[go: up one dir, main page]

JPH08166377A - Water quality monitor and water quality monitoring method - Google Patents

Water quality monitor and water quality monitoring method

Info

Publication number
JPH08166377A
JPH08166377A JP6332498A JP33249894A JPH08166377A JP H08166377 A JPH08166377 A JP H08166377A JP 6332498 A JP6332498 A JP 6332498A JP 33249894 A JP33249894 A JP 33249894A JP H08166377 A JPH08166377 A JP H08166377A
Authority
JP
Japan
Prior art keywords
water
ion concentration
concentration column
exchange resin
water quality
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.)
Pending
Application number
JP6332498A
Other languages
Japanese (ja)
Inventor
Masayoshi Ito
正義 伊藤
Tetsuo Mizuniwa
哲夫 水庭
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.)
Kurita Water Industries Ltd
Original Assignee
Kurita Water Industries Ltd
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 Kurita Water Industries Ltd filed Critical Kurita Water Industries Ltd
Priority to JP6332498A priority Critical patent/JPH08166377A/en
Publication of JPH08166377A publication Critical patent/JPH08166377A/en
Pending legal-status Critical Current

Links

Landscapes

  • Investigating Or Analyzing Materials By The Use Of Electric Means (AREA)

Abstract

(57)【要約】 【構成】強酸性カチオン交換樹脂及び強塩基性アニオン
交換樹脂を充填したイオン濃縮カラム、イオン濃縮カラ
ムに所定量の試料水を供給する試料水供給機構、イオン
濃縮カラムに捕捉されたイオンを溶離するための高温水
供給機構、イオン濃縮カラムに供給する試料水及び高温
水の切替機構、イオン濃縮カラムからの溶離液の電気伝
導率を測定する電気伝導率計を有することを特徴とする
水質モニター及び該モニターを用いる水質モニタリング
方法。 【効果】本発明の水質モニター及び水質モニタリング方
法によれば、電子工業用超純水のような従来の抵抗率計
では確認できないほどの、試料水中の極めて低いイオン
濃度を測定することができる。
(57) [Summary] [Structure] Ion concentration column packed with strongly acidic cation exchange resin and strongly basic anion exchange resin, sample water supply mechanism that supplies a predetermined amount of sample water to the ion concentration column, trapped on the ion concentration column A high temperature water supply mechanism for eluting the generated ions, a switching mechanism for sample water and high temperature water to be supplied to the ion concentration column, and an electrical conductivity meter for measuring the electrical conductivity of the eluent from the ion concentration column. A characteristic water quality monitor and a water quality monitoring method using the monitor. [Effect] According to the water quality monitor and the water quality monitoring method of the present invention, it is possible to measure an extremely low ion concentration in sample water that cannot be confirmed by a conventional resistivity meter such as ultrapure water for electronic industry.

Description

【発明の詳細な説明】Detailed Description of the Invention

【0001】[0001]

【産業上の利用分野】本発明は、水質モニター及び水質
モニタリング方法に関する。さらに詳しくは、本発明
は、電子工業用超純水のように不純物濃度が極めて低い
水について、正確かつ迅速にその全イオン濃度を測定す
ることができる水質モニター及び水質モニタリング方法
に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a water quality monitor and a water quality monitoring method. More specifically, the present invention relates to a water quality monitor and a water quality monitoring method capable of accurately and rapidly measuring the total ion concentration of water having extremely low impurity concentrations such as ultrapure water for electronic industry.

【0002】[0002]

【従来の技術】電子工業用超純水は純度が極めて高く、
溶存イオン濃度は数μg/リットルないし数ng/リッ
トルのように極めて低い。このような超純水中に存在す
るイオンは、従来は、試料水の電気伝導率を連続的に測
定し、この値を指標とすることで全イオンの存在量が評
価されてきた。また、溶存する全イオンを詳細に把握す
るために、試料水を採水し、イオン交換樹脂を充填した
濃縮用カラムを備えたイオンクロマトグラフで濃縮し、
分離分析することで、その種類を同定し、個別のイオン
濃度が測定されてきた。しかし、電子工業用超純水の純
度が上がるにつれて、超純水の抵抗率は、不純物を全く
含まない理論純水の抵抗率18.24MΩ・cmに限りなく
接近しつつある。このように極めて低い抵抗率を測定す
る際には、現在一般に使用されている抵抗率計の検出装
置では感度、精度ともに不十分であり、全イオン存在量
の確認は非常に困難になってきている。そこで、感度と
精度がより高く、しかも小型で操作が簡単な全イオン濃
度測定装置が要求されている。
2. Description of the Related Art Ultrapure water for electronic industry has extremely high purity,
The dissolved ion concentration is extremely low, such as several μg / liter to several ng / liter. Regarding the ions present in such ultrapure water, the abundance of all ions has been conventionally evaluated by continuously measuring the electrical conductivity of sample water and using this value as an index. Further, in order to grasp all the dissolved ions in detail, sample water is sampled and concentrated by an ion chromatograph equipped with a concentration column filled with an ion exchange resin,
By separate analysis, the type was identified and individual ion concentration was measured. However, as the purity of ultrapure water for electronic industry rises, the resistivity of ultrapure water approaches the resistivity of theoretical pure water containing no impurities, 18.24 MΩ · cm, as much as possible. When measuring extremely low resistivity like this, the sensitivity and accuracy of the detector currently used in the resistivity meter is insufficient, and it is very difficult to confirm the total amount of ions present. There is. Therefore, there is a demand for a total ion concentration measuring device that has higher sensitivity and accuracy, is compact, and is easy to operate.

