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JPH11258191A - Method and apparatus for measurement of concentration of carbonic acid - Google Patents

Method and apparatus for measurement of concentration of carbonic acid

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Publication number
JPH11258191A
JPH11258191A JP7493198A JP7493198A JPH11258191A JP H11258191 A JPH11258191 A JP H11258191A JP 7493198 A JP7493198 A JP 7493198A JP 7493198 A JP7493198 A JP 7493198A JP H11258191 A JPH11258191 A JP H11258191A
Authority
JP
Japan
Prior art keywords
water
carbonic acid
concentration
conductivity
sample
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
JP7493198A
Other languages
Japanese (ja)
Inventor
Madoka Tanabe
円 田辺
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.)
Organo Corp
Original Assignee
Organo Corp
Japan Organo Co 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 Organo Corp, Japan Organo Co Ltd filed Critical Organo Corp
Priority to JP7493198A priority Critical patent/JPH11258191A/en
Publication of JPH11258191A publication Critical patent/JPH11258191A/en
Pending legal-status Critical Current

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Abstract

PROBLEM TO BE SOLVED: To obtain a method and an apparatus in which the concentration of carbonic acid in water with the comparatively high concentration of carbonic acid and with little salts other than carbonic acid is measured by a simple operation and quickly during the preparation process of pure water, for cleaning, which is used in a semiconductor-device manufacturing process. SOLUTION: In a measuring apparatus 10 for the concentration of carbonic acid, a sample- water introduction pipe 21 which is provided with a hydrogen ion-type strongly acidic cation- exchange resin column 3 and a sample-water flow-rate detection part 4 is provided. A dilute- water injection pipe 22 which is provided with a dilute-water flow-rate detection part 6 joining it is provided. A conductivity detection part 5 which measures the conductivity of diluted sample water is provided. A computing part 7 which computes the concentration of carbonic acid in the sample water on the basis of signals from the two flow-rate detection parts 4, 6 and from the conductivity detection part 5 is provided. A display part 8 which displays the computed concentration of the carbonic acid is provided. By using the apparatus 10, the concentration of the carbonic acid in the permeated water, in a reverse osmosis membrane device, whose concentration of carbonic acid is high and which contains little salts other than carbonic acid or in treated water in an ultraviolet oxidation device can be measured by a simple operation and quickly in the preparation process of pure water, for cleaning, which is used, e.g. in a semiconductor-device manufacturing process.

Description

【発明の詳細な説明】DETAILED DESCRIPTION OF THE INVENTION

【0001】[0001]

【発明の属する技術分野】本発明は、例えば、半導体デ
バイス製造工程で使用される洗浄用純水の製造工程中、
炭酸濃度が比較的高く、且つ炭酸以外の塩類が少ない水
中の該炭酸濃度を、簡便な操作で、且つ迅速に測定する
方法及び装置に関するものである。
The present invention relates to a process for producing pure water for cleaning used in a process for producing semiconductor devices, for example.
The present invention relates to a method and an apparatus for measuring the concentration of carbonic acid in water having a relatively high carbonic acid concentration and low in salts other than carbonic acid by a simple operation and quickly.

【0002】[0002]

【従来の技術】純水製造装置には種々の形式のものがあ
る。その中で、井水、工業用水などの原水を直接又は除
濁などの前処理をした後、逆浸透膜装置で処理するもの
がある。これは前段逆浸透膜装置方式と呼ばれ、この方
式は後段に更に配置されるイオン交換樹脂装置や電気式
脱イオン水製造装置などの脱塩装置の負荷を低減すると
共に、原水に含まれる有機物や微粒子を除去するもので
ある。また、超純水製造装置の二次純水系では、紫外線
酸化装置、精製カラムを設置し、被処理水をこの順序で
通水することがある。すなわち、被処理水中の有機物を
紫外線酸化により有機酸と炭酸に分解し、該有機酸を精
製カラムで除去するものである。
2. Description of the Related Art There are various types of pure water producing apparatuses. Among them, there is a method in which raw water such as well water or industrial water is directly or pretreated by turbidity or the like, and then treated by a reverse osmosis membrane device. This system is called a pre-stage reverse osmosis membrane system. This system reduces the load on desalination units such as ion exchange resin units and electric deionized water production units that are further arranged at the subsequent stage, and reduces the organic matter contained in raw water. And to remove fine particles. Further, in the secondary pure water system of the ultrapure water production apparatus, an ultraviolet oxidizing apparatus and a purification column are installed, and water to be treated may be passed in this order. That is, organic substances in the water to be treated are decomposed into organic acids and carbonic acids by ultraviolet oxidation, and the organic acids are removed by a purification column.

【0003】しかし、逆浸透膜装置では被処理水中に溶
存する炭酸を除去することができない。また、紫外線酸
化装置では処理水中に炭酸を排出する。したがって、こ
れらの透過水又は処理水中には、炭酸が溶存することと
なる。これらの炭酸は、イオン状のみならず中性分子状
の炭酸ガスも溶存しており、後段の脱塩装置にはこれら
中性分子状の炭酸ガスを含めてすべてがイオン負荷とな
る。このため、後段の脱塩装置の仕様や運転方法を適切
なものとするためには、逆浸透膜装置の透過水や紫外線
酸化装置の処理水中の炭酸濃度を正確に把握することが
重要である。
However, a reverse osmosis membrane device cannot remove carbonic acid dissolved in the water to be treated. In the ultraviolet oxidation apparatus, carbon dioxide is discharged into the treated water. Therefore, carbonic acid is dissolved in the permeated water or the treated water. In these carbonic acids, not only ionic but also neutral molecular carbon dioxide is dissolved, and all of the carbon dioxide including the neutral molecular carbon dioxide is subjected to ionic load in the subsequent desalination apparatus. For this reason, in order to make the specifications and operation method of the subsequent desalination device appropriate, it is important to accurately grasp the carbon dioxide concentration in the permeated water of the reverse osmosis membrane device and the treated water of the ultraviolet oxidation device. .

