JPS6243134B2 - - Google Patents
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- Publication number
- JPS6243134B2 JPS6243134B2 JP54124431A JP12443179A JPS6243134B2 JP S6243134 B2 JPS6243134 B2 JP S6243134B2 JP 54124431 A JP54124431 A JP 54124431A JP 12443179 A JP12443179 A JP 12443179A JP S6243134 B2 JPS6243134 B2 JP S6243134B2
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- Japan
- Prior art keywords
- measured
- gas
- component
- electrode
- concentration
- Prior art date
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Links
- 238000000034 method Methods 0.000 claims description 66
- 239000012071 phase Substances 0.000 claims description 13
- 238000004868 gas analysis Methods 0.000 claims description 6
- 239000007791 liquid phase Substances 0.000 claims description 6
- 230000003068 static effect Effects 0.000 claims description 4
- 239000007789 gas Substances 0.000 description 52
- MWUXSHHQAYIFBG-UHFFFAOYSA-N nitrogen oxide Inorganic materials O=[N] MWUXSHHQAYIFBG-UHFFFAOYSA-N 0.000 description 38
- 238000012545 processing Methods 0.000 description 31
- RAHZWNYVWXNFOC-UHFFFAOYSA-N Sulphur dioxide Chemical compound O=S=O RAHZWNYVWXNFOC-UHFFFAOYSA-N 0.000 description 30
- 238000001514 detection method Methods 0.000 description 23
- 239000007788 liquid Substances 0.000 description 14
- 238000010521 absorption reaction Methods 0.000 description 13
- 238000005259 measurement Methods 0.000 description 13
- 239000000243 solution Substances 0.000 description 13
- 230000008569 process Effects 0.000 description 11
- 238000012935 Averaging Methods 0.000 description 9
- 239000000126 substance Substances 0.000 description 9
- 238000005868 electrolysis reaction Methods 0.000 description 7
- 238000009499 grossing Methods 0.000 description 6
- QSHDDOUJBYECFT-UHFFFAOYSA-N mercury Chemical compound [Hg] QSHDDOUJBYECFT-UHFFFAOYSA-N 0.000 description 6
- 229910052753 mercury Inorganic materials 0.000 description 6
- 238000004458 analytical method Methods 0.000 description 5
- 239000012064 sodium phosphate buffer Substances 0.000 description 5
- LMSDCGXQALIMLM-UHFFFAOYSA-N 2-[2-[bis(carboxymethyl)amino]ethyl-(carboxymethyl)amino]acetic acid;iron Chemical compound [Fe].OC(=O)CN(CC(O)=O)CCN(CC(O)=O)CC(O)=O LMSDCGXQALIMLM-UHFFFAOYSA-N 0.000 description 4
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 description 4
- NBIIXXVUZAFLBC-UHFFFAOYSA-N Phosphoric acid Chemical compound OP(O)(O)=O NBIIXXVUZAFLBC-UHFFFAOYSA-N 0.000 description 4
- 238000010586 diagram Methods 0.000 description 4
- 239000012528 membrane Substances 0.000 description 4
- CWYNVVGOOAEACU-UHFFFAOYSA-N Fe2+ Chemical compound [Fe+2] CWYNVVGOOAEACU-UHFFFAOYSA-N 0.000 description 3
- LSNNMFCWUKXFEE-UHFFFAOYSA-N Sulfurous acid Chemical group OS(O)=O LSNNMFCWUKXFEE-UHFFFAOYSA-N 0.000 description 3
- 230000002159 abnormal effect Effects 0.000 description 3
- 238000007796 conventional method Methods 0.000 description 3
- 230000001186 cumulative effect Effects 0.000 description 3
- 230000002452 interceptive effect Effects 0.000 description 3
- 230000001590 oxidative effect Effects 0.000 description 3
- NLKNQRATVPKPDG-UHFFFAOYSA-M potassium iodide Chemical compound [K+].[I-] NLKNQRATVPKPDG-UHFFFAOYSA-M 0.000 description 3
- 238000001179 sorption measurement Methods 0.000 description 3
- LEAHFJQFYSDGGP-UHFFFAOYSA-K trisodium;dihydrogen phosphate;hydrogen phosphate Chemical compound [Na+].[Na+].[Na+].OP(O)([O-])=O.OP([O-])([O-])=O LEAHFJQFYSDGGP-UHFFFAOYSA-K 0.000 description 3
- UFHFLCQGNIYNRP-UHFFFAOYSA-N Hydrogen Chemical compound [H][H] UFHFLCQGNIYNRP-UHFFFAOYSA-N 0.000 description 2
- 229910000147 aluminium phosphate Inorganic materials 0.000 description 2
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 2
- 238000005341 cation exchange Methods 0.000 description 2
- 238000001903 differential pulse voltammetry Methods 0.000 description 2
- 238000009792 diffusion process Methods 0.000 description 2
- 239000001257 hydrogen Substances 0.000 description 2
- 229910052739 hydrogen Inorganic materials 0.000 description 2
- 230000006872 improvement Effects 0.000 description 2
- 239000000463 material Substances 0.000 description 2
- 229910052757 nitrogen Inorganic materials 0.000 description 2
- 239000001301 oxygen Substances 0.000 description 2
- 229910052760 oxygen Inorganic materials 0.000 description 2
- 229920006395 saturated elastomer Polymers 0.000 description 2
- 239000004065 semiconductor Substances 0.000 description 2
- 230000035945 sensitivity Effects 0.000 description 2
- 238000004832 voltammetry Methods 0.000 description 2
- UOMQUZPKALKDCA-UHFFFAOYSA-K 2-[2-[bis(carboxylatomethyl)amino]ethyl-(carboxymethyl)amino]acetate;iron(3+) Chemical compound [Fe+3].OC(=O)CN(CC([O-])=O)CCN(CC([O-])=O)CC([O-])=O UOMQUZPKALKDCA-UHFFFAOYSA-K 0.000 description 1
- MGWGWNFMUOTEHG-UHFFFAOYSA-N 4-(3,5-dimethylphenyl)-1,3-thiazol-2-amine Chemical compound CC1=CC(C)=CC(C=2N=C(N)SC=2)=C1 MGWGWNFMUOTEHG-UHFFFAOYSA-N 0.000 description 1
- RWSOTUBLDIXVET-UHFFFAOYSA-N Dihydrogen sulfide Chemical compound S RWSOTUBLDIXVET-UHFFFAOYSA-N 0.000 description 1
