JPH0579988A - Humic acid quantification using chemical luminescence - Google Patents

Humic acid quantification using chemical luminescence

Info

Publication number
JPH0579988A
JPH0579988A JP24351391A JP24351391A JPH0579988A JP H0579988 A JPH0579988 A JP H0579988A JP 24351391 A JP24351391 A JP 24351391A JP 24351391 A JP24351391 A JP 24351391A JP H0579988 A JPH0579988 A JP H0579988A
Authority
JP
Japan
Prior art keywords
humic acid
luminescence
quantification
measured
acid concentration
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.)
Granted
Application number
JP24351391A
Other languages
Japanese (ja)
Other versions
JPH0765965B2 (en
Inventor
Yasuaki Maeda
泰昭 前田
Kenji Aoki
健二 青木
Koji Hattori
剛治 服部
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.)
KANSAI SOGO KANKYO CENTER KK
Kansai Environmental Engineering Center Co Ltd
Original Assignee
KANSAI SOGO KANKYO CENTER KK
Kansai Environmental Engineering Center 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 KANSAI SOGO KANKYO CENTER KK, Kansai Environmental Engineering Center Co Ltd filed Critical KANSAI SOGO KANKYO CENTER KK
Priority to JP3243513A priority Critical patent/JPH0765965B2/en
Publication of JPH0579988A publication Critical patent/JPH0579988A/en
Publication of JPH0765965B2 publication Critical patent/JPH0765965B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

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  • Investigating Or Analyzing Non-Biological Materials By The Use Of Chemical Means (AREA)
  • Investigating Or Analysing Materials By The Use Of Chemical Reactions (AREA)

Abstract

PURPOSE:To provide humic acid quantification applicable to a continuous analyzing/measuring device provided on a water supply purifying processor by quickly measuring the humic acid concentration in a specimen with high precision. CONSTITUTION:Hydrogen peroxide and formaldehyde are added to a humic acid-containing specimen, alkali such as sodium hydroxide is added to adjust PH for chemical luminescence, and the luminescence intensity in the preset wavelength, preferably the maximum luminescence wavelength, in the luminescence spectrum is extracted and recorded as the electric signal amplified by a photomultiplier and an amplifier. This luminescence intensity is compared with the luminescence intensity/humic acid concentration calibration curve measured separately for quantification. The measured value is precise because it can be measured to the unit of ppb, the humic acid concentration is directly measured, thus the quantification result is quickly obtained continuously.

Description

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

【0001】[0001]

【産業上の利用分野】この発明は、水道水等の分析その
他の工業用分析処理等に適用される化学発光を用いたフ
ミン酸定量法に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method for quantifying humic acid using chemiluminescence, which is applied to analysis of tap water and other industrial analytical treatments.

【0002】[0002]

【従来の技術】一般にフミン酸は土壌または低石炭化度
の石灰質中に存する酸性有機物であって、その化学構造
はよく知られていないものであるが、その主要構造は、
多価フェノール形の芳香族化合物と含窒素化合物との縮
合物であると考えられている。
Humic acid is an acidic organic substance generally existing in soil or calcareous matter with low coalification degree, and its chemical structure is not well known, but its main structure is
It is considered to be a condensation product of a polyhydric phenol type aromatic compound and a nitrogen-containing compound.

【0003】上記フミン酸は上水道の原水にも含まれて
いるが、この原水を塩素で殺菌処理したときに、これが
トリハロメタンに変性する可能性がある。トリハロメタ
ンは、人または動物の機能に重大な危害を与える劇薬で
あり、前記殺菌処理前の原水中の前駆物質たるフミン酸
の濃度を知ることで浄水処理対策を講じる必要がある。
The humic acid is also contained in the raw water of the water supply, but when the raw water is sterilized with chlorine, it may be modified into trihalomethane. Trihalomethane is a powerful drug that seriously impairs human or animal functions, and it is necessary to take measures for water purification treatment by knowing the concentration of humic acid, which is a precursor in the raw water before the sterilization treatment.