【0004】これら水中の炭酸は、炭酸イオン、炭酸水
素イオン、中性分子である炭酸ガスなどの形態で存在し
ている。このため、これらを測定する際には、外気と接
触を避けるため、試料水を測定設備に直接導入するイン
ライン測定とする必要がある。従来、炭酸濃度をインラ
インで測定可能な測定装置としては、イオンクロマト
法、有機炭素と無機炭素を個別に測定可能なTOC計を
用いて無機炭素濃度のみを測定する方法及び炭酸濃度に
応じて電気抵抗値が変化することを利用した導電率計を
用いる方法などが知られている。
[0004] Carbonic acid in water exists in the form of carbonate ions, bicarbonate ions, carbon dioxide as a neutral molecule, and the like. For this reason, when measuring these, in order to avoid contact with outside air, it is necessary to perform in-line measurement in which sample water is directly introduced into the measurement equipment. Conventionally, measuring devices capable of measuring carbon dioxide concentration in-line include an ion chromatography method, a method of measuring only inorganic carbon concentration using a TOC meter capable of separately measuring organic carbon and inorganic carbon, and an electric device according to carbon dioxide concentration. There is known a method using a conductivity meter that utilizes a change in resistance value.

【0005】[0005]

【発明が解決しようとする課題】しかしながら、イオン
クロマト法や、TOC計を用いる方法はいずれも高価な
測定装置を必要とし、また、その装置を運転するために
は校正作業や必要な試薬の調製作業などの煩雑な作業が
必要であった。特に、純水製造装置の動作に異常が生じ
た場合には工場の生産などへの影響を最小限に押さえて
早期回復を図るために、装置内各所における水質分析を
迅速に行う必要があるが、これら従来の方法では準備作
業が煩雑であり、迅速な対応は困難であった。また、導
電率計を用いる方法は、簡便な方法ではあるものの、炭
酸と共存する他の塩類の影響があること、さらに炭酸の
量が多い非希薄系では誤差が大きく実用的ではないなど
の問題があった。
However, both the ion chromatography method and the method using a TOC meter require an expensive measuring device, and in order to operate the device, calibration work and preparation of necessary reagents are required. Complicated work such as work was required. In particular, when an abnormality occurs in the operation of the pure water production equipment, it is necessary to quickly analyze the water quality at various points in the equipment in order to minimize the impact on the production of the factory and achieve an early recovery. However, in these conventional methods, the preparation work is complicated, and it is difficult to respond quickly. In addition, although the method using a conductivity meter is a simple method, there are problems such as the influence of other salts coexisting with carbonic acid, and a large error in a non-dilute system having a large amount of carbonic acid. was there.

【0006】したがって、本発明の目的は、例えば、半
導体デバイス製造工程で使用される洗浄用純水の製造工
程中、炭酸濃度が比較的高く、且つ炭酸以外の塩類が少
ない水中の該炭酸濃度を、簡便な操作で、且つ迅速に測
定する方法及び装置を提供することにある。
Accordingly, an object of the present invention is to reduce the concentration of carbonic acid in water having a relatively high concentration of carbonic acid and a small amount of salts other than carbonic acid during the manufacturing process of pure water for cleaning used in the semiconductor device manufacturing process. Another object of the present invention is to provide a method and an apparatus for performing simple and quick measurement.

【0007】[0007]

【課題を解決するための手段】かかる実情において、本
発明者は鋭意検討を行った結果、純水製造工程中、逆浸
透膜装置の透過水及び紫外線照射装置の処理水は、炭酸
濃度が高く、且つ炭酸と共存する他の塩類が少ないこ
と、該透過水及び処理水中の炭酸濃度を希釈して特定の
濃度範囲とすれば、炭酸濃度を導電率計で精度よく測定
できることを見出し、本発明を完成するに至った。すな
わち、本発明は、逆浸透膜装置の透過水中の炭酸濃度を
測定する方法において、該透過水を、水素イオン形強酸
性陽イオン交換樹脂に接触させた後、該接触水を高純度
水で希釈し、その希釈液の導電率の値から炭酸イオンを
算出する炭酸濃度測定方法を提供するものである。な
お、導電率の逆数が抵抗率であり、例えば、導電率0.
1μS/cmが抵抗率10M Ω・cmに相当する。比較的高純
度の水は数字を大きく表現できる抵抗率で表示すること
があるが、本発明においては導電率と抵抗率は同義語と
して扱う。本発明によれば、逆浸透膜装置の透過水中、
後段の脱塩装置の負荷イオンとなる炭酸ガス、炭酸イオ
ン及び炭酸水素ナトリウムなどのうち、炭酸水素ナトリ
ウムは、水素イオン形強酸性陽イオン交換樹脂により炭
酸に変化するため、導電率計5での測定値をより正確に
炭酸濃度へ変換できる。このため、後段の脱塩装置の負
荷量を決定する精度が向上する。また、試料水中、炭酸
以外の陰イオン成分は炭酸濃度と比較して無視できる濃
度であるが、高純度水の希釈によって該陰イオン成分は
更に低濃度となるため、導電率計での測定精度がより高
められる。
Under such circumstances, the present inventors have conducted intensive studies. As a result, during the pure water production process, the permeated water of the reverse osmosis membrane device and the treated water of the ultraviolet irradiation device have a high carbon dioxide concentration. The present invention has been found that the amount of other salts coexisting with carbonic acid is small, and that the carbonic acid concentration can be accurately measured by a conductivity meter if the carbonic acid concentration in the permeated water and the treated water is adjusted to a specific concentration range. Was completed. That is, the present invention provides a method for measuring the concentration of carbonic acid in permeated water of a reverse osmosis membrane device, wherein the permeated water is brought into contact with a hydrogen ion type strongly acidic cation exchange resin, and then the contact water is purified with high-purity water. An object of the present invention is to provide a method for measuring the concentration of carbonic acid which is diluted and calculates carbonate ions from the value of the conductivity of the diluted solution. Note that the reciprocal of the conductivity is the resistivity.
1 μS / cm corresponds to a resistivity of 10 MΩ · cm. Water of relatively high purity may be represented by a resistivity capable of expressing a large number, but in the present invention, conductivity and resistivity are treated as synonyms. According to the present invention, the permeated water of the reverse osmosis membrane device,
Among the carbon dioxide gas, carbonate ions, sodium hydrogen carbonate, and the like, which are the load ions of the subsequent desalination apparatus, sodium hydrogen carbonate is converted into carbon dioxide by the hydrogen ion type strongly acidic cation exchange resin. The measured values can be converted to carbon dioxide concentration more accurately. Therefore, the accuracy of determining the load of the subsequent desalination apparatus is improved. The anion components other than carbonic acid in the sample water are negligible compared to the carbonic acid concentration. However, the dilution of the high-purity water further reduces the anion components, so that the measurement accuracy with the conductivity meter is reduced. Is further enhanced.

