の上記水に対する濃度は、0.18mol/L未満であり、
上記希釈液中の有機溶媒を気化させる時間は、1日以上14日以内である
ことを特徴とする試料液の調製方法。 A method for preparing a sample solution for detecting the content of a metal element contained in a solution containing an organic solvent using a high-frequency inductively coupled plasma emission spectroscopy method,
Diluting a part of the solution with water to obtain a diluted solution;
Evaporating the organic solvent in the diluted solution to obtain the sample solution,
The concentration of the organic solvent in the diluent with respect to the water is more than 0.13 mol / L and less than 0.57 mol / L,
Concentration for the aqueous organic solvent of the sample solution is state, and are less than 0.18 mol / L,
The method for preparing a sample solution, wherein the time for vaporizing the organic solvent in the diluted solution is 1 day or more and 14 days or less .
上記試料液を得る工程では、上記希釈液に含まれる水が所定の気化速度を維持して気化する条件下で、上記希釈液中の有機溶媒を気化させるものであるIn the step of obtaining the sample solution, the organic solvent in the diluent is vaporized under the condition that water contained in the diluent is vaporized while maintaining a predetermined vaporization rate.
ことを特徴とする試料液の調製方法。A method for preparing a sample solution.
上記試料液を得る工程では、上記希釈液からの水の気化速度が5.0mg/日以上10.0mg/日以下となる条件下で、上記希釈液中の有機溶媒を気化させる
ことを特徴とする試料液の調製方法。 In claim 2 ,
In the step of obtaining the sample solution, the organic solvent in the diluent is vaporized under a condition where the vaporization rate of water from the diluent is 5.0 mg / day to 10.0 mg / day. To prepare a sample solution.
上記溶液は、Liイオン二次電池用の電解液である
ことを特徴とする試料液の調製方法。 In any one of Claim 1 thru | or 3,
The said solution is electrolyte solution for Li ion secondary batteries, The preparation method of the sample solution characterized by the above-mentioned.
上記有機溶媒は、炭酸エステルである
ことを特徴とする試料液の調製方法。 In claim 4,
The method for preparing a sample solution, wherein the organic solvent is a carbonate ester.
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