【0004】このようなフミン酸の定量法としては、E
DTA錯塩でマスキングし、フミン酸の可視部(410
〜480nm)における吸光度を測定する方法が採用さ
れていた。
As a method for quantifying such humic acid, E
Masked with DTA complex salt, visible part of humic acid (410
(-480 nm) was used.

【0005】[0005]

【発明が解決しようとする課題】しかし、上記従来のフ
ミン酸の定量法では、マスキング等の前処理に時間がか
かると共にセル等の操作も煩雑であり、また測定結果を
連続して得ることができないという問題点も有してい
た。
However, in the above-mentioned conventional method for quantifying humic acid, pretreatment such as masking takes time, operation of cells and the like is complicated, and measurement results can be obtained continuously. It also had a problem that it could not be done.

【0006】この発明は、上記従来のフミン酸定量法に
おける問題点を解決し、検体中のフミン酸の測定を高精
度で迅速に行ない得て、上水道浄化処理装置等に付設さ
れる連続分析測定装置等にも適用し得るフミン酸定量法
を提供することを課題としている。
The present invention solves the above-mentioned problems in the conventional humic acid determination method, can measure humic acid in a sample with high accuracy and speed, and can perform continuous analytical measurement attached to a water purification system or the like. It is an object to provide a humic acid determination method that can be applied to devices and the like.

【0007】[0007]

【課題を解決するための手段】上記の課題を解決するた
め、この発明においては、フミン酸含有検体に過酸化水
素およびホルムアルデヒドを添加して化学発光させ、そ
の発光スペクトルのうち所定波長における発光強度を光
電管によって電気信号化して測定し、前記発光強度と別
途測定した前記所定波長における発光強度−フミン酸濃
度検量線とを対比して定量する手段を採用したのであ
る。
In order to solve the above problems, in the present invention, hydrogen peroxide and formaldehyde are added to a humic acid-containing sample to cause chemiluminescence, and the luminescence intensity at a predetermined wavelength in the luminescence spectrum thereof. Was converted into an electric signal by a photoelectric tube and measured, and a means for quantifying by comparing the emission intensity and the emission intensity at the predetermined wavelength separately measured with the humic acid concentration calibration curve was adopted.

【0008】[0008]

【作用】この発明に係る化学発光を用いたフミン酸定量
法は、検体中のフミン酸、過酸化水素およびホルムアル
デヒドを反応させた際、化学発光する現象を見い出し、
その発光スペクトルのうち、適当な波長(好ましくは最
大発光波長)の発光強度を光電管から電気信号として測
定する。一方、フミン酸濃度既知の検体に前記過酸化水
素およびホルムアルデヒドを同じ条件で添加反応させて
前記波長で作成した発光強度−フミン酸濃度の検量線に
前記発光強度を対比すれば、迅速かつ精密に検体のフミ
ン酸成分が定量される。
The method for determining humic acid using chemiluminescence according to the present invention finds a phenomenon of chemiluminescence when humic acid, hydrogen peroxide and formaldehyde in a sample are reacted,
Of the emission spectrum, the emission intensity at an appropriate wavelength (preferably the maximum emission wavelength) is measured from the phototube as an electric signal. On the other hand, by comparing and adding the hydrogen peroxide and formaldehyde to a specimen of known humic acid concentration under the same conditions to produce luminescence intensity at the wavelength-contrast the luminescence intensity to a calibration curve of the humic acid concentration, it can be rapidly and accurately measured. The humic acid component of the sample is quantified.

