JP2532952B2 - Chemical oxygen demand measuring method and measuring reagent - Google Patents

Chemical oxygen demand measuring method and measuring reagent

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Publication number
JP2532952B2
JP2532952B2 JP1283653A JP28365389A JP2532952B2 JP 2532952 B2 JP2532952 B2 JP 2532952B2 JP 1283653 A JP1283653 A JP 1283653A JP 28365389 A JP28365389 A JP 28365389A JP 2532952 B2 JP2532952 B2 JP 2532952B2
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JP
Japan
Prior art keywords
cod
water
test water
reagent
hue
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JP1283653A
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Japanese (ja)
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JPH03144348A (en
Inventor
俊晴 丸岡
敬子 亀田
泰史 瀬尾
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Shikoku Chemicals Corp
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Shikoku Chemicals Corp
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Description

【発明の詳細な説明】 産業上の利用分野 本発明は化学的酸素要求量の測定方法及びこれに使用
する試薬に関するものであり、検水の化学的酸素要求量
を迅速且つ簡便に測定しうるものである。
TECHNICAL FIELD The present invention relates to a method for measuring a chemical oxygen demand and a reagent used therefor, which can quickly and simply measure the chemical oxygen demand of a test water. It is a thing.

従来の技術 化学的酸素要求量(以下CODという)の測定方法は日
本工業規格(JIS)K0101及びK0102に記載されており、
100℃における過マンガン酸カリウムによる酸素消費
量(CODMn)、20℃における過マンガン酸カリウムに
よる酸素消費量(CODMn20)、アルカリ性過マンガン
酸カリウムによる酸素消費量(CODOH)、二クロム酸
カリウムによる酸素消費量(CODcr)として測定されて
いる。また特開昭63−186147号公報には、高周波誘電加
熱手段を用いて加熱酸化反応を行うことにより、測定時
間の短縮を図る方法が提案されている。
Conventional technology The method of measuring chemical oxygen demand (hereinafter referred to as COD) is described in Japanese Industrial Standards (JIS) K0101 and K0102.
Oxygen consumption by potassium permanganate (COD Mn ) at 100 ℃, oxygen consumption by potassium permanganate (COD Mn20 ) at 20 ℃, oxygen consumption by alkaline potassium permanganate (COD OH ), potassium dichromate It is measured as oxygen consumption (COD cr ). Further, Japanese Patent Laid-Open No. 186147/1988 proposes a method of shortening the measurement time by carrying out a thermal oxidation reaction using a high frequency dielectric heating means.

発明が解決しようとする課題 JISに規定されているCODの測定方法は、加熱及び滴定
などの煩雑な操作を必要とするため、屋外にある水処理
装置あるいは浄化槽等の管理現場において、速やかにそ
の水質状態を知りたいとの要求に適応し難いものであっ
た。
Problems to be Solved by the Invention Since the COD measurement method specified in JIS requires complicated operations such as heating and titration, it is necessary to quickly perform the measurement at the management site such as an outdoor water treatment device or a septic tank. It was difficult to adapt to the request to know the water quality condition.

また特開昭63−186147号公報に記載の方法も、電力源
と高周波誘電加熱装置が必要であり、屋外の水質管理現
場において実施することは甚だ困難な方法であった。
Further, the method described in Japanese Patent Laid-Open No. 63-186147 also requires a power source and a high frequency dielectric heating device, and it is a very difficult method to carry out at the outdoor water quality control site.

課題を解決するための手段 本発明者等は、このような問題を解決するために種々
の試験を繰り返した結果、過マンガン酸カリウム、水溶
性塩基性物質及びジフェニルアミン−4−スルフォン酸
あるいは2,4−ジアミノジフェニルアミンを必須成分と
して含む試薬を検水に加え、検水の着色状態を比色する
ことで所期の目的を達成したものである。
Means for Solving the Problems The present inventors have repeated various tests in order to solve such problems, potassium permanganate, a water-soluble basic substance and diphenylamine-4-sulfonic acid or 2, The intended purpose was achieved by adding a reagent containing 4-diaminodiphenylamine as an essential component to the test water and comparing the colored state of the test water.