【0008】また、本発明は、紫外線酸化装置の処理水
中の炭酸濃度を測定する方法において、該処理水を高純
度水で希釈し、その希釈液の導電率の値から炭酸イオン
を算出する炭酸濃度測定方法を提供するものである。本
発明によれば、紫外線酸化装置の処理水中の炭酸濃度を
簡便な操作で、且つ迅速に測定できる。したがって、後
段の脱塩装置の負荷量を決定する精度が向上する。
Further, the present invention relates to a method for measuring the concentration of carbonic acid in treated water of an ultraviolet oxidizing apparatus, wherein the treated water is diluted with high-purity water, and the carbonate ion is calculated from the value of the conductivity of the diluted liquid. The present invention provides a method for measuring the concentration. ADVANTAGE OF THE INVENTION According to this invention, the concentration of carbonic acid in the treated water of an ultraviolet oxidation device can be measured quickly and simply. Therefore, the accuracy of determining the load of the subsequent desalination apparatus is improved.

【0009】[0009]

【発明の実施の形態】次に、本発明の第1の実施の形態
における炭酸濃度測定方法について、図面を参照して説
明する。図1は、本発明の第1の実施の形態における炭
酸濃度測定装置10を組み込んだ一部の純水製造装置9
を示すブロック図である。純水製造装置9は、逆浸透膜
装置1と、脱塩装置2とから構成される。被処理水は逆
浸透膜装置1に供給され、有機物や微粒子が除去され
る。次いで、透過水はイオン交換樹脂や電気式脱イオン
水製造装置などの脱塩装置2に供給され処理されて純水
となる。
Next, a method of measuring a carbon dioxide concentration according to a first embodiment of the present invention will be described with reference to the drawings. FIG. 1 shows a partial pure water producing apparatus 9 incorporating a carbon dioxide concentration measuring apparatus 10 according to the first embodiment of the present invention.
FIG. The pure water production device 9 includes a reverse osmosis membrane device 1 and a desalination device 2. The water to be treated is supplied to the reverse osmosis membrane device 1 to remove organic substances and fine particles. Next, the permeated water is supplied to a desalination device 2 such as an ion-exchange resin or an electric deionized water producing device, where it is treated to become pure water.

【0010】次に、逆浸透膜装置1の透過水の炭酸濃度
を測定する。すなわち、逆浸透膜装置1の透過水の一部
は、試料水として炭酸濃度測定装置10に導かれる。逆
浸透膜装置1の透過水の水質としては、典型的には炭酸
約10ppm 、Na2ppm 以下、Ca0.5ppm 以下、M
g0.5ppm 以下、鉱酸2ppm 以下である。炭酸濃度測
定装置10は、水素イオン形強酸性陽イオン交換樹脂塔
3及び試料水流量検出部4を備えた試料水導入配管21
と、これに合流する希釈水流量検出部6を備えた希釈水
注入配管22と、希釈された試料水の導電率を測定する
導電率計5と、該二つの流量検出部4、6と該導電率計
5の信号から試料中の炭酸濃度を算出する演算部7と、
算出した炭酸濃度を表示する表示部8と、から構成され
ている。まず、試料水は試料水導入配管21を通して水
素イオン形強酸性陽イオン交換樹脂塔3に供給される。
ここで、炭酸水素ナトリウムはナトリウムイオンがイオ
ン交換されることにより、炭酸となる。水素イオン形強
酸性陽イオン交換樹脂塔3の出口水は希釈水注入配管2
2を通して供給される希釈水と合流され、導電率検出部
5で希釈された試料水の導電率が測定される。希釈水と
しては、高純度水を用いればよく、例えば抵抗率10M
Ω・cm以上、特に17.5MΩ・cm以上の純水が好まし
い。また、水素イオン形強酸性陽イオン交換樹脂塔3の
設置位置としては、上記の他、試料水と希釈水の合流点
から導電率計5までの間としてもよい。
Next, the concentration of carbonic acid in the permeated water of the reverse osmosis membrane device 1 is measured. That is, a part of the permeated water of the reverse osmosis membrane device 1 is guided to the carbon dioxide concentration measuring device 10 as sample water. The water quality of the permeated water of the reverse osmosis membrane device 1 is typically about 10 ppm of carbon dioxide, 2 ppm or less of Na, 0.5 ppm or less of Ca, M
g 0.5 ppm or less and mineral acid 2 ppm or less. The carbonic acid concentration measuring device 10 includes a sample water introduction pipe 21 provided with a hydrogen ion type strongly acidic cation exchange resin tower 3 and a sample water flow rate detection unit 4.
A diluting water injection pipe 22 having a diluting water flow detecting unit 6 to be joined thereto, a conductivity meter 5 for measuring the conductivity of the diluted sample water, and the two flow detecting units 4 and 6; A calculation unit 7 for calculating the concentration of carbonic acid in the sample from the signal of the conductivity meter 5,
A display unit 8 for displaying the calculated carbon dioxide concentration. First, the sample water is supplied to the hydrogen ion type strongly acidic cation exchange resin tower 3 through the sample water introduction pipe 21.
Here, sodium hydrogen carbonate is converted to carbonic acid by ion exchange of sodium ions. The outlet water of the hydrogen ion type strongly acidic cation exchange resin tower 3 is diluted water injection pipe 2
The conductivity of the sample water that has been combined with the dilution water supplied through 2 and diluted by the conductivity detection unit 5 is measured. As the dilution water, high-purity water may be used.
Pure water of Ω · cm or more, especially 17.5 MΩ · cm or more is preferable. The installation position of the hydrogen ion type strongly acidic cation exchange resin tower 3 may be between the junction of the sample water and the dilution water and the conductivity meter 5 in addition to the above.