- KCXVZYZYPLLWCC-UHFFFAOYSA-N EDTA Chemical compound OC(=O)CN(CC(O)=O)CCN(CC(O)=O)CC(O)=O KCXVZYZYPLLWCC-UHFFFAOYSA-N 0.000 description 1
- BQCADISMDOOEFD-UHFFFAOYSA-N Silver Chemical compound [Ag] BQCADISMDOOEFD-UHFFFAOYSA-N 0.000 description 1
- NINIDFKCEFEMDL-UHFFFAOYSA-N Sulfur Chemical compound [S] NINIDFKCEFEMDL-UHFFFAOYSA-N 0.000 description 1
- 230000004913 activation Effects 0.000 description 1
- 239000012491 analyte Substances 0.000 description 1
- 230000003197 catalytic effect Effects 0.000 description 1
- 238000011161 development Methods 0.000 description 1
- 230000018109 developmental process Effects 0.000 description 1
- 238000010790 dilution Methods 0.000 description 1
- 239000012895 dilution Substances 0.000 description 1
- 230000000694 effects Effects 0.000 description 1
- 238000000840 electrochemical analysis Methods 0.000 description 1
- 239000003792 electrolyte Substances 0.000 description 1
- 238000002474 experimental method Methods 0.000 description 1
- 229910000037 hydrogen sulfide Inorganic materials 0.000 description 1
- HXJNJLSAZAGIBV-UHFFFAOYSA-M iodosilver silver Chemical compound [Ag].I[Ag] HXJNJLSAZAGIBV-UHFFFAOYSA-M 0.000 description 1
- 238000000691 measurement method Methods 0.000 description 1
- 150000002730 mercury Chemical class 0.000 description 1
- 239000000203 mixture Substances 0.000 description 1
- JCXJVPUVTGWSNB-UHFFFAOYSA-N nitrogen dioxide Inorganic materials O=[N]=O JCXJVPUVTGWSNB-UHFFFAOYSA-N 0.000 description 1
- 230000003287 optical effect Effects 0.000 description 1
- BASFCYQUMIYNBI-UHFFFAOYSA-N platinum Chemical compound [Pt] BASFCYQUMIYNBI-UHFFFAOYSA-N 0.000 description 1
- 238000002360 preparation method Methods 0.000 description 1
- 238000003672 processing method Methods 0.000 description 1
- 238000011002 quantification Methods 0.000 description 1
- 230000001105 regulatory effect Effects 0.000 description 1
- 230000004044 response Effects 0.000 description 1
- 238000000926 separation method Methods 0.000 description 1
- 229910052709 silver Inorganic materials 0.000 description 1
- 239000004332 silver Substances 0.000 description 1
- 229910052717 sulfur Inorganic materials 0.000 description 1
- 239000011593 sulfur Substances 0.000 description 1
- XTQHKBHJIVJGKJ-UHFFFAOYSA-N sulfur monoxide Chemical class S=O XTQHKBHJIVJGKJ-UHFFFAOYSA-N 0.000 description 1
- 229910052815 sulfur oxide Inorganic materials 0.000 description 1
- 239000000725 suspension Substances 0.000 description 1
- 238000010408 sweeping Methods 0.000 description 1
- 238000009423 ventilation Methods 0.000 description 1
Landscapes
- Other Investigation Or Analysis Of Materials By Electrical Means (AREA)
- Investigating Or Analyzing Materials By The Use Of Electric Means (AREA)
Description
【発明の詳細な説明】
本発明は気相中に含有される被測定成分の濃度
測定方法に関し、より詳細には静止電極に電位掃
引法を用いて電圧を印加する、動的な電気化学的
ガス分析法に関する。DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a method for measuring the concentration of a component to be measured contained in a gas phase, and more specifically to a method for measuring the concentration of a component to be measured contained in a gas phase. Concerning gas analysis methods.
従来、電気化学的手段でガス中の含有成分を検
出、定量するには下記の方法が用いられている。 Conventionally, the following method has been used to detect and quantify components contained in gas by electrochemical means.
(イ) 定電位電解法。これは一定電位に保持された
電極上でガスを直接または液中に溶解したのち
に電解する方法である。(a) Constant potential electrolysis method. This is a method in which gas is electrolyzed directly or after being dissolved in a liquid on an electrode held at a constant potential.
この方法では、ガス検出の選択性は電極の触
媒作用、含有成分の電極に対する活性化過電
圧、ある種の多孔質膜に対するガス成分の選択
透過性によつてもたらされるが、いずれにして
も選択性が多少なりとも向上される程度にすぎ
ず、かつ、原理的に検出器に選択性を持たせる
ものではない。 In this method, the selectivity of gas detection is provided by the catalytic action of the electrodes, the activation overpotential of the contained components with respect to the electrodes, and the permselectivity of the gas components with respect to certain porous membranes; This is only a slight improvement in the sensitivity of the detector, and does not, in principle, impart selectivity to the detector.
したがつて、電極電位をある値に設定したと
しても、なお分析に干渉してくる成分に対して
は試料ガスを検出器に導く前に、予め除去処理
をしておかねばならない。 Therefore, even if the electrode potential is set to a certain value, components that interfere with the analysis must be removed before the sample gas is introduced to the detector.
(ロ) 溶液導電率法。この方法は分析目的成分を溶
液に溶かし、交流ブリツジ法などで溶液の導電
率変化から濃度を求める方法である。(b) Solution conductivity method. In this method, the target component to be analyzed is dissolved in a solution, and the concentration is determined from changes in the conductivity of the solution using the AC bridge method or the like.
しかし、原理上から、溶解してイオン化する
ガス成分はすべて検出されるので選択性は悪
く、用途は限定されている。 However, in principle, all gas components that dissolve and become ionized are detected, so the selectivity is poor and its applications are limited.
(ハ) ヨードメトリーなど。これは試料ガスと酸化
還元性物質とを接触させ、生成した酸化態また
は還元態の酸化還元性物質をガルバニセルなど
を用いて定量し、ガス濃度を測定する方法であ
る。(c) Iodometry etc. This is a method in which a sample gas and a redox substance are brought into contact, and the generated oxidized or reduced redox substance is quantified using a galvanic cell or the like to measure the gas concentration.