本発明の実施において使用する過マンガン酸カリウム
は、特級あるいは一級として市販されているもので、そ
の形態は固体粉末、水溶液のいずれでもよい。
The potassium permanganate used in the practice of the present invention is commercially available as a special grade or primary grade, and its form may be solid powder or aqueous solution.

本発明の実施に適する水溶性塩基性物質は水酸化アル
カリ(土類)金属、リン酸アルカリ金属塩、ホウ酸アル
カリ金属塩、炭酸アルカリ金属塩などの水溶性で、しか
もその水溶液が塩基性を示す化合物であって、その代表
的なものは水酸化ナトリウム、水酸化カリウム、水酸化
カルシウム、リン酸三ナトリウム、リン酸三カリウム、
炭酸ナトリウム、炭酸カリウム等である。
Water-soluble basic substances suitable for carrying out the present invention are water-soluble alkali metal hydroxides (earth metals), alkali metal phosphates, alkali metal borates, alkali metal carbonates, etc. Of the compounds shown, representative ones are sodium hydroxide, potassium hydroxide, calcium hydroxide, trisodium phosphate, tripotassium phosphate,
Examples include sodium carbonate and potassium carbonate.

本発明の実施に用いるジフェニルアミン−4−スルフ
ォン酸あるいは2,4−ジアミノジフェニルアミンは特級
あるいは一級として市販されているものが好適であり、
その形態は固体、粉末、水溶液いずれでもよい。
The diphenylamine-4-sulfonic acid or 2,4-diaminodiphenylamine used in the practice of the present invention is preferably a commercially available special grade or primary grade,
The form may be solid, powder or aqueous solution.

本発明の実施において必須成分である過マンガン酸カ
リウム、水溶性塩基性物質及びジフェニルアミン−4−
スルフォン酸あるいは2,4−ジアミノジフェニルアミン
を含む試薬を検水に加える手段は、あらかじめ粉末混合
物にしておき加える方法、あらかじめ混合物の水溶液に
しておき加える方法、各成分を個別に粉末で加える方
法、各成分を個別に水溶液で加える方法等のいずれの方
法を用いても差し支えないが、あらかじめ混合物の水溶
液にしておく方法が特に適している。
In carrying out the present invention, potassium permanganate, a water-soluble basic substance and diphenylamine-4-, which are essential components, are used.
The means for adding the reagent containing sulfonic acid or 2,4-diaminodiphenylamine to the test water is a method of adding it in a powder mixture in advance, a method of adding it in an aqueous solution of the mixture in advance, a method of adding each component individually in powder, Although any method such as a method of individually adding the components in an aqueous solution may be used, a method of preparing an aqueous solution of the mixture in advance is particularly suitable.

本発明の実施により着色した検水からその検水のCOD
を測定する方法としては、連続的な色相変化を有する基
準色相板を用いて検水の着色状態を比色する方法が望ま
しく、特に屋外での使用に耐えるため、無色アクリル樹
脂に着色剤を加えて成形した合成樹脂製基準色相板が好
適である。
COD from the test water colored according to the practice of the invention
As a method of measuring, it is desirable to compare the coloring state of the test water using a standard hue plate having a continuous hue change, especially in order to withstand outdoor use, a colorant is added to the colorless acrylic resin. A synthetic resin reference hue plate formed by molding is suitable.

作 用 アルカリ性において過マンガン酸カリウムが還元され
る場合、過マンガン酸カリウムの還元に伴い、その色相
が変化することは既に知られている。しかしながら、そ
の色相の変化は非常に鈍く、その変化からCOD値を予想
することは困難であった。
It is already known that, when potassium permanganate is reduced under alkaline conditions, its hue changes with the reduction of potassium permanganate. However, the change in the hue was very slow, and it was difficult to predict the COD value from the change.