【0003】[0003]

【発明が解決しようとする課題】本発明は、超純水中の
イオン性不純物を捕捉、濃縮して、その濃度を容易にモ
ニタリングすることができる超純水用水質モニター及び
水質モニタリング方法を提供することを目的としてなさ
れたものである。
The present invention provides a water quality monitor for ultrapure water and a water quality monitoring method capable of capturing and concentrating ionic impurities in ultrapure water and easily monitoring the concentration. It was made for the purpose of doing.

【0004】[0004]

【課題を解決するための手段】本発明者らは、上記の課
題を解決すべく鋭意研究を重ねた結果、超純水中のイオ
ン性不純物をイオン交換樹脂で捕捉したのち、捕捉した
イオン性不純物を高温水で溶離し、その電気伝導率を測
定することにより、超純水中のイオン性不純物の量を容
易に測定し得ることを見いだし、この知見に基づいて本
発明を完成するに至った。すなわち、本発明は、(1)
強酸性カチオン交換樹脂及び強塩基性アニオン交換樹脂
を充填したイオン濃縮カラム、イオン濃縮カラムに所定
量の試料水を供給する試料供給機構、イオン濃縮カラム
に捕捉されたイオンを溶離するための高温水供給機構、
イオン濃縮カラムに供給する試料水及び高温水の切替機
構、イオン濃縮カラムからの溶離液の電気伝導率を測定
する電気伝導率計を有することを特徴とする水質モニタ
ー、及び、(2)試料水を強酸性カチオン交換樹脂及び
強塩基性アニオン交換樹脂を充填したイオン濃縮カラム
に通液して陽イオン及び陰イオンを捕捉せしめたのち、
イオン濃縮カラムに高温水を供給して陽イオン及び陰イ
オンを溶離し、溶離液の電気伝導率を測定することによ
り試料水中の全電解質量を求めることを特徴とする水質
モニタリング方法、を提供するものである。さらに、本
発明の好ましい態様として、(3)強酸性カチオン交換
樹脂と強塩基性アニオン交換樹脂の容量比が、4:6〜
6:4である第(1)項記載の水質モニター又は第(2)項
記載の水質モニタリング方法、及び、(4)高温水の温
度が60〜100℃である第(2)項記載の水質モニタリ
ング方法、を挙げることができる。
Means for Solving the Problems As a result of intensive studies to solve the above problems, the present inventors have found that after capturing ionic impurities in ultrapure water with an ion exchange resin, the captured ionic It was found that the amount of ionic impurities in ultrapure water can be easily measured by eluting impurities with high temperature water and measuring the electric conductivity thereof, and the present invention was completed based on this finding. It was That is, the present invention provides (1)
Ion concentration column packed with strongly acidic cation exchange resin and strong basic anion exchange resin, sample supply mechanism that supplies a predetermined amount of sample water to the ion concentration column, high temperature water for eluting the ions trapped in the ion concentration column Supply mechanism,
A water quality monitor characterized by having a switching mechanism for sample water and high-temperature water supplied to the ion concentration column, an electric conductivity meter for measuring the electric conductivity of the eluent from the ion concentration column, and (2) sample water Was passed through an ion concentration column packed with a strongly acidic cation exchange resin and a strongly basic anion exchange resin to capture cations and anions,
Provided is a water quality monitoring method, characterized in that high-temperature water is supplied to an ion concentrating column to elute cations and anions, and the electric conductivity of the eluent is measured to determine the total electrolytic mass in sample water. It is a thing. Furthermore, as a preferred embodiment of the present invention, (3) the volume ratio of the strongly acidic cation exchange resin and the strongly basic anion exchange resin is 4: 6 to.
The water quality monitor according to item (1) or the water quality monitoring method according to item (2), which is 6: 4, and (4) the water quality according to item (2), wherein the temperature of the high-temperature water is 60 to 100 ° C. A monitoring method can be mentioned.

