JPH0312703B2 - - Google Patents
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- Publication number
- JPH0312703B2 JPH0312703B2 JP2588984A JP2588984A JPH0312703B2 JP H0312703 B2 JPH0312703 B2 JP H0312703B2 JP 2588984 A JP2588984 A JP 2588984A JP 2588984 A JP2588984 A JP 2588984A JP H0312703 B2 JPH0312703 B2 JP H0312703B2
- Authority
- JP
- Japan
- Prior art keywords
- measured
- sample
- ion
- ion species
- amount
- 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.)
- Expired
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Classifications
-
- G—PHYSICS
- G01—MEASURING; TESTING
- G01N—INVESTIGATING OR ANALYSING MATERIALS BY DETERMINING THEIR CHEMICAL OR PHYSICAL PROPERTIES
- G01N30/00—Investigating or analysing materials by separation into components using adsorption, absorption or similar phenomena or using ion-exchange, e.g. chromatography or field flow fractionation
- G01N30/96—Investigating or analysing materials by separation into components using adsorption, absorption or similar phenomena or using ion-exchange, e.g. chromatography or field flow fractionation using ion-exchange
-
- G—PHYSICS
- G01—MEASURING; TESTING
- G01N—INVESTIGATING OR ANALYSING MATERIALS BY DETERMINING THEIR CHEMICAL OR PHYSICAL PROPERTIES
- G01N30/00—Investigating or analysing materials by separation into components using adsorption, absorption or similar phenomena or using ion-exchange, e.g. chromatography or field flow fractionation
- G01N30/96—Investigating or analysing materials by separation into components using adsorption, absorption or similar phenomena or using ion-exchange, e.g. chromatography or field flow fractionation using ion-exchange
- G01N2030/965—Investigating or analysing materials by separation into components using adsorption, absorption or similar phenomena or using ion-exchange, e.g. chromatography or field flow fractionation using ion-exchange suppressor columns
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- Physics & Mathematics (AREA)
- Health & Medical Sciences (AREA)
- Life Sciences & Earth Sciences (AREA)
- Chemical & Material Sciences (AREA)
- Analytical Chemistry (AREA)
- Biochemistry (AREA)
- General Health & Medical Sciences (AREA)
- General Physics & Mathematics (AREA)
- Immunology (AREA)
- Pathology (AREA)
- Investigating Or Analyzing Non-Biological Materials By The Use Of Chemical Means (AREA)
- Treatment Of Liquids With Adsorbents In General (AREA)
Description
【発明の詳細な説明】
〔発明の属する分野〕
本発明は、イオンクロマトグラフイにおいて採
取された試料の量とこの試量中のイオン濃度とを
同時に測定できるようなイオン種測定方法に関す
る。DETAILED DESCRIPTION OF THE INVENTION [Field of the Invention] The present invention relates to a method for measuring ion species that can simultaneously measure the amount of a sample collected in ion chromatography and the ion concentration in this sample amount.
イオンクロマトグラフイにおける試料の採取方
法は、計量管を有するインジエクタを駆動させて
一定量の試料を移動相(溶離液)中に注入する方
法と、マイクロシリンジなどを用いて大略一定量
の試料を移動相中に注入する方法とがある。前者
においては、標準液(若しくは標準ガス)と被測
定試料とによるクロマトグラム作成を行ない、こ
の2つのクロマトグラムの保持時間が一致してい
るピークの高さ比(若しくは面積比)から被測定
試料中のイオン濃度を求める所謂絶対検量線法が
採用されることが多い。また、後者においては、
被測定試料中に一定量の内部標準物質を加えての
ちクロマトグラムを作成し、このクロマトグラム
と内部標準物質標準液物質のクロマトグラムとを
比較して試料中のイオン濃度を求める所謂内部標
準法が採用されることが多い。 然し乍ら、上記
絶対検量線法を採用した場合、試料中のイオン濃
度に対応させてクロマトグラムのピークの大きさ
を調節することが一般に困難となる欠点があつ
た。これは、ピークの大きさが上記インジエクタ
の計量管内容積に比例するのに、該計量管内容積
の増減は一般に困難だからである。また、上記内
部標準法を採用した場合には、内部標準物質を被
測定試料に正確に添加するという面倒な操作が必
要になる欠点があつた。これは、内部標準物質
は、被測定試料中に存在するイオン種と異なるも
のであつてクロマトグラム上もこれらイオン種と
完全分離するようなものでなければならないこと
に起因している。