したがつて、より強力な酸化性または還元性
物質が存在すると直接的な干渉成分となる。 Therefore, the presence of more powerful oxidizing or reducing substances becomes a direct interfering component.
(ニ) 半導体センサーなどを用いる方法。半導体セ
ンサーへのガス吸着によつて生じる電導度変化
などを検知し、ガス濃度を知る方法であるが、
ガス吸着が物理的吸着で選択性にとぼしく化学
的な選択性をもつ検出器とすることが困難であ
る。(d) A method using semiconductor sensors, etc. This is a method of determining gas concentration by detecting changes in conductivity caused by gas adsorption on a semiconductor sensor.
Gas adsorption is physical adsorption and has poor selectivity, making it difficult to create a detector with chemical selectivity.
上述のように(イ)〜(ニ)の従来の方法は、いずれも
選択性に問題があり、かつ、分析目的成分の種類
の増加につれて検出器の数も増加する。 As mentioned above, all of the conventional methods (a) to (d) have problems with selectivity, and the number of detectors increases as the types of components to be analyzed increase.
これは従来の方法がいわば静的な定電位電解法
という方法や特定の酸化還元物質を用いるガス分
析法であることに起因している。 This is due to the fact that the conventional methods are a so-called static constant potential electrolysis method and a gas analysis method using a specific redox substance.
本発明はこれらの欠点を解消せんとするもので
あつて、検出の選択性を著るしく向上せしめると
同時に、一つの検出器で複数の成分の測定が可能
な、いわば動的なガス分析法を提供せんとするも
のである。 The present invention aims to eliminate these drawbacks, and provides a so-called dynamic gas analysis method that significantly improves detection selectivity and at the same time allows measurement of multiple components with one detector. We aim to provide the following.
本発明はかかる目的達成のために、液相および
電極を静止系とし、この静止電極に電位掃引法に
よつて電圧を印加すると共に、このときの前記電
極からの電解電流値をデータ処理して得られたボ
ルタングラム中の被測定成分に基づく波の高さ、
またはピータ面積を計測して気相中の被測定成分
濃度を測定せんとするものである。 In order to achieve such an object, the present invention uses a stationary system with a liquid phase and an electrode, applies a voltage to the stationary electrode by a potential sweep method, and processes the electrolytic current value from the electrode at this time. Wave height based on the measured component in the obtained voltamgram,
Alternatively, the concentration of the component to be measured in the gas phase is measured by measuring the Peter area.
以下本発明の実施例を図面にもとづき説明す
る。 Embodiments of the present invention will be described below based on the drawings.
本発明で使用する分析装置は、たとえば第1図
に示す系統図で示され、その主要部は吸収液2、
検出電極1、対極4等からなる検出部と、直流電
圧およびそれに重畳される交流波、パルス等を印
加、掃引して、電極を流れる電流を検出し、それ
を出力する定電位電解装置9、ポーラログラフ8
等からなるボルタングラフ部分と、さらに出力さ
れたデータを処理して、分析目的成分濃度を表示
し、かつ、ボルタングラフ部分を制御するボルタ
ングラフ制御およびデータ処理装置10、プリン
タ11等からなるデータ処理部から構成されてい
る。 The analyzer used in the present invention is shown, for example, in the system diagram shown in FIG. 1, and its main parts are an absorption liquid 2,
a detection unit consisting of a detection electrode 1, a counter electrode 4, etc.; a constant potential electrolysis device 9 that applies and sweeps a DC voltage and an AC wave superimposed thereon, a pulse, etc., detects a current flowing through the electrode, and outputs it; polarograph 8
It is composed of a voltam graph section consisting of a voltamic graph section, etc., and a data processing section consisting of a voltamic graph control and data processing device 10, a printer 11, etc. that further processes the output data, displays the concentration of the component to be analyzed, and controls the voltamgraph section. has been done.
そして、かかる分析装置を用いて気相中の被測
定成分濃度を測定するには、吸収液2に試料ガス
を供給して試料ガス中の被測定成分を吸収液2に
溶解、乳濁、または懸濁などによつて移相させた
後に静止系とされている検出電極1に電位掃引法
によつて電圧の印加を繰り返し行なう。 To measure the concentration of a component to be measured in the gas phase using such an analyzer, a sample gas is supplied to the absorption liquid 2, and the component to be measured in the sample gas is dissolved, emulsified, or After phase shifting by suspension or the like, a voltage is repeatedly applied to the detection electrode 1, which is considered to be a stationary system, by a potential sweep method.
すなわち、電極に印加させる電圧、つまり電極
電位がある範囲内を繰り返し掃引されるようにす
る。 That is, the voltage applied to the electrodes, that is, the electrode potential, is repeatedly swept within a certain range.
この電位掃引と同時に、検出電極1における電
解電流の値をボルタングラフ制御およびデータ処
理装置10によつてデータ処理して分析目的成分
に対応する波高もしくはピーク面積を得る。 Simultaneously with this potential sweep, the value of the electrolytic current in the detection electrode 1 is data-processed by the voltamgraph control and data processing device 10 to obtain the wave height or peak area corresponding to the component to be analyzed.
一方、被測定成分濃度が既知の標準ガスを用い
て、あらかじめ上記と同様の方法によつてボルタ
ングラムを求め、被測定成分の濃度とボルタング
ラムの波高との関係、または既知の被測定成分濃
度とボルタングラムの面積との関係を、あらかじ
めボルタングラフ制御およびデータ処理装置10
に記憶させて置く。 On the other hand, using a standard gas with a known concentration of the component to be measured, a voltamgram is obtained in advance by the same method as above, and the relationship between the concentration of the component to be measured and the wave height of the voltamgram, or the concentration of the component to be measured is known. The relationship between
Store it in memory.
次に、上記濃度未知被測定成分のボルタングラ
ムの波高または面積を上記標準ガスから求めた値
と比較すれば被測定成分の試料ガス中の濃度を知
ることができる。 Next, by comparing the wave height or area of the voltamgram of the component to be measured with unknown concentration with the value determined from the standard gas, the concentration of the component to be measured in the sample gas can be determined.