【0005】本発明の水質モニターにおいて、強酸性カ
チオン交換樹脂及び強塩基性アニオン交換樹脂を充填し
たイオン濃縮カラムは、強酸性カチオン交換樹脂及び強
塩基性アニオン交換樹脂を混合して充填した1本のカラ
ムとすることができ、あるいは、強酸性カチオン交換樹
脂を充填したカラムと強塩基性アニオン交換樹脂を充填
したカラムを直列に連結することができる。強酸性カチ
オン交換樹脂を充填したカラムと強塩基性アニオン交換
樹脂を充填したカラムを直列に連結する場合、連結の順
序に制限はなく、いずれのカラムを上流側に置くことも
可能である。本発明の水質モニターにおいて、試料水供
給機構としては、所定量の試料水をイオン濃縮カラムに
供給することができるものであれば、特に制限なく使用
することが可能であり、例えば、定量ポンプを用いて供
給することができ、あるいは、加圧装置と定流量装置を
組み合わせて供給することができる。高温水供給機構と
しては、例えば、高温水を貯えた恒温水槽より定量ポン
プにより高温水を供給する機構、あるいは、常温水を定
量ポンプで送り、定量ポンプとイオン濃縮カラムの間に
熱交換装置を設けて水を加熱する機構などを使用するこ
とができる。イオン濃縮カラムに供給する試料水及び高
温水の供給切替機構としては、カラムに試料水及び高温
水の配管を接続し、それぞれの配管にコックを設けるこ
とにより試料水及び高温水を切り替えることができ、試
料水及び高温水を配管で三方コックにつなぎ、残りの一
方をカラムにつなぐことができ、あるいは、試料水と高
温水の流路を切り替える切替バルブを設けることができ
る。本発明の水質モニターにおいて、イオン濃縮カラム
からの溶離液は、電気伝導率計へ直接導くことができ、
イオン濃縮カラムと電気伝導率計の間に熱交換器を設け
て溶離液の温度を一定温度まで低下させることができ、
あるいは、イオン濃縮カラムと電気伝導率計の間に一定
量の溶離液を貯留し均一に混合するための容器を設ける
ことができる。電気伝導率の測定値は温度によって大き
く異なるため、電気伝導率計は恒温槽内に設置するか、
温度補償機能、特に二重温度補償機能を有するものが好
ましい。本発明においては、電気伝導率計の代わりに電
気伝導度計を用いることができる。電気伝導度計を用い
るときは、測定した電気伝導度にセル定数を乗じて電気
伝導率を算出する。
In the water quality monitor of the present invention, the ion-concentrating column packed with the strongly acidic cation exchange resin and the strongly basic anion exchange resin is one packed with a mixture of the strongly acidic cation exchange resin and the strongly basic anion exchange resin. Column, or a column packed with a strongly acidic cation exchange resin and a column packed with a strongly basic anion exchange resin can be connected in series. When the column filled with the strongly acidic cation exchange resin and the column filled with the strongly basic anion exchange resin are connected in series, there is no limitation on the order of connection, and any column can be placed on the upstream side. In the water quality monitor of the present invention, the sample water supply mechanism can be used without particular limitation as long as it can supply a predetermined amount of sample water to the ion concentration column. For example, a metering pump can be used. It can be supplied by using, or can be supplied by combining a pressurizing device and a constant flow device. As the high temperature water supply mechanism, for example, a mechanism that supplies high temperature water from a constant temperature water tank that stores high temperature water with a constant volume pump, or sends normal temperature water with a constant volume pump, and installs a heat exchange device between the constant volume pump and the ion concentration column. It is possible to use a mechanism that is provided to heat water. As a mechanism for switching the supply of sample water and high temperature water to the ion concentration column, it is possible to switch between the sample water and high temperature water by connecting the sample water and high temperature water pipes to the column and providing a cock on each pipe. The sample water and the high-temperature water can be connected to the three-way cock by piping and the other one can be connected to the column, or a switching valve for switching the flow paths of the sample water and the high-temperature water can be provided. In the water quality monitor of the present invention, the eluent from the ion concentration column can be directly led to an electric conductivity meter,
A heat exchanger can be installed between the ion concentration column and the conductivity meter to lower the temperature of the eluent to a certain temperature.
Alternatively, a container may be provided between the ion concentrating column and the electric conductivity meter to store a certain amount of the eluent and mix it uniformly. Since the measured value of electric conductivity varies greatly depending on the temperature, should the electric conductivity meter be installed in a thermostatic chamber?
Those having a temperature compensation function, particularly a dual temperature compensation function, are preferable. In the present invention, an electric conductivity meter can be used instead of the electric conductivity meter. When using an electric conductivity meter, the electric conductivity is calculated by multiplying the measured electric conductivity by the cell constant.