【0009】[0009]

【実施例】この発明に用いるホルムアルデヒドは、HC
HOの40%水溶液である市販のホルマリンを適当な濃
度として用いる他、ホルムアルデヒドの誘導体であるパ
ラホルムアルデヒド、ポリホルムアルデヒド等を選択的
に用いることも可能である。
EXAMPLE Formaldehyde used in the present invention is HC
Commercially available formalin, which is a 40% aqueous solution of HO, may be used at an appropriate concentration, or paraformaldehyde, polyformaldehyde or the like, which is a derivative of formaldehyde, may be selectively used.

【0010】また、この発明に用いる過酸化水素を分解
反応し易くするために、適宜、水酸化ナトリウム等のア
ルカリを添加して反応容器内のPHを4〜5程度に調整
しておくことが望ましい。
In order to facilitate the decomposition reaction of hydrogen peroxide used in the present invention, the pH in the reaction vessel may be adjusted to about 4 to 5 by adding an alkali such as sodium hydroxide. desirable.

【0011】また、上記PH以外の化学発光反応時の条
件として金属触媒を添加すれば、発光強度が増すので、
一層高感度の測定が可能となる。
If a metal catalyst is added as a condition for the chemiluminescence reaction other than the above PH, the luminescence intensity increases.
Higher sensitivity measurement is possible.

【0012】この発明における発光強度の測定に使用し
得る波長、すなわち、光電管に入力し得る波長を調べる
ために、以下の実験を行なった。
The following experiment was carried out in order to investigate the wavelength that can be used for measuring the emission intensity in the present invention, that is, the wavelength that can be input to the photoelectric tube.

【0013】すなわち、ホルムアルデヒドおよび過酸化
水素の量と濃度を任意に設定し、PHを調整してこれら
をフミン酸と効率よく反応させ、波長範囲185〜85
0nmに分光感度をもつ光電子増倍管を用いて最大発光
波長640nmの光を検出した。
That is, the amounts and concentrations of formaldehyde and hydrogen peroxide are arbitrarily set, the pH is adjusted, and these are reacted with humic acid efficiently, and the wavelength range is 185 to 85.
Light with a maximum emission wavelength of 640 nm was detected using a photomultiplier tube having a spectral sensitivity of 0 nm.

【0014】次に、上記実験で調べた最大発光強度の波
長を用いた定量装置の実験例について説明する。
Next, an experimental example of the quantification device using the wavelength of the maximum emission intensity investigated in the above experiment will be described.

【0015】〔実験例〕まず、図1に示す装置を用い
て、発光強度−フミン酸濃度検量線を作製した。すなわ
ち、10、20、40、100ppmの濃度でフミン酸
標準濃度液1をペリスタポンプ2を介して毎分2ミリリ
ットルの流量で混合管3に供給し、一方、3%の過酸化
水素水4を毎分2ミリリットルの流量で攪拌容器5に導
入し、この攪拌容器5には、さらに市販のホルムアルデ
ヒドの5%水溶液6を毎分2ミリリットル、また1モル
濃度の水酸化ナトリウム水溶液7を毎分2ミリリットル
の流量でペリスタポンプ2から攪拌容器5に導入し、攪
拌後の混液をさらに混合管3に供給して前記フミン酸標
準濃度液1と混合し、反応容器8に供給した。この反応
容器8内での反応条件は、常温、常圧とした。
[Experimental Example] First, an emission intensity-humic acid concentration calibration curve was prepared using the apparatus shown in FIG. That is, the humic acid standard concentration liquid 1 having a concentration of 10, 20, 40, and 100 ppm was supplied to the mixing pipe 3 through the peristaltic pump 2 at a flow rate of 2 ml / min, while the 3% hydrogen peroxide solution 4 was supplied. The mixture was introduced into the stirring container 5 at a flow rate of 2 ml / min, and in the stirring container 5, 2 ml / min of a commercially available 5% aqueous solution of formaldehyde 6 and 2 ml / min of a 1 molar sodium hydroxide aqueous solution 7 were further introduced. Was introduced into the stirring container 5 from the peristaltic pump 2 at a flow rate of 1, and the mixed liquid after stirring was further supplied to the mixing tube 3 to be mixed with the humic acid standard concentration liquid 1 and supplied to the reaction container 8. The reaction conditions in the reaction vessel 8 were room temperature and atmospheric pressure.