ここで本発明の方法の特徴の一つである電位掃
引法による電圧の印加は、たとえば第1図に示す
ように検出電極1を微分パルスポーラログラフ8
に接続し、ボルタングラフ制御およびデータ処理
装置10によつて外部から制御しながら検出電極
1にパルスを加え、パルス印加直前の電解電流
と、パルス印加後の電解電流との差を求める微分
パルス法によつて行なうことができるが、これの
みに限定されるのではなく、被測定成分の種類に
応じて電圧を印加する際の印加波形として直流三
角波のみを印加する直流法、直流三角波に交流を
重畳する交流法または直流三角波に矩形波を重畳
する矩形波法などを適宜用いることができる。 Here, the application of voltage by the potential sweep method, which is one of the characteristics of the method of the present invention, is performed by moving the detection electrode 1 to a differential pulse polarograph 8 as shown in FIG.
A pulse is applied to the detection electrode 1 under external control by the voltamgraph control and data processing device 10, and the differential pulse method is used to calculate the difference between the electrolytic current immediately before the pulse is applied and the electrolytic current after the pulse is applied. However, the method is not limited to this method, and the method is not limited to this method. Depending on the type of component to be measured, a DC method in which only a DC triangular wave is applied as the applied waveform when applying a voltage, and an AC method in which AC is superimposed on a DC triangular wave. An alternating current method in which a rectangular wave is superimposed on a direct current triangular wave, or a rectangular wave method in which a rectangular wave is superimposed on a direct current triangular wave, etc. can be used as appropriate.
又、電位掃引法によつて印加される電圧の範囲
は、上記した電圧印加方法の種類や、被測定成分
の種類に応じて種々選ぶことができるが、たとえ
ばイオウ酸化物や窒素酸化物を被測定成分とする
ときの印加電圧範囲は参照電極(飽和甘汞電極)
電位に対して通常では−0.3V〜−1.1Vの範囲で
ある。 The range of the voltage applied by the potential sweep method can be selected depending on the type of voltage application method described above and the type of component to be measured. The applied voltage range when measuring the component is the reference electrode (saturated Amane electrode).
The potential is usually in the range of -0.3V to -1.1V.
更に、一般にボルタンメトリーの場合、定常的
ないしは準定常的なデータを得るために、回転電
極や滴下水銀電極などの、いわゆる水力学的な電
極系を用いて電極−溶液界面の被電解物質の拡散
層の厚さを安定化させるのが常法である。 Furthermore, in general, in the case of voltammetry, in order to obtain stationary or quasi-stationary data, a so-called hydraulic electrode system such as a rotating electrode or a dropping mercury electrode is used to create a diffusion layer of the electrolyte at the electrode-solution interface. The conventional method is to stabilize the thickness of the material.
しかし、本発明の方法では従来の定電位電解法
と同じく、被電解物質の拡散層の厚さを定常化す
る処置をとらずに静止系としている。 However, in the method of the present invention, like the conventional constant potential electrolysis method, a static system is used without taking any measures to stabilize the thickness of the diffusion layer of the substance to be electrolyzed.
このため、一面では検出部が外部からの振動な
どの影響を受け易いが、ボルタングラフ制御およ
びデータ処理装置10によつて、下記のように電
解電流値をデータ処理してデータのばらつきを調
整している。 For this reason, on the one hand, the detection section is easily affected by external vibrations, etc., but by using the voltamgraph control and data processing device 10, the electrolytic current value is data processed as described below to adjust the data variation. There is.
すなわち、本発明の方法におけるデータ処理は
通常では(イ)異状データの除去、(ロ)平滑化処理およ
び(ハ)積算平均化処理の3種類の方法によつて行な
う。 That is, data processing in the method of the present invention is normally performed by three methods: (a) removal of abnormal data, (b) smoothing processing, and (c) cumulative averaging processing.
(イ)は電位掃引を繰り返したときに前回のデータ
との差が異状に大きい値を除去することであり、
通常では50%以上の差があるデータを排除する処
理である。 (a) is to remove values that have an abnormally large difference from the previous data when potential sweeps are repeated;
Normally, this process eliminates data with a difference of 50% or more.
(ロ)はたとえば11点数をとる重みつき移動平均に
よる平滑化処理であり、(イ)と組合せて行なうこと
もできる。 (B) is a smoothing process using a weighted moving average that takes 11 points, for example, and can also be performed in combination with (B).
(ハ)はたとえば掃引回数4回ごとの積算平均化に
よる処理であり、(イ)と組合せて行なうこともでき
る。 (C) is a process of integrating and averaging every four sweeps, and can also be performed in combination with (B).
これらデータ処理は測定時の環境に起因するボ
ルタングラムへのノイズ発生に対応して(イ)〜(ハ)の
全種類を用いることもあり、測定環境が良好でノ
イズ発生が少ない場合には、(イ),(ロ)を省略して(ハ)
単独の処理のみでも良い。 All types of data processing (a) to (c) may be used in response to noise generation in the voltamgram caused by the environment at the time of measurement.If the measurement environment is good and there is little noise generation, (a) and (b) are omitted and (c)
It is also possible to perform only a single process.
更にノイズがほとんど現われない場合には、(ハ)
の積算平均化処理も前後2回の電位掃引の平均だ
けで十分満足できる測定値を得ることができる。 Furthermore, if there is almost no noise, (c)
In the integrated averaging process, it is possible to obtain a sufficiently satisfactory measured value by just averaging two potential sweeps before and after.
なお、吸収液2は試料ガス中の被測定成分の種
類に応じて適宜選ぶことができ、被測定成分を溶
解せしめるか、又は被測定成分と吸収液2の成分
との間に化学的結合、たとえば錯体を形成せしめ
て被測定成分を吸収液2に移相せしめるか、ある
いは被測定成分を乳濁もしくは懸濁せしめ得るも
のである。 The absorption liquid 2 can be selected as appropriate depending on the type of the component to be measured in the sample gas, and either dissolves the component to be measured or creates a chemical bond between the component to be measured and the component of the absorption liquid 2. For example, the component to be measured can be phase-shifted into the absorption liquid 2 by forming a complex, or the component to be measured can be emulsified or suspended.
更に、被測定成分は気相中に含有される如何な
るものでも測定対象とすることができるが、通常
ではイオウ酸化物、窒素酸化物、又は硫化水素な
どであり、又、測定可能な下限は気相中の被測定
成分含有率で通常数ppmのレベルである。 Furthermore, the component to be measured can be anything contained in the gas phase, but it is usually sulfur oxides, nitrogen oxides, or hydrogen sulfide, and the measurable lower limit is the gas phase. The content of the component to be measured in the phase is usually at the level of several ppm.