【0006】以下、図面により本発明を詳細に説明す
る。図1は、本発明の水質モニターの一態様の系統図で
ある。本図は、イオン濃縮カラムにおいて試料水中のイ
オンを捕捉している状態を示す。試料水路1より試料水
供給ポンプ2により試料水が一定速度で切替バルブ3を
経由して、強酸性イオン交換樹脂及び強塩基性イオン交
換樹脂を充填したイオン濃縮カラム4へ送られ、イオン
濃縮カラムでイオンが捕捉されたのち切替バルブ5を経
由して放流される。試料水の他の一部は、配管6を通っ
て恒温水槽7へ導かれ、恒温水槽内で温度設定型噴流式
撹拌装置を備えた温度調節器8により所定の温度まで加
熱され、高温水となる。高温水は、高温水供給ポンプ9
により一定速度で送られ、切替バルブ5及び3を経由し
て電気伝導率計10へ送られ、電気伝導率κ0が測定さ
れる。試料水として電子工業用超純水を用いる場合は、
電気伝導率κ0の値は通常非常に小さい。図2は、図1
に示す水質モニターのイオン溶離状態を示す系統図であ
る。試料水供給ポンプ2により、所定の流速で所定の時
間、イオン濃縮カラム4に試料水を送り、試料水中の陽
イオン及び陰イオンをカラムに捕捉させたのち、切替バ
ルブ3及び5を回転して図2の状態とする。この状態に
おいて、試料水供給ポンプ2により送られる試料水は、
切替バルブ3及び5を経由して放流される。恒温水槽7
内の高温水は、高温水供給ポンプ9により一定速度で送
られ、切替バルブ5を経由してイオン濃縮カラム4でイ
オンを溶離し、溶離液は切替バルブ3を経由して電気伝
導率計10へ送られ、電気伝導率が測定される。溶離液
の電気伝導率は、連続的に測定することができる。図1
の状態において、試料水を加熱した高温水を、ふたたび
冷却して電気伝導率計10に送り続けることにより、電
気伝導率計に付属する記録計上に、電気伝導率κ0に相
当する安定したベースラインを描かせる。次いで切替バ
ルブを切り替えることにより、高温水によってイオン濃
縮カラムに捕捉されたイオンを溶離し、電気伝導率計に
送る。溶離したイオンが電気伝導率計に送られるにつ
れ、電気伝導率が上昇して記録用紙上にピークが描か
れ、ふたたび電気伝導率の値がベースラインに戻るの
で、ピーク面積より溶離したイオンの量を求めることが
できる。あらかじめ既知量のイオンを含む試料水を用い
て測定を行い、イオン量とピーク面積の関係を表す検量
線を作成しておくことにより、試料水の中に含まれるイ
オンの量を容易に求めることができる。高温水によりイ
オン濃縮カラムから溶離した溶離液の電気伝導率は、回
分式に測定することがでる。回分式に測定する場合は、
切替バルブ3と電気伝導率計10の間に溶離液貯槽(図
1及び図2には示していない。)を設け、一定量の高温
水により陽イオン及び陰イオンを溶離したのち、高温水
の送液を中止し、溶離液貯槽に貯留した溶離液を均一に
混合して電気伝導率計10へ送り、電気伝導率κ1を測
定する。κ1−κ0の値が試料水中に存在した電解質に起
因する電気伝導率となるので、この値及びイオン濃縮カ
ラムに送った試料水の量より、検量線を利用して試料水
中の電解質の量を求めることができる。
The present invention will be described in detail below with reference to the drawings. FIG. 1 is a system diagram of one embodiment of the water quality monitor of the present invention. This figure shows a state where ions in the sample water are captured in the ion concentration column. The sample water is supplied from the sample water channel 1 by the sample water supply pump 2 at a constant speed through the switching valve 3 to the ion concentration column 4 filled with the strongly acidic ion exchange resin and the strongly basic ion exchange resin, and the ion concentration column After the ions are captured by, the ions are discharged via the switching valve 5. The other part of the sample water is guided to the constant temperature water tank 7 through the pipe 6, and is heated to a predetermined temperature by the temperature controller 8 equipped with a temperature-setting type jet stirring device in the constant temperature water tank to obtain high temperature water. Become. The high temperature water is the high temperature water supply pump 9
Is sent at a constant speed and is sent to the electric conductivity meter 10 via the switching valves 5 and 3, and the electric conductivity κ 0 is measured. When using ultra pure water for electronics industry as sample water,
The value of electrical conductivity κ 0 is usually very small. FIG. 2 shows FIG.
3 is a system diagram showing an ion elution state of the water quality monitor shown in FIG. The sample water supply pump 2 sends the sample water to the ion concentration column 4 at a predetermined flow rate for a predetermined period of time to capture cations and anions in the sample water in the column, and then the switching valves 3 and 5 are rotated. The state of FIG. 2 is assumed. In this state, the sample water sent by the sample water supply pump 2 is
It is discharged via the switching valves 3 and 5. Constant temperature water tank 7
The high-temperature water in the inside is sent at a constant speed by the high-temperature water supply pump 9, elutes the ions in the ion concentration column 4 via the switching valve 5, and the eluent passes through the switching valve 3 and the electric conductivity meter 10 And the electrical conductivity is measured. The electric conductivity of the eluent can be continuously measured. FIG.
In this state, the high-temperature water obtained by heating the sample water is cooled again and kept being sent to the electric conductivity meter 10, so that a stable base corresponding to the electric conductivity κ 0 is recorded on the recorder attached to the electric conductivity meter. Draw a line. Then, by switching the switching valve, the ions captured in the ion concentrating column are eluted by the high temperature water and sent to the electric conductivity meter. As the eluted ions are sent to the electric conductivity meter, the electric conductivity rises and a peak is drawn on the recording paper, and the electric conductivity value returns to the baseline again. Can be asked. The amount of ions contained in the sample water can be easily obtained by performing measurement in advance using sample water containing a known amount of ions and creating a calibration curve that shows the relationship between the ion amount and the peak area. You can The electrical conductivity of the eluent eluted from the ion concentrating column with high temperature water can be measured batchwise. When measuring in batch mode,
An eluent storage tank (not shown in FIGS. 1 and 2) is provided between the switching valve 3 and the electric conductivity meter 10 to elute cations and anions with a certain amount of high temperature water, and then the high temperature water. The liquid supply is stopped, the eluents stored in the eluent storage tank are uniformly mixed and sent to the electric conductivity meter 10, and the electric conductivity κ 1 is measured. The value of κ 1 −κ 0 is the electrical conductivity due to the electrolyte present in the sample water.Therefore, from this value and the amount of sample water sent to the ion concentration column, the calibration curve is used to determine the electrolyte The quantity can be calculated.