【0011】希釈倍率及び導電率の算出方法を次に示
す。図2a、図2b、図2cは炭酸濃度と、水の導電率
あるいは抵抗率との関係を示した図である。この関係図
は一般に知られており、純水に炭酸のみが溶解している
場合における水のイオン積、炭酸の解離平衡などから作
成されたものである。本第1の実施の形態における逆浸
透膜装置1の透過水の導電率は図2a中、A点で示され
る。すなわち、A点付近は炭酸濃度と導電率との関係が
飽和状態(傾斜のない平坦な曲線)にあり、わずかな導
電率の変動で炭酸濃度が大きく変わる誤差の大きい領域
にある。本発明においては、該試料水を高純度水で希釈
することにより、炭酸濃度の変化に対して、導電率の変
化が大きい、換言すれば、炭酸による導電率の寄与が大
きい濃度領域で導電率の測定を行うことができること、
更に、このような希釈により、低導電率の水にすること
で、導電率検出部に、より測定精度の高い抵抗率計を使
用することができることにより、炭酸濃度の定量精度の
向上が図られると共に、共存する他の陰イオンが導電率
(抵抗率)に影響しない濃度まで希釈されるので、共存
イオンによる妨害の少ない測定が可能である。希釈の程
度としては、例えば、図2a中、合流水の導電率が1.
25μS/cm以下(炭酸濃度が1ppm 以下)の領域に入る
ように希釈すればよく、好ましくは、図2b中、炭酸濃
度0.250ppm以下となるように希釈するとよく、より好ま
しくは、図2c中、合流水の抵抗率7.00〜17.00 MΩ・
cmの範囲(炭酸濃度0.0025〜0.0250ppm の範囲)となる
ように希釈すればよい。具体的には、逆浸透膜装置の透
過水を抵抗率18MΩ・cmの純水で希釈する場合、希釈
倍率は5〜4000倍程度である。
A method for calculating the dilution ratio and the conductivity will be described below. 2a, 2b and 2c are diagrams showing the relationship between the concentration of carbonic acid and the conductivity or resistivity of water. This relationship diagram is generally known, and is created from the ionic product of water and the dissociation equilibrium of carbonic acid when only carbonic acid is dissolved in pure water. The conductivity of the permeated water of the reverse osmosis membrane device 1 according to the first embodiment is indicated by a point A in FIG. 2A. That is, the vicinity of the point A is in a saturated state (flat curve with no slope) between the carbonic acid concentration and the electrical conductivity, and is in a region where there is a large error in which the carbonic acid concentration greatly changes due to a slight change in electrical conductivity. In the present invention, by diluting the sample water with high-purity water, the change in the conductivity is large with respect to the change in the carbonic acid concentration, in other words, the conductivity in the concentration region where the contribution of the conductivity by carbonic acid is large. Measurement of
Furthermore, by such dilution, by making water of low conductivity, it is possible to use a resistivity meter having higher measurement accuracy in the conductivity detection unit, thereby improving the quantitative accuracy of the carbonic acid concentration. At the same time, since other coexisting anions are diluted to a concentration that does not affect the conductivity (resistivity), measurement with less interference by coexisting ions is possible. As for the degree of dilution, for example, in FIG.
It may be diluted so as to fall within a region of 25 μS / cm or less (carbonic acid concentration is 1 ppm or less), preferably in FIG. 2b, so as to have a carbonic acid concentration of 0.250 ppm or less, and more preferably, in FIG. Joint water resistivity 7.00-17.00 MΩ
It may be diluted so as to be in the range of cm (the range of 0.0025 to 0.0250 ppm of carbon dioxide). Specifically, when the permeated water of the reverse osmosis membrane device is diluted with pure water having a resistivity of 18 MΩ · cm, the dilution ratio is about 5 to 4000 times.

【0012】導電率計5により求められた合流水の炭酸
濃度値は、演算部7に入力され試料水の炭酸濃度が算出
される。すなわち、試料水の炭酸濃度は合流水の導電率
から算出された炭酸濃度に、該試料水の希釈倍率である
(V1 +V2)/ V1 の値を乗じて算出される。V1(L/h)
は試料水の流量検出部4で求められる流量を示し、V
2(L/h)は希釈水の流量検出部6で求められる流量を示
す。また、該炭酸濃度値などは表示部8に表示される。
The carbonic acid concentration value of the combined water obtained by the conductivity meter 5 is input to the arithmetic unit 7 to calculate the carbonic acid concentration of the sample water. That is, the carbon dioxide concentration of the sample water is calculated by multiplying the carbon dioxide concentration calculated from the conductivity of the combined water by the value of (V 1 + V 2 ) / V 1 , which is the dilution factor of the sample water. V 1 (L / h)
Denotes the flow rate obtained by the sample water flow rate detection unit 4;
2 (L / h) indicates the flow rate obtained by the flow rate detection unit 6 for the dilution water. The carbonic acid concentration value and the like are displayed on the display unit 8.