上述のように、本発明の方法は静止電極に電位
掃引法を用いて電位を印加する、動的な方法なの
で、定電位電解法のような静的な測定法とは異な
つた、すぐれた諸効果が奏せられる。 As mentioned above, the method of the present invention is a dynamic method in which a potential is applied to a stationary electrode using a potential sweep method, so it has various advantages that are different from static measurement methods such as potentiostatic electrolysis. The effect is produced.
まず、電位掃引を繰り返し行なつて複数のデー
タを得、このデータをたとえば平滑化処理およ
び/又は積算平均化処理することによつて分析精
度を向上することができる。 First, the accuracy of analysis can be improved by repeatedly performing potential sweeps to obtain a plurality of data, and subjecting this data to smoothing processing and/or cumulative averaging processing, for example.
とくに近年、発達の著るしいマイクロコンピユ
ータを用いれば、データのデジタル処理が容易で
あり、分析精度の向上は一層促進される。 In particular, if microcomputers, which have been significantly developed in recent years, are used, digital processing of data is easy, and the improvement of analysis accuracy is further promoted.
又、本発明の方法はボルタンメトリーの手法を
とり込んだガス分析法である。そして直流ボルタ
ンメトリーをはじめとして、交流、矩形波、微分
パルスボルタンメトリー等を使用して得られるデ
ータ中の、分析目的成分に起因するシグナルなど
の検出感度を向上させることができ、さらに複数
の被測定成分に対応するシグナルの相互分離性を
高めることができる。 Further, the method of the present invention is a gas analysis method that incorporates a voltammetric technique. In addition, it is possible to improve the detection sensitivity of signals caused by the target component of analysis in data obtained using DC voltammetry, alternating current, square wave, differential pulse voltammetry, etc. It is possible to improve the mutual separability of signals corresponding to .
更に従来の定電位電解法では、原理的に分離不
可能で、干渉成分となつていた強酸化性もしくは
強還元性の共存物質に対しても、吸収液の組成を
考慮すれば被測定物質との分離が可能であり、し
かも、そのような共存干渉成分の濃度測定も可能
である。 Furthermore, in the conventional constant potential electrolysis method, strongly oxidizing or strongly reducing coexisting substances, which cannot be separated in principle and are interfering components, can be separated from the analyte by considering the composition of the absorption liquid. It is possible to separate these components, and also to measure the concentration of such coexisting interfering components.
更に又、電気化学的ガス分析法は一般に選択
性、安定性が他法、たとえば光学的方法に比較し
て劣るものの、装置価格が安価であることが利点
とされていた。 Furthermore, although the electrochemical gas analysis method is generally inferior in selectivity and stability to other methods, such as optical methods, it has been considered advantageous that the equipment cost is low.
本発明の方法では電源、電流検出およびデータ
処理部が従来の電気化学的分析法よりも複雑にな
り、それだけ価格の上昇は避けられないものの、
近年の電子機器類の発達は装置の価格上昇を補つ
て余るものがあり、総体的にまた価格面に関して
も依然として他分析法よりも有利にあることに変
わりはない。 In the method of the present invention, the power supply, current detection, and data processing section are more complicated than in the conventional electrochemical analysis method, and the price inevitably increases accordingly.
Recent developments in electronic equipment have more than compensated for the rise in equipment prices, and it remains advantageous over other analytical methods both overall and in terms of price.
かつ、選択性、安定性も上述のように著るしく
改善された。 Moreover, the selectivity and stability were also significantly improved as mentioned above.
更に加えて、本発明の方法は静止液、静止電極
である点においては従来の定電位電解法と変わら
ない。 Additionally, the method of the present invention is no different from the conventional constant potential electrolysis method in that it uses a stationary liquid and a stationary electrode.
したがつて、分析精度や分離性が向上したにも
かかわらず、操作が複雑になることはほとんどな
い。 Therefore, even though analytical accuracy and separation performance have improved, the operation is hardly complicated.
次に本発明の実施例を述べる。 Next, examples of the present invention will be described.
実施例 1
第1図に示した系統図の装置を用いて試料ガス
中の窒素酸化物および二酸化イオウを検出した。Example 1 Nitrogen oxides and sulfur dioxide in a sample gas were detected using the system diagram shown in FIG.
吸収液2には0.01moldm-3の鉄エチレンジアミ
ン四酢酸錯体を含むPH2のリン酸、リン酸ナトリ
ウム系緩衝液を用い、検出電極1には水銀を用い
た。 For the absorption liquid 2, a phosphoric acid/sodium phosphate buffer solution with a pH of 2 containing a 0.01 moldm -3 iron ethylenediaminetetraacetic acid complex was used, and for the detection electrode 1, mercury was used.
対極側には対極4に白金線、対極液5にPH2の
リン酸、リン酸ナトリウム系緩衝液を使用し、対
極液と吸収液とを陽イオン交換膜の隔膜6で分離
した。 On the counter electrode side, a platinum wire was used as the counter electrode 4, a phosphoric acid/sodium phosphate buffer solution with a pH of 2 was used as the counter electrode solution 5, and the counter electrode solution and the absorption solution were separated by a diaphragm 6 made of a cation exchange membrane.
ところで、鉄エチレンジアミン四酢酸錯体は第
一鉄の状態で良好に一酸化窒素を吸収してニトロ
シル錯体を形成する。 By the way, the iron ethylenediaminetetraacetic acid complex absorbs nitrogen monoxide well in the ferrous state to form a nitrosyl complex.
このニトロシル錯体が検出電極1で分解されて
試料ガス中の窒素酸化物に基づくシグナルがボル
タングラム中に得られる。 This nitrosyl complex is decomposed at the detection electrode 1, and a signal based on nitrogen oxides in the sample gas is obtained in the voltamgram.
しかし、第一鉄エチレンジアミン四酢酸錯体は
試料ガス中に共存する酸素や二酸化窒素などの酸
化性物質によつて酸化を受け、一酸化窒素を吸収
しない第二鉄エチレンジアミン四酢酸錯体が生成
する。 However, the ferrous ethylenediaminetetraacetic acid complex is oxidized by oxidizing substances such as oxygen and nitrogen dioxide coexisting in the sample gas, and a ferric ethylenediaminetetraacetic acid complex that does not absorb nitrogen monoxide is generated.