【0007】図1及び図2においては、試料水と高温水
は、イオン濃縮カラムにおいて逆方向に流れる向流方式
となっている。向流方式によれば、各カラムに捕捉され
たイオンを短時間に溶離し、排出することができる。し
かし、必要に応じて、試料水と高温水がイオン濃縮カラ
ムにおいて同一方向に流れる並流方式を採用することが
できる。本発明の水質モニターにおいて、使用する強酸
性カチオン交換樹脂及び強塩基性アニオン交換樹脂の比
率は、容量比で3:7〜7:3であることが好ましく、
4:6〜6:4であることがさらに好ましく、5:5で
あることが特に好ましい。強酸性カチオン交換樹脂と強
塩基性アニオン交換樹脂は、混合して1本のカラムに充
填して使用することができ、あるいは、強酸性カチオン
交換樹脂と強塩基性アニオン交換樹脂を別々のカラムに
充填し、2本のカラムを直列に連結して使用することが
できる。本発明の水質モニタリング方法において、高温
水の温度は60〜100℃であることが好ましく、70
〜90℃であることがさらに好ましい。高温水の温度が
60℃未満であると、イオン濃縮カラムに捕捉されたイ
オンの溶離速度が遅く、溶離液の量が多くなり、溶離液
のイオン濃度が希くなる。高温水の温度が100℃を超
えると、沸騰を抑えるために加圧しなければならないの
で装置及び操作が複雑になる。本発明の水質モニターに
おいては、制御装置を設けることができ、例えば、制御
盤で、試料水供給時間、流速の設定、測定開始指示を行
い、切換バルブの操作、検出データの記録、ピーク面積
の計算、標準試料(検量線)との対比、結果の記録、ポ
ンプの発停を制御することができる。本発明の水質モニ
タリング方法においては、試料水中のイオンをイオン濃
縮カラムに試料水を通水することにより捕捉せしめ、そ
の後切替バルブを切り替えて、高温水をイオン濃縮カラ
ムに通液してイオンを溶離する。溶離されたイオンは、
電気伝導率計により電気伝導率を測定することによって
イオン濃度を求める。試料水のイオン濃度が極めて低い
場合には、通水量を多く、すなわちイオンの濃縮量を多
くすることにより、数十倍ないし数百倍に濃縮して、試
料水中の極めて低濃度の全イオンを測定することができ
る。本発明の水質モニターの一態様は、試料水供給ポン
プ、強酸性イオン交換樹脂及び強塩基性イオン交換樹脂
を混合して充填した濃縮カラム、切替バルブ、恒温水
槽、高温水送水ポンプ及び電気伝導率計で構成されてい
る。試料水をポンプで濃縮カラムに通水することにより
全イオンを濃縮し、次に高温水を濃縮カラムに送水して
濃縮したイオンを溶離し、これを電気伝導率計で測定す
ることにより、従来の電気伝導率計では測定できないよ
り低濃度レベルの電解質の量を、全イオン濃度として測
定することができる。また、この装置の構成が単純であ
り、分析操作が非常に簡略化されていることから、監視
装置として適用することができる。試料水の全イオン濃
度が極めて低い場合には、通水時間を長くして濃縮量を
多くすることにより、精度よく測定することができる。
In FIG. 1 and FIG. 2, the sample water and the high temperature water are in a countercurrent system in which they flow in opposite directions in the ion concentrating column. According to the countercurrent method, the ions trapped in each column can be eluted and discharged in a short time. However, if necessary, a parallel flow method in which the sample water and the high temperature water flow in the same direction in the ion concentration column can be adopted. In the water quality monitor of the present invention, the ratio of the strongly acidic cation exchange resin and the strongly basic anion exchange resin used is preferably 3: 7 to 7: 3 by volume ratio,
It is more preferably 4: 6 to 6: 4, and particularly preferably 5: 5. The strongly acidic cation exchange resin and the strongly basic anion exchange resin can be mixed and packed in one column for use, or the strongly acidic cation exchange resin and the strongly basic anion exchange resin can be used in separate columns. It can be packed and used by connecting two columns in series. In the water quality monitoring method of the present invention, the temperature of the high temperature water is preferably 60 to 100 ° C.,
More preferably, the temperature is 90 ° C. When the temperature of the high-temperature water is lower than 60 ° C., the elution rate of the ions captured by the ion concentrating column is slow, the amount of the eluent increases, and the ion concentration of the eluent becomes low. If the temperature of the hot water exceeds 100 ° C., pressure and pressure must be applied to suppress boiling, which complicates the apparatus and operation. In the water quality monitor of the present invention, a control device can be provided, and for example, a control panel is used to set the sample water supply time, flow rate setting, measurement start instruction, operation of the switching valve, recording of detection data, and measurement of peak area. It is possible to control calculation, comparison with a standard sample (calibration curve), recording of results, and start / stop of the pump. In the water quality monitoring method of the present invention, the ions in the sample water are captured by passing the sample water through the ion concentration column, and then the switching valve is switched to pass the high temperature water through the ion concentration column to elute the ions. To do. The eluted ions are
The ion concentration is determined by measuring the electric conductivity with an electric conductivity meter. When the ion concentration of sample water is extremely low, the amount of water flow is increased, that is, by increasing the concentration of ions, the concentration is increased to several tens to several hundreds of times, and all ions of extremely low concentration in the sample water are collected. Can be measured. One aspect of the water quality monitor of the present invention is a sample water supply pump, a concentration column filled with a mixture of a strongly acidic ion exchange resin and a strongly basic ion exchange resin, a switching valve, a constant temperature water tank, a high temperature water feed pump, and an electric conductivity. It consists of a total. By concentrating all the ions by pumping sample water through the concentrating column, then sending hot water to the concentrating column to elute the concentrated ions and measuring them with an electric conductivity meter. The amount of electrolyte at a lower concentration level, which cannot be measured by the electric conductivity meter described above, can be measured as the total ion concentration. Moreover, since the structure of this device is simple and the analysis operation is very simplified, it can be applied as a monitoring device. When the total ion concentration of sample water is extremely low, it is possible to perform accurate measurement by increasing the water passage time and increasing the concentration amount.