【0013】本第1の実施の形態における炭酸濃度測定
方法によれば、逆浸透膜装置1の透過水中、後段の脱塩
装置2の負荷イオンとなる炭酸ガス、炭酸イオン及び炭
酸水素ナトリウムなどのうち、炭酸水素ナトリウムは、
水素イオン形強酸性陽イオン交換樹脂3により炭酸に変
化するため、導電率計5での測定値をより正確に炭酸濃
度へ変換できる。このため、後段の脱塩装置2の負荷量
を決定する精度が向上する。また、試料水中、炭酸以外
の陰イオン成分は炭酸濃度と比較して無視できる濃度で
あるが、高純度水の希釈によって該陰イオン成分は更に
低濃度となるため、導電率計5での測定精度がより高め
られる。
According to the method for measuring the concentration of carbonic acid in the first embodiment, the permeated water of the reverse osmosis membrane device 1 and the carbon dioxide, carbonate ion and sodium hydrogencarbonate which are the load ions of the subsequent desalination device 2 are used. Of which, sodium bicarbonate
Since the hydrogen ion type strongly acidic cation exchange resin 3 changes to carbonic acid, the value measured by the conductivity meter 5 can be more accurately converted to carbonic acid concentration. Therefore, the accuracy of determining the load of the subsequent desalination device 2 is improved. The anion component other than carbonic acid in the sample water has a negligible concentration as compared with the carbonic acid concentration. However, the concentration of the anion component is further reduced by dilution with high-purity water. Accuracy is further improved.

【0014】本発明の第2の実施の形態における炭酸濃
度測定方法について、図3を参照して説明する。図3
は、本発明の第2の実施の形態における炭酸濃度測定装
置20を組み込んだ一部の精製水製造装置19を示すブ
ロック図である。図1と同一の構成要素には同一の符号
を付してその説明を省略し、異なる点について主に述べ
る。すなわち、図3において図1と異なる点は、精製水
製造工程19が二次純水系の特定の工程である点及び炭
酸濃度測定装置20に水素イオン形強酸性陽イオン交換
樹脂塔を用いない点にある。精製水製造工程19は、例
えば半導体製造工程で使用される洗浄用超純水製造装置
の二次純水系の一部に使用されるもので、紫外線酸化装
置11と、精製カラム(カートリッジ式混床ポリッシャ
ー)12とから構成される。有機物を含有する被処理水
は185nm付近の波長を照射可能な紫外線酸化装置11
により、有機酸と炭酸に分解される。紫外線酸化装置1
1の処理水の一部は、試料水として炭酸濃度測定装置装
置20に導かれる。
A method for measuring the concentration of carbonic acid according to the second embodiment of the present invention will be described with reference to FIG. FIG.
FIG. 7 is a block diagram showing a part of a purified water producing apparatus 19 incorporating a carbon dioxide concentration measuring apparatus 20 according to a second embodiment of the present invention. The same components as those in FIG. 1 are denoted by the same reference numerals, description thereof will be omitted, and different points will be mainly described. That is, FIG. 3 differs from FIG. 1 in that the purified water production step 19 is a specific step of the secondary pure water system and that the hydrogen ion type strongly acidic cation exchange resin tower is not used in the carbon dioxide concentration measuring device 20. It is in. The purified water producing step 19 is used for a part of a secondary pure water system of a cleaning ultrapure water producing apparatus used in a semiconductor producing step, for example. Polisher 12). The water to be treated containing organic matter is irradiated with an ultraviolet oxidizer 11 capable of irradiating a wavelength around 185 nm.
, It is decomposed into organic acid and carbonic acid. UV oxidation device 1
A part of the treated water 1 is guided to the carbon dioxide concentration measuring device 20 as sample water.

【0015】次に、紫外線酸化装置11の処理水中の炭
酸濃度を測定する。紫外線酸化装置11の処理水の水質
としては、典型的には炭酸約0.05ppm 、その他の塩
類は0.005ppm 以下である。炭酸濃度装置測定装置
20は、試料水流量検出部4を備えた試料水導入配管2
1と、これに合流する希釈水流量検出部6を備えた希釈
水注入配管22と、希釈された試料水の導電率を測定す
る導電率計5と、該二つの流量検出部4、6と該導電率
計5の信号から試料中の炭酸濃度を算出する演算部7
と、算出した炭酸濃度を表示する表示部8と、から構成
されている。試料水導入配管21を通して供給される試
料水は、希釈水注入配管22を通して供給される希釈水
と合流され、導電率検出部5で合流水の導電率が測定さ
れる。以後の炭酸濃度測定方法は第1の実施の形態と同
様である。なお、紫外線酸化装置11の処理水を抵抗率
18MΩ・cmの純水で希釈する場合、希釈倍率は2〜2
0倍程度である。
Next, the concentration of carbonic acid in the treated water of the ultraviolet oxidation device 11 is measured. The quality of the treated water of the ultraviolet oxidizer 11 is typically about 0.05 ppm for carbonic acid and 0.005 ppm or less for other salts. The carbon dioxide concentration measuring device 20 includes a sample water introduction pipe 2 having a sample water flow rate detection unit 4.
1, a dilution water injection pipe 22 provided with a dilution water flow detecting unit 6 to be joined thereto, a conductivity meter 5 for measuring the conductivity of the diluted sample water, and the two flow detecting units 4, 6. A calculation unit 7 for calculating the concentration of carbonic acid in the sample from the signal of the conductivity meter 5
And a display unit 8 for displaying the calculated carbon dioxide concentration. The sample water supplied through the sample water introduction pipe 21 is combined with the dilution water supplied through the dilution water injection pipe 22, and the conductivity detection unit 5 measures the conductivity of the combined water. Subsequent methods for measuring the concentration of carbon dioxide are the same as in the first embodiment. When the treated water of the ultraviolet oxidizer 11 is diluted with pure water having a resistivity of 18 MΩ · cm, the dilution ratio is 2 to 2.
It is about 0 times.

【0016】本第2の実施の形態における炭酸濃度測定
方法によれば、紫外線酸化装置11の処理水中の炭酸濃
度を簡易な操作方法で、且つ迅速に求めることができ
る。このため、後段の精製カラム12の負荷量を決定す
る精度が向上する。
According to the method for measuring the concentration of carbonic acid in the second embodiment, the concentration of carbonic acid in the treated water of the ultraviolet oxidizing apparatus 11 can be quickly obtained by a simple operation method. Therefore, the accuracy of determining the load of the purification column 12 at the subsequent stage is improved.