【0016】上記反応容器8は、分光フィルタ付き光電
子増倍管9に連結させて、発生した化学発光の最大発光
波長640nmにおける強度を電気信号量として検出
し、増幅器10を介して発光強度(相対値)を記録計1
1に入力した。得られた各フミン酸濃度における発光強
度を両対数グラフにプロットして、直線関係の検量線
(図2参照)を得た。
The reaction vessel 8 is connected to a photomultiplier tube 9 with a spectral filter to detect the intensity of the generated chemiluminescence at the maximum emission wavelength of 640 nm as an electric signal amount, and the emission intensity (relative to the relative intensity via an amplifier 10). Value) Recorder 1
Entered in 1. The emission intensity at each obtained humic acid concentration was plotted on a logarithmic log graph to obtain a linear calibration curve (see FIG. 2).

【0017】つぎに、濃度未知のフミン酸含有検体Aの
濃度は、以下のようにして求めた。
Next, the concentration of the humic acid-containing specimen A of unknown concentration was determined as follows.

【0018】すなわち、フミン酸標準濃度液1に代え
て、フミン酸含有検体Aを混合管3内に導入し、過酸化
水素水4、ホルムアルデヒド水溶液6、水酸化ナトリウ
ム水溶液7を上記と全く同様にして混合管3に供給し、
発光強度を前記記録された検出線に対比して検体Aのフ
ミン酸濃度を求めた。反応容器8内の廃液は、真空ポン
プ12によって廃液溜め13内に収容した。
That is, instead of the humic acid standard concentration liquid 1, the humic acid-containing sample A is introduced into the mixing tube 3, and the hydrogen peroxide solution 4, the formaldehyde solution 6, and the sodium hydroxide solution 7 are treated in exactly the same manner as above. Supply to the mixing tube 3,
The humic acid concentration of the sample A was determined by comparing the emission intensity with the recorded detection line. The waste liquid in the reaction container 8 was stored in the waste liquid reservoir 13 by the vacuum pump 12.

【0019】上記実験例のフミン酸濃度検出限界は10
ppbであり、1ppmにおける5回測定の標準偏差は
2.3%であった。
The detection limit of humic acid concentration in the above experimental example is 10
ppb, standard deviation of 5 measurements at 1 ppm was 2.3%.

【0020】なお、反応容器8内の形状変更とコーティ
ングおよび反応セルの設置などを応用すれば、上記した
以上の測定感度と信頼性を得ることも可能である。
If the shape of the reaction vessel 8 is changed, the coating and the reaction cell are installed, it is possible to obtain the measurement sensitivity and reliability above.

【0021】[0021]

【効果】この発明は、以上説明したように、フミン酸と
過酸化水素およびホルムアルデヒドとの極めて鋭敏な反
応によって発生する化学発光の強度を測定することで、
検体中のフミン酸の存在を直接に検出する定量法である
から、高精度で、しかも迅速に連続してフミン酸の定量
を行なうことができる。
As described above, the present invention can measure the intensity of chemiluminescence generated by the extremely sensitive reaction of humic acid with hydrogen peroxide and formaldehyde.
Since this is a quantitative method that directly detects the presence of humic acid in a sample, it is possible to perform quantification of humic acid with high accuracy and rapidly.

【0022】したがって、上水道の塩素添加量を制御す
る正確なデータを迅速に得るために、この方法を適用す
ることができ、この発明の産業上の利用価値は極めて高
いものであるということができる。
Therefore, this method can be applied to quickly obtain accurate data for controlling the amount of chlorine added to waterworks, and it can be said that the industrial utility value of the present invention is extremely high. .