【0008】[0008]

【実施例】以下に、実施例を挙げて本発明をさらに詳細
に説明するが、本発明はこれらの実施例によりなんら限
定されるものではない。 実施例1 図1に示す装置を用いて、電子工業用超純水に塩化ナト
リウムを加えた水について、水質の測定を行い検量線を
作成した。陽イオン濃縮カラム4は、内径4mm×長さ3
5mmのガラスカラムに強酸性カチオン交換樹脂0.14m
l及び強塩基性アニオン交換樹脂0.14mlを充填したも
のである。試料水供給ポンプ2は、送水量4ml/分のプ
ランジャー式定量ポンプである。恒温水槽の温度は、温
度設定型噴流式撹拌装置を備えた温度調節器により設定
されている。高温水供給ポンプ9は、送水量4ml/分の
プランジャー式定量ポンプである。電気伝導率計10
は、ダイオネクス(株)製、DX−100型で、温度補償
機能を有するものである。切替バルブ3及び5を図1の
状態とし、試料水供給ポンプ2により、超純水に塩化ナ
トリウムが10ng/リットルになるよう加えた水を3
0分間、送水量が120mlになるまで切替バルブ3を通
じてイオン濃縮カラム4に送水し、ナトリウムイオン及
び塩素イオンを捕捉せしめ、切替バルブ5を通じて放流
した。この間、高温水供給ポンプ9により高温水を送水
し、切替バルブ5及び3を経由して、電気伝導率計10
により電気伝導率を測定した。電気伝導率計に付属する
記録計の表示は送水開始5分後には安定し、ベースライ
ンは直線状となった。イオン濃縮カラムへの送水量が1
20mlに達したとき、2個の切替バルブを回転して図2
の状態とし、高温水によるナトリウムイオン及び塩素イ
オンの溶離を開始した。高温水の温度は70℃に設定
し、恒温水槽からの配管、高温水供給ポンプ、切替バル
ブ5及びイオン濃縮カラムは保温して、イオン濃縮カラ
ムの温度が70±1℃となる状態でナトリウムイオン及
び塩素イオンの溶離を行った。溶離液は、切替バルブ3
を経由し電気伝導率計に送った。ほどなく電気伝導率計
の記録計には電気伝導率の上昇が認められ、記録用紙に
ピークが記録されたのち、電気伝導率の値は再びベース
ラインの値にもどった。記録計で求めたピーク面積は、
451nS・cm-1・secであった。塩化ナトリウムの濃度
が50ng/リットル及び100ng/リットルの水を
用いて全く同じ試験を繰り返したところ、ピーク面積は
それぞれ523nS・cm-1・sec及び612nS・cm-1・sec
であった。塩化ナトリウムの濃度を横軸に、ピーク面積
を縦軸にとって、これらのデータをプロットしたとこ
ろ、図3に示すようにほぼ直線となった。すなわち、図
3は、通水量120mlに対応する、ピーク面積と塩化ナ
トリウム濃度の関係を示すグラフであり、このグラフを
もとにして検量線を作成し、試料水中の電解質の量を塩
化ナトリウムに換算して求めることができる。 実施例2 電子工業用超純水中の電解質の量を測定した。超純水の
水路に試料水供給ポンプ2をつなぎ、切替バルブ3及び
5を図1の状態とし、試料水供給ポンプ2により、超純
水を30分間、送水量が120mlになるようイオン濃縮
カラム4に送水した。この間、高温水供給ポンプにより
高温水を送水し、2個の切替バルブを経由して、電気伝
導率計により電気伝導率を測定した。電気伝導率計に付
属する記録計の表示は終始安定し、ベースラインは直線
状であった。イオン濃縮カラムへの送水量が120mlに
達したとき、2個の切替バルブを回転して図2の状態と
し、実施例1と同様にして高温水による陽イオン及び陰
イオンの溶離を開始した。ほどなく電気伝導率計の記録
計には電気伝導率の上昇が認められ、記録用紙にピーク
が記録されたのち、電気伝導率の値は再びベースライン
の値にもどった。記録計で求めたピーク面積は、432
nS・cm-1・secであった。この結果から、この電子工業
用超純水の中には塩化ナトリウムに換算して240ng
/リットルに相当する電解質が含まれていることが分か
った。
The present invention will be described in more detail below with reference to examples, but the present invention is not limited to these examples. Example 1 Using the apparatus shown in FIG. 1, the water quality of water obtained by adding sodium chloride to ultrapure water for electronic industry was measured to prepare a calibration curve. The cation concentration column 4 has an inner diameter of 4 mm and a length of 3
Strongly acidic cation exchange resin 0.14 m in a 5 mm glass column
and 0.14 ml of a strongly basic anion exchange resin. The sample water supply pump 2 is a plunger type metering pump having a water supply rate of 4 ml / min. The temperature of the constant temperature water tank is set by a temperature controller equipped with a temperature setting type jet stirring device. The high temperature water supply pump 9 is a plunger type metering pump having a water supply rate of 4 ml / min. Electrical conductivity meter 10
Is a DX-100 type manufactured by Dionex Co., Ltd., which has a temperature compensation function. With the switching valves 3 and 5 in the state shown in FIG. 1, the sample water supply pump 2 was used to add 3 parts of water added to ultrapure water so that sodium chloride was adjusted to 10 ng / liter.
Water was fed to the ion concentration column 4 through the switching valve 3 for 0 minutes until the amount of water fed reached 120 ml to trap sodium ions and chlorine ions, and then discharged through the switching valve 5. During this time, high temperature water is sent by the high temperature water supply pump 9, and the electric conductivity meter 10 is passed through the switching valves 5 and 3.