そこで水銀プール電極12によつて第二鉄錯体
を第一鉄錯体に還元した。 Therefore, the ferric complex was reduced to a ferrous complex using the mercury pool electrode 12.
検出電極1および水銀プール電極12は飽和甘
汞電極の参照電極7によつて電位規制した。 The potential of the detection electrode 1 and the mercury pool electrode 12 was regulated by the reference electrode 7, which was a saturated mercury electrode.
又、水銀プール電極12は定電位電解装置9に
よつて−0.9V飽和甘汞電極基準に設定した。 Further, the mercury pool electrode 12 was set to -0.9V saturation electrode reference by the constant potential electrolyzer 9.
検出電極1は微分パルスポーラログラフ8に接
続し、−0.3Vから−1.1V対飽和甘汞電極基準まで
の電位掃引を繰り返した。 The detection electrode 1 was connected to a differential pulse polarograph 8, and a potential sweep was repeated from −0.3 V to −1.1 V versus the saturated Gampa electrode reference.
微分パルスポーラログラフ8の測定条件は下記
のとおりである。 The measurement conditions of the differential pulse polarograph 8 are as follows.
測定条件 3電極微分パルスボルタンメトリー
電位の掃引 −0.3Vで5秒保持後、20mVsec-1
でカソーデイツクに掃引し、−1.1Vで
終止し、−0.3Vに戻した。 Measurement conditions: 3-electrode differential pulse voltammetry Potential sweep: -0.3V held for 5 seconds, then 20mVsec -1
It was swept to the cathode at -1.1V and returned to -0.3V.
パルス巾 100msec、パルス高さ5mV
電流測定時間 20msec(パルス印加前および
後の電流測定時間)
電流測定間隔 40msec(パルス印加前および
後の電流測定間隔)
パルス間隔 0.5sec(パルス印加から次のパル
ス印加までの間隔)
微分パルスボルタングラフ8の電位掃引は、ボ
ルタングラフ制御およびデータ処理装置10のマ
イクロコンピユータによつて制御した。 Pulse width 100 msec, pulse height 5 mV Current measurement time 20 msec (current measurement time before and after pulse application) Current measurement interval 40 msec (current measurement interval before and after pulse application) Pulse interval 0.5 sec (from pulse application to next pulse application) The potential sweep of the differential pulse voltamgraph 8 was controlled by the microcomputer of the voltamgraph control and data processing device 10.
まずはじめに標準ガスとして標準ガスボンベ1
3から一酸化窒素446ppm、二酸化イオウ
662ppmの窒素バランスガスを使用し、それぞれ
50mlmin-1の流量でガスフローライン14、三方
弁15を経て吸収液2に送入し、定電位電解装置
9およびボルタングラフ8を作動して測定を行な
つた。この操作は標準ガスによる装置のキヤリブ
レーシヨンである。 First of all, standard gas cylinder 1 is used as standard gas.
3 to 446ppm nitrogen monoxide, sulfur dioxide
Using 662ppm nitrogen balance gas, each
The gas was introduced into the absorption liquid 2 through the gas flow line 14 and the three-way valve 15 at a flow rate of 50 ml min -1 , and the constant potential electrolyzer 9 and voltamgraph 8 were operated to perform measurements. This operation is a calibration of the device with standard gases.
約10分間この操作を続け、各掃引ごとに得たボ
ルタングラムについてデジタル化した後に、下記
のデータ処理を行なつた。 This operation was continued for about 10 minutes, and after digitizing the voltamgrams obtained for each sweep, the following data processing was performed.
(イ) 一回の電位掃引におけるデータ処理。(b) Data processing in one potential sweep.
(イ−1) 一回の掃引中に一つ前にサンプリ
ングしたデータと現時点にサンプリングした
データとを比較して、その値が50%以上異な
るときは、現時点のデータを棄却し、その箇
所に一つ前のデータをそのまま入れる処置を
行つた。 (A-1) Compare the data sampled before and the data sampled at the current time during one sweep, and if the values differ by 50% or more, the current data is rejected and the data sampled at that point is I took steps to input the previous data as is.
(イ−2) (イ−1)の処理後、11点数をと
る重み付き移動平均による平滑化処理を行な
う処置を施した。 (A-2) After the processing in (A-1), a smoothing process using a weighted moving average taking 11 points was performed.
(ロ) 繰り返し電位掃引におけるデータ処理。(b) Data processing in repeated potential sweeps.
(ロ−1) 一つ前に行つた電位掃引のデータ
のうち、同じ電極電位のデータを比較し、50
%以上差のあるデータを除去して、そこには
一つ前の掃引の同電位のデータをそのまま入
れた。 (Ro-1) Compare the data of the same electrode potential among the data of the previous potential sweep, and
Data with a difference of more than % was removed, and the data of the same potential from the previous sweep was inserted as is.
(ロ−2) (イ)の処理を行ない、次いで(ロ)(ロ
−1)の処理を行なつた後に、掃引回数4回
ごとの積算平均化処理を行ない、ノイズの除
去されたなめらかなボルタングラムを得た。 (Ro-2) After performing the processing in (a), then (b) after performing the processing in (ro-1), an integrated averaging process is performed every four sweeps to create a smooth image with noise removed. Obtained the voltamgram.
これら(イ−1)から(ロ−2)までの4種類
のデータ処理によつてノイズ等に起因する異状デ
ータが除去され、測定のばらつきがなくなるが、
測定時の環境が良好で大きなノイズがほとんど表
われない場合には、(ロ−2)の積算平均化処理
のみを前後2回の電位掃引について行なうだけで
十分満足できる結果が得られた。 These four types of data processing from (A-1) to (RO-2) remove abnormal data caused by noise, etc., and eliminate measurement variations.
When the environment at the time of measurement is good and there is almost no large noise, satisfactory results were obtained by performing only the cumulative averaging process (Rho-2) for the two previous and subsequent potential sweeps.
このボルタングラムから二酸化イオウおよび窒
素酸化物に基づく波高を測定し、ガス濃度と波高
との関係をデータ処理装置10に記憶させた。 The wave height based on sulfur dioxide and nitrogen oxide was measured from this voltamgram, and the relationship between the gas concentration and the wave height was stored in the data processing device 10.