【0017】本発明の炭酸濃度測定装置は、純水製造工
程の所望の場所に組み込まれて利用される。その利用例
について図4を参照して説明する。図4は本発明の炭酸
濃度測定装置10を組み込んだ純水製造装置29のブロ
ック図である。被処理水は、前段逆浸透膜装置13、後
段逆浸透膜装置1、脱塩装置2の順序で通水される。ま
た、前段逆浸透膜装置13と後段逆浸透膜装置1との接
合管23にアルカリを添加するアルカリ添加手段14を
設け、被処理水中の炭酸を中和する。また、後段逆浸透
膜装置1の出口水の一部を試料水として炭酸濃度測定装
置10に導入し、その測定結果を調節器15にフィード
バックして添加するアルカリ量を調整する。炭酸濃度測
定装置10は前記第1の実施の形態で用いたものと同様
のものが使用できる。また、アルカリ添加手段14とし
ては、図では省略するが、例えばアルカリ溶液貯槽と注
入ポンプで構成されるものであればよい。アルカリとし
ては、アルカリ金属、アミン類など水に溶解した時にア
ルカリ性を示す物質を任意に選択でき、例えば水酸化ナ
トリウム、水酸化カリウムが好ましい。
The carbon dioxide concentration measuring device of the present invention is used by being incorporated in a desired place in a pure water production process. An example of its use will be described with reference to FIG. FIG. 4 is a block diagram of a pure water producing apparatus 29 incorporating the carbon dioxide concentration measuring apparatus 10 of the present invention. The water to be treated is passed through the reverse osmosis membrane device 13, the reverse osmosis membrane device 1, and the desalination device 2 in this order. In addition, an alkali addition means 14 for adding alkali is provided in a joining pipe 23 between the first-stage reverse osmosis membrane device 13 and the second-stage reverse osmosis membrane device 1 to neutralize carbonic acid in the water to be treated. In addition, a part of the outlet water of the latter reverse osmosis membrane device 1 is introduced as sample water into the carbon dioxide concentration measuring device 10, and the measurement result is fed back to the controller 15 to adjust the amount of alkali to be added. As the carbon dioxide concentration measuring device 10, the same device as used in the first embodiment can be used. Although the alkali adding means 14 is not shown in the figure, any means may be used as long as the means comprises, for example, an alkaline solution storage tank and an injection pump. As the alkali, a substance which exhibits alkalinity when dissolved in water, such as an alkali metal or an amine, can be arbitrarily selected. For example, sodium hydroxide and potassium hydroxide are preferable.

【0018】本利用例によれば、前段逆浸透膜装置13
の透過水にアルカリを添加して、高pHとすることによ
り、後段逆浸透膜装置1で炭酸を効率よく除去すること
ができる。そして、原水変動などにより炭酸の量が増減
しても、炭酸濃度測定装置の測定値をフィードバックし
てアルカリ添加手段を制御するため、理想的なアルカリ
添加をすることができ、薬品類の無駄な消費がなくなる
と共に、後段逆浸透膜装置1の透過水のイオン量を最も
少ない値とすることができる。
According to this application example, the pre-stage reverse osmosis membrane device 13
By adding an alkali to the permeated water to increase the pH, carbon dioxide can be efficiently removed by the reverse osmosis membrane device 1 in the latter stage. Then, even if the amount of carbonic acid increases or decreases due to fluctuations in raw water, the measured value of the carbonic acid concentration measurement device is fed back to control the alkali adding means, so that ideal alkali addition can be performed, and waste of chemicals can be achieved. The consumption is eliminated, and the amount of ions in the permeated water of the latter reverse osmosis membrane device 1 can be set to the minimum value.

【0019】本利用例において、逆浸透膜装置は上記2
段の他、3段以上の多段としてもよい。この場合、炭酸
濃度測定装置10に導入する試料水の採取場所として
は、第2段目以降の逆浸透膜装置の処理水であればよ
い。
In this application example, the reverse osmosis membrane device is
In addition to stages, three or more stages may be provided. In this case, the place where the sample water to be introduced into the carbon dioxide concentration measuring device 10 is collected may be the treated water of the reverse osmosis membrane device in the second and subsequent stages.

【0020】[0020]

【実施例】次に、実施例を挙げて、本発明を更に具体的
に説明する。 実施例1 下記仕様の装置、機器類並びに希釈水を用い、図1に示
す炭酸濃度測定装置を構成した。なお、試料水は逆浸透
膜装置の透過水の典型的な組成を再現するため、大気中
の炭酸が飽和濃度で溶解し、炭酸濃度が0.5ppm で抵
抗率が1.2MΩ・cmの純水に、重炭酸ナトリウムを1
9.1ppm 、硝酸ナトリウムを1.37ppm 添加して、
予め炭酸濃度が約10ppm となるように調製したものを
使用した。試料水の流量は0.1L/h 、希釈水の流量は
300L/h (希釈倍率3001倍)とした。測定の結
果、合流水の抵抗率は15.5MΩ・cmであり、試料水
から算出される炭酸濃度は10.5ppm であり、実際の
値とよく近似していた。
Next, the present invention will be described more specifically with reference to examples. Example 1 The carbon dioxide concentration measuring device shown in FIG. 1 was configured by using the devices, devices and dilution water having the following specifications. In order to reproduce the typical composition of the permeated water of the reverse osmosis membrane apparatus, the sample water was dissolved in carbon dioxide in the atmosphere at a saturated concentration, and a pure carbon solution with a carbon dioxide concentration of 0.5 ppm and a resistivity of 1.2 MΩ · cm. One piece of sodium bicarbonate in water
Add 9.1 ppm, 1.37 ppm of sodium nitrate,
What was prepared beforehand so that the carbonic acid concentration was about 10 ppm was used. The flow rate of the sample water was 0.1 L / h, and the flow rate of the dilution water was 300 L / h (dilution factor 3001). As a result of the measurement, the resistivity of the combined water was 15.5 MΩ · cm, and the carbonic acid concentration calculated from the sample water was 10.5 ppm, which closely approximated the actual value.