The electrical conductivity was measured by. The display of the recorder attached to the electric conductivity meter became stable 5 minutes after the start of water supply, and the baseline became linear. The amount of water sent to the ion concentration column is 1
When it reaches 20 ml, rotate the two switching valves and
Then, elution of sodium ion and chlorine ion with high temperature water was started. The temperature of the high-temperature water is set to 70 ° C, the piping from the constant temperature water tank, the high-temperature water supply pump, the switching valve 5 and the ion concentration column are kept warm, and the temperature of the ion concentration column is 70 ± 1 ° C And chlorine ions were eluted. Eluent is switching valve 3
It sent to the electric conductivity meter via. Soon after, an increase in the electric conductivity was observed in the recorder of the electric conductivity meter, and after the peak was recorded on the recording paper, the electric conductivity value returned to the baseline value again. The peak area obtained by the recorder is
It was 451 nS · cm −1 · sec. When exactly the same test was repeated using water having sodium chloride concentrations of 50 ng / liter and 100 ng / liter, the peak areas were 523 nS · cm −1 · sec and 612 nS · cm −1 · sec, respectively.
Met. When these data were plotted by plotting the concentration of sodium chloride on the horizontal axis and the peak area on the vertical axis, a substantially straight line was obtained as shown in FIG. That is, FIG. 3 is a graph showing the relationship between the peak area and the sodium chloride concentration corresponding to a water flow rate of 120 ml, and a calibration curve was created based on this graph, and the amount of electrolyte in sample water was changed to sodium chloride. It can be calculated and calculated. Example 2 The amount of electrolyte in ultrapure water for electronic industry was measured. The sample water supply pump 2 is connected to the ultrapure water channel, the switching valves 3 and 5 are set to the state shown in FIG. 1, and the sample water supply pump 2 is used to supply ultrapure water for 30 minutes and the amount of water supplied is 120 ml. Water was sent to 4. During this time, high temperature water was sent by a high temperature water supply pump, and the electric conductivity was measured by an electric conductivity meter via two switching valves. The display of the recorder attached to the conductivity meter was stable from beginning to end, and the baseline was linear. When the amount of water supplied to the ion concentrating column reached 120 ml, the two switching valves were rotated to the state shown in FIG. 2, and elution of cations and anions with high temperature water was started in the same manner as in Example 1. Soon after, an increase in the electric conductivity was observed in the recorder of the electric conductivity meter, and after the peak was recorded on the recording paper, the electric conductivity value returned to the baseline value again. The peak area obtained by the recorder is 432
It was nS · cm −1 · sec. From this result, 240 ng of ultrapure water for electronic industry is converted into sodium chloride.
It was found to contain an electrolyte corresponding to 1 liter / liter.