There are two methods for collecting samples in ion chromatography: one method is to drive an injector with a measuring tube to inject a fixed amount of sample into the mobile phase (eluent), and the other is to use a microsyringe etc. to collect a roughly fixed amount of sample. There is a method of injecting into a mobile phase. In the former, a chromatogram is created using a standard solution (or standard gas) and a sample to be measured, and the sample to be measured is determined from the height ratio (or area ratio) of peaks whose retention times match in the two chromatograms. The so-called absolute calibration curve method is often adopted to determine the ion concentration in the sample. Also, in the latter case,
The so-called internal standard method involves adding a certain amount of internal standard substance to the sample to be measured, then creating a chromatogram, and comparing this chromatogram with the chromatogram of the internal standard substance standard solution substance to determine the ion concentration in the sample. is often adopted. However, when the above-mentioned absolute calibration curve method is employed, there is a drawback that it is generally difficult to adjust the size of the peak of the chromatogram in accordance with the ion concentration in the sample. This is because although the magnitude of the peak is proportional to the volume within the metering tube of the injector, it is generally difficult to increase or decrease the volume within the metering tube. Furthermore, when the internal standard method described above is adopted, there is a drawback that a troublesome operation of accurately adding the internal standard substance to the sample to be measured is required. This is because the internal standard substance must be different from the ion species present in the sample to be measured and must be completely separated from these ion species on the chromatogram.
本発明は、かかる欠点に鑑みてなされたもので
あり、その目的は、被測定試料を正確に計量する
ことなく採取された試料の量とこの試料中のイオ
ン濃度とを同時に測定できぬようなイオン種測定
方法を提供することにある。
The present invention has been made in view of these drawbacks, and its purpose is to solve the problem in which the amount of a sample to be measured and the ion concentration in the sample cannot be measured simultaneously without accurately weighing the sample to be measured. An object of the present invention is to provide a method for measuring ion species.
本発明の特徴は、イオンクロマトグラフイを用
いて被測定試料中のイオン種を測定する方法にお
いて、被測定イオン種と同一の各種イオン種およ
び水分を含む標準液を用いて、あらかじめ、水分
によるピークの面積値と標準液注入量との関係を
示す第1グラフと、前記各種イオン種のピーク面
積値とイオン量との関係を示す第2グラフとを作
成し、その後、被測定試料を用いて得られるクロ
マトグラムの水分ピークおよび各イオンピークの
夫々の面積値と前記第1および第2のグラフとか
ら、被測定試料の注入量Vと被測定イオン種のイ
オン量Wiとを求め、これらの商(Wi/V)から
前記被測定イオン種の濃度を求めるようにしたこ
とにある。
A feature of the present invention is that in a method for measuring ion species in a sample to be measured using ion chromatography, a standard solution containing the same various ion species and water as the ion species to be measured is used to A first graph showing the relationship between the peak area value and the standard solution injection amount and a second graph showing the relationship between the peak area value of the various ion species and the ion amount are created, and then, using the sample to be measured, The injection amount V of the sample to be measured and the ion amount Wi of the ion species to be measured are determined from the respective area values of the moisture peak and each ion peak of the chromatogram obtained by the method and the first and second graphs. The concentration of the ion species to be measured is determined from the quotient (Wi/V).