次に標準ガスの送付をやめ、別途調整した空
気、二酸化イオウ、および窒素酸化物の混合試料
ガスをエアポンプ16によつて検出部に100ml
min-1の流量で導入した。電解検出およびデータ
処理は前記標準ガスによるキヤリブレーシヨンの
場合と同様に行なつた。 Next, the delivery of the standard gas was stopped, and 100ml of a separately prepared mixed sample gas of air, sulfur dioxide, and nitrogen oxide was delivered to the detection unit using the air pump 16.
It was introduced at a flow rate of min -1 . Electrolytic detection and data processing were performed in the same manner as in the standard gas calibration.
得られた二酸化イオウと窒素酸化物に基づくピ
ーク高さを測定し、前記キヤリブレーシヨンのと
きに測定した波高と濃度の関係から二酸化イオウ
と一酸化窒素との濃度を求めた。 The peak heights based on the obtained sulfur dioxide and nitrogen oxide were measured, and the concentrations of sulfur dioxide and nitrogen monoxide were determined from the relationship between the wave height and the concentration measured during the calibration.
その結果、得られた値は試料ガス調製の際の希
釈比から求めた濃度と一致した。 As a result, the obtained value matched the concentration determined from the dilution ratio during sample gas preparation.
又、上述の実験においてピークの波高測定の代
わりにピークの面積測定を行なつて試料ガス中の
二酸化イオウと一酸化窒素の濃度を求めた。 Furthermore, in the above experiment, the concentrations of sulfur dioxide and nitrogen monoxide in the sample gas were determined by measuring the area of the peak instead of measuring the height of the peak.
その結果は、波高測定の場合と同様に良好な結
果を得た。 The results were as good as the wave height measurements.
なお、第3図にデータ処理を全く行わない場合
の試料ガスのボルタングラムの1例を示した。 Note that FIG. 3 shows an example of the voltamgram of the sample gas when no data processing is performed.
この図で、−0.5Vから−0.6Vに見られるピーク
が亜硫酸、−0.9V付近のピークがニトロシル錯
体、−1.0V付近の立ち上りは水素発生に起因して
おり、ニトロシル錯体と水素発生との間にノイズ
が見られる。 In this figure, the peak seen from −0.5V to −0.6V is sulfite, the peak around −0.9V is the nitrosyl complex, and the rise around −1.0V is due to hydrogen generation. Noise can be seen in between.
しかしこのノイズも上記データ処理によつて除
くことができた。 However, this noise could also be removed by the data processing described above.
実施例 2
検出電極1を鉛とし、吸収液2に鉄エチレンジ
アミン四酢酸を含まないPH2のリン酸−リン酸ナ
トリウム緩衝液を用いた以外は、実施例1と同様
の装置を用いて空気、二酸化イオウ混合ガス(二
酸化イオウ濃度既知)中の二酸化イオウの検出、
定量を行なつた。Example 2 The same apparatus as in Example 1 was used, except that the detection electrode 1 was lead and the absorption liquid 2 was a phosphoric acid-sodium phosphate buffer solution with a pH of 2 that did not contain iron ethylenediaminetetraacetic acid. Detection of sulfur dioxide in sulfur mixed gas (sulfur dioxide concentration known),
Quantification was performed.
標準ガスには662ppm二酸化イオウの窒素バラ
ンガスを使用した。 A nitrogen balun gas containing 662 ppm sulfur dioxide was used as the standard gas.
データ処理方法は実施例1と同様に、前データ
との値が大きい異状データの除去、平滑処理およ
び積算平均化処理を行ない、ボルタングラムの波
高比によつて混合ガス中の二酸化イオウ濃度を求
めた。 The data processing method is the same as in Example 1, by removing abnormal data that has a large value with the previous data, smoothing processing, and integrating averaging processing, and determining the sulfur dioxide concentration in the mixed gas from the peak ratio of the voltamogram. Ta.
この結果、得られた二酸化イオウ濃度は空気、
二酸化イオウ混合比から算出した濃度と一致し
た。 As a result, the obtained sulfur dioxide concentration is
The concentration agreed with the concentration calculated from the sulfur dioxide mixing ratio.
実施例 3
第2図に示す検出器を用い、実施例1と同様の
空気、二酸化イオウ、および一酸化窒素混合ガス
を使用して電位掃引を行なつて得られるボルタン
グラムの状態を観察した。Example 3 Using the detector shown in FIG. 2, a potential sweep was performed using the same mixed gas of air, sulfur dioxide, and nitrogen monoxide as in Example 1, and the state of the voltamgram obtained was observed.
この検出器では、実施例1と同様に検出電極1
の材質として水銀を用い、吸収液2には鉄エチレ
ンジアミン四酢酸を含むPH2のリン酸−リン酸ナ
トリウム緩衝液を用いた。 In this detector, as in Example 1, the detection electrode 1
Mercury was used as the material, and a phosphoric acid-sodium phosphate buffer solution of pH 2 containing iron ethylenediaminetetraacetic acid was used as the absorption liquid 2.
しかし、対極側はリン酸−リン酸ナトリウム緩
衝液にヨウ化カリウムを溶解して対極液5とし、
これに銀網4,7を挿入して銀−ヨウ化銀電極を
作り、対極4と同時に参照電極7の機能も持たせ
た。 However, for the counter electrode side, potassium iodide was dissolved in a phosphoric acid-sodium phosphate buffer solution to prepare the counter electrode solution 5.
A silver-silver iodide electrode was made by inserting silver nets 4 and 7 into this, and the counter electrode 4 and the reference electrode 7 functioned simultaneously.
検出電極1との間には隔膜6として陽イオン交
換膜を用いた。 A cation exchange membrane was used as a diaphragm 6 between the detection electrode 1 and the detection electrode 1 .
又、試料ガスが存在する気相と吸収液の液相と
を気体透過性多孔質膜17で分離した。 Further, the gas phase containing the sample gas and the liquid phase of the absorption liquid were separated by a gas permeable porous membrane 17.
第4図Aにただ1回の掃引によつて得たデータ
処理前のボルタングラムの1例を示す。 FIG. 4A shows an example of a voltamgram before data processing obtained by just one sweep.