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

【図1】模式化して示す実験例の定量装置図FIG. 1 is a schematic diagram showing a quantitative device of an experimental example.

【図2】発光強度−フミン酸濃度両対数検量線図FIG. 2 Luminous intensity-humic acid concentration bilogarithmic calibration curve diagram

【符号の説明】[Explanation of symbols]

A フミン酸含有検体 4 過酸化水素水 6 ホルムアルデヒド水溶液 A Humic acid-containing sample 4 Hydrogen peroxide water 6 Formaldehyde aqueous solution

Claims (1)

【特許請求の範囲】[Claims] 【請求項1】 フミン酸含有検体に過酸化水素およびホ
ルムアルデヒドを添加して化学発光させ、その発光スペ
クトルのうち所定波長における発光強度を光電管によっ
て電気信号化して測定し、前記発光強度と別途測定した
前記所定波長における発光強度−フミン酸濃度検量線と
を対比して定量する化学発光を用いたフミン酸定量法。
1. Hydrogen peroxide and formaldehyde are added to a humic acid-containing sample to cause chemiluminescence, and the emission intensity at a predetermined wavelength in the emission spectrum is measured by converting it into an electric signal by a photoelectric tube, and the emission intensity is separately measured. A humic acid quantification method using chemiluminescence in which luminescence intensity at a predetermined wavelength is compared with a humic acid concentration calibration curve for quantification.
JP3243513A 1991-09-24 1991-09-24 Chemiluminescent humic acid determination method Expired - Fee Related JPH0765965B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP3243513A JPH0765965B2 (en) 1991-09-24 1991-09-24 Chemiluminescent humic acid determination method

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP3243513A JPH0765965B2 (en) 1991-09-24 1991-09-24 Chemiluminescent humic acid determination method

Publications (2)

Publication Number Publication Date
JPH0579988A true JPH0579988A (en) 1993-03-30
JPH0765965B2 JPH0765965B2 (en) 1995-07-19

Family

ID=17105027

Family Applications (1)

Application Number Title Priority Date Filing Date
JP3243513A Expired - Fee Related JPH0765965B2 (en) 1991-09-24 1991-09-24 Chemiluminescent humic acid determination method

Country Status (1)

Country Link
JP (1) JPH0765965B2 (en)

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2013221773A (en) * 2012-04-13 2013-10-28 National Agriculture & Food Research Organization Simplified method for estimating quantity of phenylpropanoid polymer
MD4221C1 (en) * 2012-01-10 2013-11-30 Институт Химии Академии Наук Молдовы Method for quantitative determination of humic substances in natural waters
MD4305C1 (en) * 2013-04-02 2015-04-30 Институт Химии Академии Наук Молдовы Process for determining water-soluble humic substances in natural waters and solid rocks
JPWO2022039125A1 (en) * 2020-08-19 2022-02-24

Citations (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH03225262A (en) * 1990-01-30 1991-10-04 Meidensha Corp Method and instrument for measuring consumption of oxidizing agent

Patent Citations (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH03225262A (en) * 1990-01-30 1991-10-04 Meidensha Corp Method and instrument for measuring consumption of oxidizing agent

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
MD4221C1 (en) * 2012-01-10 2013-11-30 Институт Химии Академии Наук Молдовы Method for quantitative determination of humic substances in natural waters
JP2013221773A (en) * 2012-04-13 2013-10-28 National Agriculture & Food Research Organization Simplified method for estimating quantity of phenylpropanoid polymer
MD4305C1 (en) * 2013-04-02 2015-04-30 Институт Химии Академии Наук Молдовы Process for determining water-soluble humic substances in natural waters and solid rocks
JPWO2022039125A1 (en) * 2020-08-19 2022-02-24
WO2022039125A1 (en) * 2020-08-19 2022-02-24 株式会社日吉 Sensitizer for use in measurement of chemiluminescence of ammonium ion, ammonium ion analysis method, ammonium ion analysis device

Also Published As

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