以下、本発明について図を用いて詳細に説明す
る。第1図は、本発明実施例の構成説明図であ
り、図中、1aは例えば濃度5mMのHNO3でな
る溶離液が貯留されている槽、2は例えばプラン
ジヤー型(若しくはダイヤフラム型又はシリンジ
型等)の送液ポンプでなり溶離液を圧送するポン
プ、3は例えば第1〜第6の接続口3a〜3fお
よび計量管3gを有し第1図の実線接続状態と破
線接続状態とが交互に切換えられるインジエク
タ、4は容離液の脈動を防止するダンパー、5お
よび6は例えば低イオン交換容量の陽イオン交換
体が充填されてなるプレカラムおよび分離カラ
ム、7は例えば導電率検出器でなる検出器、8は
検出器7からの検出信号を受けて信号処理するイ
ンテグレータ、9はプレカラム5、分離カラム
6、および検出器7を収容しこれらを所定温度
(例えば40℃)に保つ恒温槽、1bは検出器7か
ら排出される液体を収容する廃液槽である。尚、
計量管3gの内容積は、通常2mlのものが使用さ
れる(第1図の実施例の場合も2ml)が、これに
限定されるものではなく、例えば10mlや20mlで
あつてもよい。
Hereinafter, the present invention will be explained in detail using figures. FIG. 1 is an explanatory diagram of the configuration of an embodiment of the present invention. In the figure, 1a is a tank in which an eluent consisting of HNO3 with a concentration of 5mM is stored, and 2 is a plunger type (or diaphragm type or syringe type). etc.), which pumps the eluent under pressure, 3 has, for example, first to sixth connection ports 3a to 3f and a metering tube 3g, and the solid line connection state and the broken line connection state in FIG. 1 are alternately connected. 4 is a damper that prevents pulsation of the eluent; 5 and 6 are a pre-column and a separation column filled with, for example, a cation exchanger with a low ion exchange capacity; and 7 is, for example, a conductivity detector. Detector; 8 is an integrator that receives a detection signal from the detector 7 and processes the signal; 9 is a thermostat that houses the precolumn 5, the separation column 6, and the detector 7 and keeps them at a predetermined temperature (for example, 40°C); 1b is a waste liquid tank that accommodates the liquid discharged from the detector 7. still,
The internal volume of the measuring tube 3g is usually 2 ml (also 2 ml in the embodiment shown in FIG. 1), but is not limited to this, and may be, for example, 10 ml or 20 ml.
以下、上記構成からなる本発明実施例の動作に
ついて説明する。第1図において、、ポンプ2が
駆動すると、槽1a内の溶離液は、ポンプ2→ダ
ンパー4→インジエクタ3の第1および第2接続
口3a,3b→プレカラム5→分離カラム6→検
出器7→廃液槽1bの流路で流れる。また、Li+
0.1ppm,Na+0.5ppm,NH4 +0.5ppm、およびK+
1ppmを含む溶液(以下標準液」という)を200μl
だけマイクロシリンジで正確に計量し、インジエ
クタ3の第4接続口3dから計量管3g内に注入
する。この状態で、インジエクタ3をオンにする
と、インジエクタ3の内部流路は、第1図の実線
状態から破線状態に切換わる。このため、ダンパ
ー4を経由した溶離液は、インジエクタ3の第1
接続口3a→第6接続口3f→計量管3g→第3
接続口3c→第2接続口3b→プレカラム5の流
路で流れる。従つて、計量管3g内に注入されて
いた上記標準液は、溶離液によつてプレカラム5
に搬入されるようになる。この標準液は、プレカ
ラム5および分離カラム6で含有イオン種が所定
の分離を受け、その後、検出器7に到達して、そ
の導電率が検出される。。この検出器7から出力
される検出信号は、インテグレータ8に導びかれ
て所定の信号処理を受け、第2図に示すようなク
ロマトグラムと積分値等を与える。次に、上記標
準液を1000μlだけマイクロシリンジで正確に計量
し、インジエクタ3に注入して同様の操作を行な
うと、第3図に示すようなクロマトグラムと積分
値等が得られる。第2図および第3図において、
クロマトグラムの各ピークは導電率が減少する方
向に出ており、最初のピークが水分によるピーク
(所謂ウオータデイツプ)である。このウオータ
デイツプは、標準液の注入量が増加すると飽和す
ることが多い。また、クロマトグラムのベースラ
インを示している導電率の絶対値は約2400μs/cm
である。同様にして、、上記標準液が100μl,
500μl、および2000μlの各場合についてクロマト
グラムと積分値等を得る。このようにして得られ
た積分値等に基ずいて、上記インジエクタ3への
標準液注入量(μl)とウオータデイツプの面積値
(1面積カウントを0.125μV・secとする)との関
係をプロツトすると第4図が得られる。この第4
図から、上記標準液注入量とウオータデイツプ面
積値との間には比例関係があることが分り、試料
注入量(標準液注入量)をVとし、ウオータデイ
ツプ面積値をAwdとすると、下式(1)が成立する。 The operation of the embodiment of the present invention having the above configuration will be described below. In FIG. 1, when the pump 2 is driven, the eluent in the tank 1a flows from the pump 2 to the damper 4 to the first and second connection ports 3a and 3b of the injector 3 to the precolumn 5 to the separation column 6 to the detector 7. →Flows through the flow path of the waste liquid tank 1b. Also, Li +
0.1ppm, Na + 0.5ppm, NH 4 + 0.5ppm, and K +
200μl of a solution containing 1ppm (hereinafter referred to as standard solution)
accurately measure the amount using a microsyringe, and inject it into the measuring tube 3g from the fourth connection port 3d of the injector 3. When the injector 3 is turned on in this state, the internal flow path of the injector 3 switches from the solid line state in FIG. 1 to the broken line state. Therefore, the eluent that has passed through the damper 4 is transferred to the first injector 3.