【0009】[0009]

【発明の効果】本発明の水質モニター及び水質モニタリ
ング方法によれば、電子工業用超純水のような従来の抵
抗率計では確認できないほどの、試料水中の極めて低い
イオン濃度を測定することができる。
According to the water quality monitor and the water quality monitoring method of the present invention, it is possible to measure an extremely low ion concentration in sample water that cannot be confirmed by a conventional resistivity meter such as ultrapure water for electronic industry. it can.

【図面の簡単な説明】[Brief description of drawings]

【図1】図1は、本発明の水質モニターの一態様の系統
図である。
FIG. 1 is a system diagram of one embodiment of a water quality monitor of the present invention.

【図2】図2は、図1に示す水質モニターのイオン溶離
状態を示す系統図である。
FIG. 2 is a system diagram showing an ion elution state of the water quality monitor shown in FIG.

【図3】図3は、ピーク面積と塩化ナトリウム濃度の関
係を示すグラフである。
FIG. 3 is a graph showing the relationship between peak area and sodium chloride concentration.

【符号の説明】[Explanation of symbols]

1 試料水路 2 試料水供給ポンプ 3 切替バルブ 4 イオン濃縮カラム 5 切替バルブ 6 配管 7 恒温水槽 8 温度調節器 9 高温水供給ポンプ 10 電気伝導率計 1 Sample Water Channel 2 Sample Water Supply Pump 3 Switching Valve 4 Ion Concentration Column 5 Switching Valve 6 Piping 7 Constant Temperature Water Tank 8 Temperature Controller 9 High Temperature Water Supply Pump 10 Electrical Conductivity Meter

Claims (2)

【特許請求の範囲】[Claims] 【請求項1】強酸性カチオン交換樹脂及び強塩基性アニ
オン交換樹脂を充填したイオン濃縮カラム、イオン濃縮
カラムに所定量の試料水を供給する試料水供給機構、イ
オン濃縮カラムに捕捉されたイオンを溶離するための高
温水供給機構、イオン濃縮カラムに供給する試料水及び
高温水の切替機構、イオン濃縮カラムからの溶離液の電
気伝導率を測定する電気伝導率計を有することを特徴と
する水質モニター。
1. An ion concentration column filled with a strongly acidic cation exchange resin and a strongly basic anion exchange resin, a sample water supply mechanism for supplying a predetermined amount of sample water to the ion concentration column, and an ion trapped in the ion concentration column. Water quality characterized by having a high-temperature water supply mechanism for elution, a switching mechanism for sample water and high-temperature water supplied to the ion concentration column, and an electric conductivity meter for measuring the electric conductivity of the eluent from the ion concentration column monitor.
【請求項2】試料水を強酸性カチオン交換樹脂及び強塩
基性アニオン交換樹脂を充填したイオン濃縮カラムに通
液して陽イオン及び陰イオンを捕捉せしめたのち、イオ
ン濃縮カラムに高温水を供給して陽イオン及び陰イオン
を溶離し、溶離液の電気伝導率を測定することにより試
料水中の全電解質量を求めることを特徴とする水質モニ
タリング方法。
2. Sample water is passed through an ion concentration column packed with a strongly acidic cation exchange resin and a strongly basic anion exchange resin to capture cations and anions, and then high temperature water is supplied to the ion concentration column. A method for monitoring water quality, characterized in that the total electrolytic mass in sample water is obtained by eluting positive and negative ions and measuring the electric conductivity of the eluent.
JP6332498A 1994-12-13 1994-12-13 Water quality monitor and water quality monitoring method Pending JPH08166377A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP6332498A JPH08166377A (en) 1994-12-13 1994-12-13 Water quality monitor and water quality monitoring method

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP6332498A JPH08166377A (en) 1994-12-13 1994-12-13 Water quality monitor and water quality monitoring method

Publications (1)

Publication Number Publication Date
JPH08166377A true JPH08166377A (en) 1996-06-25

Family

ID=18255614

Family Applications (1)

Application Number Title Priority Date Filing Date
JP6332498A Pending JPH08166377A (en) 1994-12-13 1994-12-13 Water quality monitor and water quality monitoring method

Country Status (1)

Country Link
JP (1) JPH08166377A (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2008309699A (en) * 2007-06-15 2008-12-25 Hitachi High-Technologies Corp Two-dimensional liquid chromatograph with ion exchange and normal phase column

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2008309699A (en) * 2007-06-15 2008-12-25 Hitachi High-Technologies Corp Two-dimensional liquid chromatograph with ion exchange and normal phase column

Similar Documents

Publication Publication Date Title
US3897213A (en) Automated quantitative analysis of ionic species
US20110174063A1 (en) Multichannel ion chromatography system and method
JP2004506185A (en) Low level boron detection and measurement
Shintani et al. Gradient anion chromatography with hydroxide and carbonate eluents using simultaneous conductivity and pH detection
Mohilner et al. Activities of organic compounds in aqueous electrolyte solutions
AU711415B2 (en) Multi-cycle loop injection for trace analysis by ion chromatography apparatus and method
US3918906A (en) Determining total ionic content
JPH08166377A (en) Water quality monitor and water quality monitoring method
JPH08166378A (en) Water quality monitor and water quality monitoring method
Tabatabai et al. Liquid chromatography
EP2820401B1 (en) Device and method for calorimetrically measuring sorption processes
JPH0262819B2 (en)
JP3900504B2 (en) Ultrapure water ion monitor
Muntean Food Analysis: Using Ion Chromatography
Haddad et al. On-line analysis of alkaline samples with a flow-through electrodialysis device coupled to an ion chromatograph
JPS60114579A (en) Etching solution control method
JPS60190859A (en) Ion species analysis method and device
US3451403A (en) Method and apparatus for determining the purity of a flowing solution or mixture
CN201607423U (en) Fast constant temperature measurement device
CN101109727A (en) Automatic constant temperature measuring apparatus of ammonia nitrogen automonitor
WO2025260477A1 (en) Ion chromatography detection system for zinc and nickel ions in primary loop of nuclear power plant
JPS61195354A (en) Method and instrument for measuring trace cation
CN210992298U (en) Quantitative fixed-distance injection device for trace liquid based on thermal expansion
JPH0439906B2 (en)
SU1564530A1 (en) Liquid chromatograph

Legal Events

Date Code Title Description
A977 Report on retrieval

Effective date: 20060118

Free format text: JAPANESE INTERMEDIATE CODE: A971007

A131 Notification of reasons for refusal

Effective date: 20060131

Free format text: JAPANESE INTERMEDIATE CODE: A131

A601 Written request for extension of time

Free format text: JAPANESE INTERMEDIATE CODE: A601

Effective date: 20060501

A602 Written permission of extension of time

Free format text: JAPANESE INTERMEDIATE CODE: A602

Effective date: 20060509

A521 Written amendment

Free format text: JAPANESE INTERMEDIATE CODE: A523

Effective date: 20060719

A02 Decision of refusal

Effective date: 20061222

Free format text: JAPANESE INTERMEDIATE CODE: A02