【0021】(炭酸濃度測定装置) ・水素イオン形陽イオン交換樹脂塔;アンバーライトES
G-K 、通水流速SV100 ・導電率計;AQ−11(電気化学計器社製) ・流量測定部;微量流量センサー(日本フローセル社
製) ・希釈水;18.2MΩ・cmの純水 ・演算部及び表示部;パーソナルコンピュータ
(Carbonic acid concentration measuring device) Hydrogen ion type cation exchange resin tower; Amberlite ES
GK, water flow velocity SV100 ・ Conductivity meter; AQ-11 (manufactured by Electrochemical Instruments) ・ Flow measurement unit; trace flow sensor (manufactured by Nippon Flowcell) ・ Dilution water: pure water of 18.2 MΩ · cm ・ Calculation unit And display unit; personal computer

【0022】比較例1 水素イオン形陽イオン交換樹脂塔を省略した以外は、実
施例1と同様の方法により行った。測定の結果、合流水
の抵抗率は17.2MΩ・cmであり、本抵抗率から算出
される試料水の炭酸濃度は3.96ppm であり、実施例
1と比較して、誤差が大であった。
Comparative Example 1 The same procedure as in Example 1 was carried out except that the hydrogen ion type cation exchange resin tower was omitted. As a result of the measurement, the resistivity of the combined water was 17.2 MΩ · cm, and the carbonic acid concentration of the sample water calculated from the resistivity was 3.96 ppm, and the error was larger than that in Example 1. Was.

【0023】実施例2 超純水製造装置の二次純水系における紫外線酸化装置の
処理水の典型的な組成を再現するため、試料水として、
TOCが1.00ppb で抵抗率が18.2MΩ・cmの超
純水に、メタノールを添加して、TOC濃度を19.2
4ppb とし、紫外線酸化装置(TDFL-4;千代田工販社
製)に照射量0.48kW・h/m3で通水して、TOC濃度
1.54ppb 、抵抗率4.12MΩ・cmの処理水を試料
水としたこと、水素イオン形強酸性陽イオン交換樹脂塔
を省略したこと、及び希釈水流量を減少させ、希釈倍率
を5倍としたこと以外は、実施例1と同様の方法で行っ
た。上記紫外線酸化装置前後のTOCの減少分がすべて
炭酸に分解されたとすると、0.0649ppm の炭酸が
処理水に含まれる計算となる。測定の結果、合流水の抵
抗率は10.2MΩ・cmであり、炭酸濃度は0.063
4ppm であり、よく近似していた。
Example 2 In order to reproduce a typical composition of the treated water of the ultraviolet oxidizing apparatus in the secondary pure water system of the ultrapure water producing apparatus,
Methanol is added to ultrapure water having a TOC of 1.00 ppb and a resistivity of 18.2 MΩ · cm to reduce the TOC concentration to 19.2 MΩ · cm.
4 ppb, water was passed through an ultraviolet oxidizer (TDFL-4; manufactured by Chiyoda Kohan Co., Ltd.) at an irradiation dose of 0.48 kW · h / m 3 to treat water having a TOC concentration of 1.54 ppb and a resistivity of 4.12 MΩ · cm The procedure was performed in the same manner as in Example 1 except that the sample water was used, the hydrogen ion type strongly acidic cation exchange resin tower was omitted, and the dilution water flow rate was reduced and the dilution ratio was set to 5 times. . Assuming that all the decrease in TOC before and after the ultraviolet oxidizing device is decomposed into carbonic acid, the calculated value is that 0.0649 ppm of carbonic acid is contained in the treated water. As a result of the measurement, the resistivity of the combined water was 10.2 MΩ · cm, and the carbonic acid concentration was 0.063.
It was 4 ppm, which was a good approximation.

【0024】[0024]

【発明の効果】本発明によれば、例えば、半導体デバイ
ス製造工程で使用される洗浄用純水の製造工程中、炭酸
濃度が比較的高く、且つ炭酸以外の塩類が少ない逆浸透
膜装置の透過水又は紫外線酸化装置の処理水中の該炭酸
濃度を、簡便な操作で、且つ迅速に測定することができ
る。このため、後段の脱塩装置の負荷量を決定する精度
が向上し、該脱塩装置の設計や交換時期など運転の指針
に有用な情報を提供することができる。
According to the present invention, for example, during the process of producing pure water for cleaning used in the process of producing semiconductor devices, the permeation of a reverse osmosis membrane apparatus having a relatively high carbon dioxide concentration and a small amount of salts other than carbon dioxide. The concentration of the carbonic acid in the water or the treated water of the ultraviolet oxidizing apparatus can be quickly measured by a simple operation. For this reason, the accuracy of determining the load of the subsequent desalination apparatus is improved, and useful information such as the design and replacement timing of the desalination apparatus can be provided.

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

【図1】本発明の第1の実施の形態における炭酸濃度測
定装置を組み込んだ純水製造装置のブロック図を示す。
FIG. 1 is a block diagram of a pure water producing apparatus incorporating a carbon dioxide concentration measuring apparatus according to a first embodiment of the present invention.

【図2】炭酸濃度と導電率又は抵抗率との関係を示す図
であり、図2aは横軸の炭酸濃度を0 〜10ppm とした
図、図2bは同様に横軸を0 〜1.0ppmとした図、図2c
は横軸を0 〜0.1ppmとした図である。
FIG. 2 is a graph showing the relationship between the carbon dioxide concentration and the electrical conductivity or resistivity. FIG. 2a is a graph in which the carbon dioxide concentration on the horizontal axis is 0 to 10 ppm, and FIG. Figure 2c
Is a diagram in which the horizontal axis is 0 to 0.1 ppm.

【図3】本発明の第2の実施の形態における炭酸濃度測
定装置を組み込んだ精製水製造装置のブロック図を示
す。
FIG. 3 shows a block diagram of a purified water producing apparatus incorporating a carbon dioxide concentration measuring apparatus according to a second embodiment of the present invention.

【図4】本発明の第1の実施の形態における炭酸濃度測
定装置を利用した純水製造装置のブロック図を示す。
FIG. 4 is a block diagram of a pure water producing apparatus using the carbon dioxide concentration measuring apparatus according to the first embodiment of the present invention.