Connection port 3a → 6th connection port 3f → Measuring tube 3g → 3rd
It flows through the flow path from the connection port 3c to the second connection port 3b to the precolumn 5. Therefore, the standard solution injected into the measuring tube 3g is transferred to the precolumn 5 by the eluent.
It began to be imported into The ionic species contained in this standard solution undergo predetermined separation in the precolumn 5 and the separation column 6, and then reach the detector 7, where its conductivity is detected. . The detection signal outputted from the detector 7 is guided to an integrator 8 and subjected to predetermined signal processing to provide a chromatogram, an integral value, etc. as shown in FIG. Next, by accurately measuring 1000 μl of the above standard solution using a microsyringe, injecting it into the injector 3, and performing the same operation, a chromatogram and integral values as shown in FIG. 3 are obtained. In Figures 2 and 3,
Each peak in the chromatogram appears in the direction of decreasing conductivity, and the first peak is a peak due to water (so-called water dip). This water dip often becomes saturated as the amount of standard solution injected increases. Additionally, the absolute value of conductivity, which indicates the baseline of the chromatogram, is approximately 2400 μs/cm.
It is. Similarly, 100 μl of the above standard solution,
Obtain chromatograms and integral values for each case of 500 μl and 2000 μl. Based on the integral value etc. obtained in this way, the relationship between the amount of standard solution injected into the injector 3 (μl) and the area value of the water dip (one area count is 0.125μV・sec) is plotted. Figure 4 is obtained. This fourth
From the figure, it can be seen that there is a proportional relationship between the standard solution injection amount and the water dip area value, and if the sample injection amount (standard solution injection amount) is V and the water dip area value is Awd, the following formula (1 ) holds true.
V=4.9×10-6×Awd ……(1)
一方、第2図や第3図のようにして得られたク
ロマトグラム等から、Li+,NH4+,Na+,およ
びK+に関して各イオン量(ng)に対するピーク
面積値をプロツトすると、第5図が得られる。こ
の第5図から、上記各イオン種(ng)とピーク
面積値(1面積カウント0.125μV・sec)との間
には比例関係があることが分る。また、Li+,
NH4+,Na+,およびK+のイオン量を夫々WLi+,
WNH4+,WNa+,およびWK+とし、Li+,
NH4+,Na+,およびK+のピーク面積値を夫々
AL1+,ANH4+,ANa+,およびAK+とすると、第
5図から下式(2)〜(5)が導びき出される。 V=4.9×10 -6 ×Awd...(1) On the other hand, from the chromatograms obtained as shown in Figures 2 and 3, each of Li + , NH 4+ , Na + , and K + When the peak area value is plotted against the ion amount (ng), FIG. 5 is obtained. From FIG. 5, it can be seen that there is a proportional relationship between each of the ion species (ng) and the peak area value (one area count 0.125 μV·sec). Also, Li + ,
The ion amounts of NH 4+ , Na + , and K + were determined as W Li + , respectively.
Let W NH4 +, W Na +, and W K +, Li+,
The peak area values of NH 4+ , Na + , and K + are
Assuming A L1 +, A NH4 +, A Na +, and A K+ , the following equations (2) to (5) can be derived from FIG.