0.0Vから−0.2Vに見られる亜硫酸、−0.3Vから
−0.6Vに見られるニトロシル錯体のピークは共
に頂点が二つに割れているなど、このままでは波
高測定がしにくい形になつているが、10回の繰り
返し掃引を行なう積算平均化処理を行なうことに
よつて第4図Aのボルタングラムは第4図Bに示
すように、なめらかな曲線となつた。 The sulfite peak seen from 0.0V to -0.2V and the nitrosyl complex peak seen from -0.3V to -0.6V both have their apexes split into two, making it difficult to measure the wave height as is. By carrying out an integrated averaging process in which sweeps are repeated 10 times, the voltamgram in FIG. 4A becomes a smooth curve as shown in FIG. 4B.
検出器が安定な状態に保たれていれば、ただ1
回の掃引によつて得たボルタングラムでもノイズ
は大きく減少するので、2回の積算平均化処理、
もしくは1回掃引だけの単純移動平均による平滑
化処理だけで、なめらかなボルタングラムが得ら
れた。 If the detector is kept stable, only 1
Since the noise is greatly reduced even in the voltamgram obtained by sweeping twice,
Alternatively, a smooth voltamgram could be obtained by simply performing smoothing processing using a simple moving average with only one sweep.
なお、データ処理を行なわめ場合には前後のデ
ータにばらつきが見られた。 In addition, when data processing was performed, there were variations in the data before and after.
次に酸素を全く含まない標準ガスだけの場合に
ついて検討したが、検出器を安定な状態に保つこ
とは比較的容易であつた。 Next, we considered the case of using only a standard gas that does not contain any oxygen, but it was relatively easy to maintain the detector in a stable state.
二酸イオウ、一酸化窒素の各標準ガスを混合し
た場合の結果を第5図に示す。 Figure 5 shows the results when the standard gases of sulfur dioxide and nitrogen monoxide were mixed.
第5図の一点鎖線は標準ガス通気後10分の第1
回掃引のボルタングラムであり、実線は第2回か
ら第5回掃引のボルタングラムである。 The dot-dash line in Figure 5 indicates the first 10 minutes after standard gas ventilation.
The solid line is the voltamgram of the second to fifth sweeps.
このことから、第2回の掃引以後は十分に定常
的なボルタングラムが得られることが理解でき
る。 From this, it can be understood that a sufficiently steady voltamgram can be obtained after the second sweep.
実施例 4
実施例3と同様の検出器および混合ガスを用
い、直流法、交流法、矩形波法および微分パルス
法の各法によつて電圧を印加しながら電位掃引法
によるボルタングラムを観察した。Example 4 Using the same detector and mixed gas as in Example 3, voltage was applied using the direct current method, alternating current method, square wave method, and differential pulse method, and the voltamgram was observed using the potential sweep method. .
直流法でニトロシル錯体と水素発生に関する波
の分離が因難であつた外は、いずれの方法でも良
好な亜硫酸とニトロシル錯体のシグナルを得るこ
とができた。 Good signals for sulfite and nitrosyl complexes were obtained using both methods, except that the direct current method had difficulty in separating the waves related to nitrosyl complexes and hydrogen generation.
第1図は本発明で使用する測定装置の一系統
図、第2図はその検出器の一概要図、第3図、第
4図、第5図はいずれも本発明の方法で観測され
たボルタングラムの一例を示す図である。
1……検出電極、2……吸収液、3……試料ガ
ス、4……対極、7……参照電極、8……微分パ
ルスポーラログラフ、10……ボルタングラム制
御およびデータ処理装置。
Figure 1 is a system diagram of the measuring device used in the present invention, Figure 2 is a schematic diagram of its detector, and Figures 3, 4, and 5 are all images observed using the method of the present invention. It is a figure showing an example of a voltamgram. DESCRIPTION OF SYMBOLS 1...Detection electrode, 2...Absorption liquid, 3...Sample gas, 4...Counter electrode, 7...Reference electrode, 8...Differential pulse polarograph, 10...Voltangram control and data processing device.
Claims (1)
め、前記液相中に移相した前記被測定成分を前記
液相と直接接する電極によつて電解検出し、定量
する気体分析方法において、前記液相および前記
電極を静止系とすると共に、前記電極に印加電圧
範囲内の電圧をくり返し印加し、前記電極からの
電解電流値を平滑化処理および/又は積算平均化
処理して得られたボルタングラム中の前記被測定
成分に基づく波高、またはピーク面積を計測して
前記気相中の前記被測定成分濃度を測定すること
を特徴とする気相中に含有される被測定成分の濃
度測定方法。1. A gas analysis method in which a gas phase containing a component to be measured is brought into contact with a liquid phase, and the component to be measured whose phase has shifted into the liquid phase is electrolytically detected and quantified by an electrode in direct contact with the liquid phase, The liquid phase and the electrodes are set as a static system, and a voltage within the applied voltage range is repeatedly applied to the electrodes, and the electrolytic current value from the electrodes is smoothed and/or integrated and averaged. Measuring the concentration of a component to be measured contained in a gas phase, characterized in that the concentration of the component to be measured in the gas phase is measured by measuring a wave height or a peak area based on the component to be measured in a voltamgram. Method.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP12443179A JPS5647751A (en) | 1979-09-27 | 1979-09-27 | Measuring method for concentration |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP12443179A JPS5647751A (en) | 1979-09-27 | 1979-09-27 | Measuring method for concentration |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS5647751A JPS5647751A (en) | 1981-04-30 |
| JPS6243134B2 true JPS6243134B2 (en) | 1987-09-11 |
Family
ID=14885311
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP12443179A Granted JPS5647751A (en) | 1979-09-27 | 1979-09-27 | Measuring method for concentration |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPS5647751A (en) |
Families Citing this family (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP5969433B2 (en) * | 2013-07-12 | 2016-08-17 | トヨタ自動車株式会社 | SOx concentration detection device for internal combustion engine |
| JP5981398B2 (en) * | 2013-07-12 | 2016-08-31 | 株式会社日本自動車部品総合研究所 | SOx concentration detection device for internal combustion engine |
| JP5910648B2 (en) * | 2014-02-20 | 2016-04-27 | トヨタ自動車株式会社 | Control device for internal combustion engine |
-
1979
- 1979-09-27 JP JP12443179A patent/JPS5647751A/en active Granted
Also Published As
| Publication number | Publication date |
|---|---|
| JPS5647751A (en) | 1981-04-30 |
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