【符号の説明】[Explanation of symbols]

1、13 逆浸透膜装置 2 脱塩装置 3 水素イオン形陽イオン交換樹脂 4、6 流量検出部 5 導電率計 7 演算部 8 表示部 9 純水製造装置 10、20 炭酸濃度測定装置 11 紫外線酸化装置 12 精製カラム 14 アルカリ添加手段 15 調節器 21 試料水導入配管 22 希釈水注入配管 1, 13 reverse osmosis membrane device 2 desalination device 3 hydrogen ion type cation exchange resin 4, 6 flow rate detection unit 5 conductivity meter 7 calculation unit 8 display unit 9 pure water production device 10, 20 carbon dioxide concentration measurement device 11 ultraviolet oxidation Apparatus 12 Purification column 14 Alkali addition means 15 Controller 21 Sample water introduction pipe 22 Dilution water injection pipe

Claims (5)

【特許請求の範囲】[Claims] 【請求項1】 逆浸透膜装置の透過水中の炭酸濃度を測
定する方法において、該透過水を、水素イオン形強酸性
陽イオン交換樹脂に接触させた後、該接触水を高純度水
で希釈し、その希釈液の導電率の値から炭酸イオンを算
出することを特徴とする炭酸濃度測定方法。
In a method for measuring the concentration of carbonic acid in permeated water of a reverse osmosis membrane device, the permeated water is contacted with a hydrogen ion type strongly acidic cation exchange resin, and then the contact water is diluted with high-purity water. And calculating a carbonate ion from the value of the conductivity of the diluted solution.
【請求項2】 紫外線酸化装置の処理水中の炭酸濃度を
測定する方法において、該処理水を高純度水で希釈し、
その希釈液の導電率の値から炭酸イオンを算出すること
を特徴とする炭酸濃度測定方法。
2. A method for measuring the concentration of carbonic acid in treated water of an ultraviolet oxidizer, wherein the treated water is diluted with high-purity water,
A method for measuring the concentration of carbonic acid, comprising calculating carbonate ions from the value of the conductivity of the diluent.
【請求項3】 紫外線酸化装置の処理水は、超純水製造
装置の二次純水系の紫外線酸化装置の処理水である請求
項2記載の炭酸濃度測定方法。
3. The method for measuring the concentration of carbonic acid according to claim 2, wherein the treated water of the ultraviolet oxidizing apparatus is treated water of a secondary pure water-based ultraviolet oxidizing apparatus of the ultrapure water producing apparatus.
【請求項4】 試料水流量検出部を備えた試料水導入配
管と、これに合流する希釈水流量検出部を備えた希釈水
注入配管と、希釈された試料水の導電率を測定する導電
率検出部と、該二つの流量検出部と該導電率検出部の信
号から試料水中の炭酸濃度を算出する演算部と、算出し
た炭酸濃度を表示する表示部と、を有することを特徴と
する炭酸濃度測定装置。
4. A sample water introduction pipe having a sample water flow rate detection section, a dilution water injection pipe having a dilution water flow rate detection section which joins the sample water introduction pipe, and a conductivity for measuring the conductivity of the diluted sample water. A carbon dioxide detector, comprising: a detector, a calculator for calculating the concentration of carbonic acid in the sample water from the signals of the two flow rate detectors and the conductivity detector, and a display for displaying the calculated carbonic acid concentration. Concentration measuring device.
【請求項5】 更に、前記試料水導入配管中、前記導電
率検出部までのいずれかの位置に水素イオン形強酸性陽
イオン交換樹脂塔を設置することを特徴とする請求項4
記載の炭酸濃度測定装置。
5. A hydrogen ion type strongly acidic cation exchange resin tower is installed at any position in the sample water introduction pipe up to the conductivity detecting section.
The carbon dioxide concentration measuring device according to the above.
JP7493198A 1998-03-09 1998-03-09 Method and apparatus for measurement of concentration of carbonic acid Pending JPH11258191A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP7493198A JPH11258191A (en) 1998-03-09 1998-03-09 Method and apparatus for measurement of concentration of carbonic acid

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP7493198A JPH11258191A (en) 1998-03-09 1998-03-09 Method and apparatus for measurement of concentration of carbonic acid

Publications (1)

Publication Number Publication Date
JPH11258191A true JPH11258191A (en) 1999-09-24

Family

ID=13561605

Family Applications (1)

Application Number Title Priority Date Filing Date
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Country Status (1)

Country Link
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Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2001201476A (en) * 2000-01-20 2001-07-27 Sumitomo Metal Ind Ltd Acid concentration meter and acid concentration measurement method
JP2012026912A (en) * 2010-07-26 2012-02-09 Atago:Kk Salinity concentration measuring instrument and salinity concentration measuring method
CN105999764A (en) * 2016-06-02 2016-10-12 中国科学院青海盐湖研究所 Ion enrichment method and ion enrichment device
CN115902004A (en) * 2022-11-08 2023-04-04 中科特肯(山东)智能科技有限公司 Measuring device and measuring method for conductivity of degassed hydrogen

Cited By (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2001201476A (en) * 2000-01-20 2001-07-27 Sumitomo Metal Ind Ltd Acid concentration meter and acid concentration measurement method
JP2012026912A (en) * 2010-07-26 2012-02-09 Atago:Kk Salinity concentration measuring instrument and salinity concentration measuring method
CN102495024A (en) * 2010-07-26 2012-06-13 株式会社爱宕 Salinity concentration measuring device and salinity concentration measuring method
CN102495024B (en) * 2010-07-26 2015-03-11 株式会社爱宕 Salinity concentration measuring device and salinity concentration measuring method
CN105999764A (en) * 2016-06-02 2016-10-12 中国科学院青海盐湖研究所 Ion enrichment method and ion enrichment device
CN115902004A (en) * 2022-11-08 2023-04-04 中科特肯(山东)智能科技有限公司 Measuring device and measuring method for conductivity of degassed hydrogen
CN115902004B (en) * 2022-11-08 2023-08-18 中科特肯(山东)智能科技有限公司 Measurement device and measurement method for conductivity of degassed hydrogen

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