WLi+=2.44×10-4×ALi+ ……(2)
WNa+=8.13×10-4×ANa+ ……(3)
WNH4+=6.71×10-4×ANH4+ ……(4)
WK+=1.49×10-3×AK+ ……(5)
従つて、第2図や第3図に示したようなクロマ
トグラム等を、被測定試料の場合について作成す
ると、ウオータデイツプの面積値と上記第(1)式
(即ち第2図)から被測定試料の注入量を知るこ
とができる。また、このクロマトグラム等におけ
る各イオンのピーク面積値と上記第(2)式〜第(5)式
(即ち第3図)から各イオンのイオン量を知るこ
とができる。更に、上記第(2)式〜第(5)式を夫々上
記第(1)式で割つた値(商)が各イオンのイオン濃
度〔ng/μl=ppm〕となる。このため、L+,
Na+,NH4 +,およびK+イオンの各イオン濃度値
を夫々CLi+,CNa+,CNH4+,およびCK+とする
と、下式(6)〜(9)が成立し、この式から被測定試料
中の各イオン濃度が容易に求められるようにな
る。 W Li +=2.44×10 -4 ×A Li + …(2) W Na +=8.13×10 -4 ×A Na + …(3) W NH4 +=6.71×10 -4 ×A NH4 + … …(4) W K+ =1.49×10 -3 ×A K+ …(5) Therefore, if a chromatogram, etc. as shown in Figures 2 and 3 is created for the sample to be measured, the water dip will be The injection amount of the sample to be measured can be determined from the area value and the above equation (1) (ie, FIG. 2). Further, the ion amount of each ion can be determined from the peak area value of each ion in this chromatogram etc. and the above equations (2) to (5) (ie, FIG. 3). Further, the value (quotient) obtained by dividing each of the above equations (2) to (5) by the above equation (1) becomes the ion concentration [ng/μl=ppm] of each ion. Therefore, L + ,
If the ion concentration values of Na + , NH 4 + , and K + ions are respectively C Li +, C Na +, C NH4 +, and C K+ , the following equations (6) to (9) hold, and this The concentration of each ion in the sample to be measured can be easily determined from the formula.
CLi+=WLi+/V=4.97×10×ALi+/Awd ……(6)
CNa+=WNa+/V=1.66×102×ANa+/Awd ……(7)
CNH4+=WNH4+/V=1.37×102×ANH4+/Awd……(8)
CK+=WK+/V=3.04×102×AK+/Awd ……(9)
以上詳しく説明したような本発明の実施例よれ
ば、ウオータデイツプの面積値から被測定試料の
注入量を知り各イオンのピーク面積値から各イオ
ンのイオン量を知るような構成であるため、被測
定試料を正確に計量することなく採取された試料
の量とこの試料中のイオン濃度とを測定できる利
点がある。また、被測定試料のイオン濃度が低い
場合に被測定イオン種を濃縮するために行なわれ
る従来の所謂濃縮カラム法においては、濃縮カラ
ムに一定量の試料を正確に注入しなければならな
いという煩雑な操作を必要としていたが、本願発
明によれば、濃縮カラムに注入する程度の概略量
だけ被測定試料を注入すればよく操作が簡単にな
る利点がある。更に、従来の上記濃縮カラム法に
おいては、被測定イオン種のマトリクスによつて
濃縮カラムに完全に捕捉されないようなイオン種
も生じていたが、本願発明によれば、注入された
試料中の被測定イオン種は全てプレカラム等に搬
送されるようになるため、被測定イオン種の測定
誤差が著しく減少するようになる利点もある。 C Li+ = W Li + / V = 4.97 × 10 × A Li + / Awd ... (6) C Na + = W Na + / V = 1.66 × 10 2 × A Na + / Awd ... (7) C NH4 + = W NH4 +/V=1.37×10 2 ×A NH4+ /Awd……(8) C K+ =W K+ /V=3.04×10 2 ×A K+ /Awd……(9) The present invention as explained in detail above According to the embodiment, the injection amount of the sample to be measured is determined from the area value of the water dip, and the ion amount of each ion is determined from the peak area value of each ion, so the sample to be measured can be collected without accurately weighing it. It has the advantage of being able to measure the amount of sample taken and the concentration of ions in this sample. In addition, the conventional so-called concentration column method, which is used to concentrate the ion species to be measured when the ion concentration of the sample to be measured is low, requires the complicated process of precisely injecting a certain amount of sample into the concentration column. However, according to the present invention, it is possible to simplify the operation by injecting the sample to be measured in the approximate amount to be injected into the concentration column. Furthermore, in the conventional concentration column method, some ion species were generated that were not completely captured by the concentration column due to the matrix of ion species to be measured, but according to the present invention, the ion species in the injected sample were Since all of the ion species to be measured are transported to the pre-column or the like, there is also the advantage that measurement errors of the ion species to be measured are significantly reduced.
第1図は本発明実施例の構成説明図、第2図お
よび第3図は標準液を用いて作成したクロマトグ
ラム等、第4図は標準液注入量とウオータデイツ
プピークの面積値との関係を示す図、第5図は標
準液に含有されるイオンの各イオン量とピーク面
積値との関係を示す図である。
1a,1b……槽、2……ポンプ、3……イン
ジエクタ、4……ダンパー、5……プレカラム、
6……分離カラム、7……検出器、8……インテ
グレータ、9……恒温槽。
Figure 1 is an explanatory diagram of the configuration of an embodiment of the present invention, Figures 2 and 3 are chromatograms created using a standard solution, and Figure 4 shows the relationship between the amount of the standard solution injected and the area value of the water dip peak. FIG. 5 is a diagram showing the relationship between the amount of each ion contained in the standard solution and the peak area value. 1a, 1b...tank, 2...pump, 3...injector, 4...damper, 5...precolumn,
6... Separation column, 7... Detector, 8... Integrator, 9... Constant temperature bath.
Claims (1)
中のイオン種を測定する方法において、被測定イ
オン種と同一の各種イオン種および水分を含む標
準液を用いて、あらかじめ、前記水分によるピー
クの面積値と標準液注入量との関係を示す第1グ
ラフと、前記各種イオン種のピーク面積値とイオ
ン量との関係を示す第2グラフとを作成し、その
後、被測定試料を用いてクロマトグラムを作成
し、該クロマトグラム上の水分ピークの面積値と
前記第1グラフから前記被測定試料の注入量Vを
得ると共に、前記クロマトグラム上の各イオンピ
ークの面積値と前記第2グラフから前記被測定試
料中に含まれる各被測定イオン種のイオン量Wi
を得、これらの商(Wi/V)から前記被測定イ
オン種の濃度を求めることを特徴とするイオン種
測定方法。 2 前記水分ピークはウオータデイツプでなる特
許請求範囲第1項記載のイオン種測定方法。 3 前記各被測定イオン種は、Li+,Na+,
NH4 +,およびK+の各イオンでなる特許請求範囲
第1項若しくは第2項記載のイオン種測定方法。[Scope of Claims] 1. In a method for measuring ion species in a sample to be measured using ion chromatography, the above-mentioned A first graph showing the relationship between the area value of the peak due to water and the amount of standard solution injected, and a second graph showing the relationship between the peak area value of the various ion species and the amount of ions are created, and then the sample to be measured is Create a chromatogram using From the second graph, the amount of ions Wi of each ion species to be measured contained in the sample to be measured
A method for measuring an ion species, characterized in that the concentration of the ion species to be measured is determined from the quotient (Wi/V). 2. The ion species measuring method according to claim 1, wherein the moisture peak is a water dip. 3 Each of the ion species to be measured is Li + , Na + ,
The method for measuring ion species according to claim 1 or 2, which comprises NH 4 + and K + ions.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP2588984A JPS60169764A (en) | 1984-02-14 | 1984-02-14 | Measurement of ion speed using ion chromatography |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP2588984A JPS60169764A (en) | 1984-02-14 | 1984-02-14 | Measurement of ion speed using ion chromatography |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS60169764A JPS60169764A (en) | 1985-09-03 |
| JPH0312703B2 true JPH0312703B2 (en) | 1991-02-20 |
Family
ID=12178352
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP2588984A Granted JPS60169764A (en) | 1984-02-14 | 1984-02-14 | Measurement of ion speed using ion chromatography |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPS60169764A (en) |
Families Citing this family (5)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP2572142B2 (en) * | 1990-02-28 | 1997-01-16 | 功二 橋本 | Amorphous alloy catalyst for carbon dioxide conversion |
| JPH0743356B2 (en) * | 1990-03-13 | 1995-05-15 | 信越半導体株式会社 | Dispenser |
| US5316630A (en) * | 1993-03-30 | 1994-05-31 | Dionex Corporation | Methods for chromatography analysis |
| JP2002372521A (en) * | 2001-06-14 | 2002-12-26 | Tosoh Corp | Method for measuring alkalinity using ion chromatography and method for simultaneous measurement with monovalent cations |
| CN110702171A (en) * | 2019-10-29 | 2020-01-17 | 深圳慧格科技服务咨询有限公司 | Method, device and system for monitoring building waste accepting field |
-
1984
- 1984-02-14 JP JP2588984A patent/JPS60169764A/en active Granted
Also Published As
| Publication number | Publication date |
|---|---|
| JPS60169764A (en) | 1985-09-03 |
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