本発明はこの鈍い色相の変化を鋭敏な変化にさせるこ
とにより、その色相の差を明らかなものとし、安定且つ
正確に測定できるようにしたものである。
The present invention makes this dull hue change sharp to make the difference in hue clear, and enables stable and accurate measurement.

すなわち、過マンガン酸カリウム、塩基性物質にジフ
ェニルアミン−4−スルフォン酸あるいは2,4−ジアミ
ノジフェニルアミンを添加することにより、鈍い色相の
変化を鋭敏な色相の差に変える作用が生起され、迅速且
つ簡便な比色測定が可能である。
That is, by adding diphenylamine-4-sulfonic acid or 2,4-diaminodiphenylamine to potassium permanganate or a basic substance, an effect of changing a gradual change in hue into a sharp difference in hue is caused, which is quick and simple. Various colorimetric measurements are possible.

ジフェニルアミン−4−スルフォン酸あるいは2,4−
ジアミノジフェニルアミンは、通常の化学分析では酸化
還元滴定法の指示薬として用いられている物質であり、
変色点の酸化還元電位は+0.70Vあるいは+0.80Vを示
し、両者とも酸化形は赤色を示し、還元形では無色とな
る。従ってアルカリ性における過マンガン酸カリウムの
酸化還元反応の当量点電位+0.57Vの近辺での変色は鋭
敏であり、過マンガン酸カリウムの変色と相互に作用し
合い鋭敏な色相の差が現れるものと考えられる。
Diphenylamine-4-sulfonic acid or 2,4-
Diaminodiphenylamine is a substance used as an indicator for redox titration in ordinary chemical analysis,
The redox potential at the color change point is +0.70 V or +0.80 V, both of which show red in the oxidized form and colorless in the reduced form. Therefore, it is considered that discoloration near the equivalence point potential of + 0.57V of the redox reaction of potassium permanganate in alkaline is sensitive and interacts with the discoloration of potassium permanganate to cause a sharp difference in hue. To be

実施例 1 COD源物質として、グルコースとポリペプトンと肉エ
キスを重量比で50:30:20の割合で混ぜ合わせたもの(以
下人工汚水COD源という)を水に溶解し、CODMn濃度が2,
5,10,15,20,25,30,40,50ppmの検水をそれぞれ調整し
た。次いで前記検水をそれぞれ10ml採取し、これに過マ
ンガン0.62mg、水酸化ナトリウム8mg及び2,4−ジアミノ
ジフェニルアミン0.04mgを混合物の水溶液0.2mlとして
加え、室温(25℃)で4分間放置し、その時点での各検
水の着色状態を観察したところ、表1に示したとおりで
あった。
Example 1 As a COD source substance, a mixture of glucose, polypeptone, and meat extract in a weight ratio of 50:30:20 (hereinafter referred to as artificial sewage COD source) was dissolved in water to give a COD Mn concentration of 2,
5,10,15,20,25,30,40,50 ppm sample water was prepared respectively. Then, 10 ml each of the test water was sampled, 0.62 mg of permanganese, 8 mg of sodium hydroxide and 0.04 mg of 2,4-diaminodiphenylamine were added as 0.2 ml of an aqueous solution of the mixture, and the mixture was allowed to stand at room temperature (25 ° C.) for 4 minutes, When the coloring state of each test water at that time was observed, it was as shown in Table 1.

この検水の色相を標準にして透光性合成樹脂からなる
基準色相板を9枚作成し、図面に示すようにこれらを連
続的配置した円形状の基準色相板を造った。(図面参
照) 次に、CODMn未知の人工汚水COD源水溶液を検水とし、
その10mlを採取し、これに前記と同じ試薬を加え、同様
の条件で着色させたところ、紫色を呈し基準色相板から
この検水のCODMnは10ppmと判定した。他方この人工汚水
COD源水溶液をJIS K0102に記載された方法によって測
定するとCODMnは9.8ppmであり、本発明の測定値とほぼ
一致した。
Nine reference hue plates made of a translucent synthetic resin were prepared by using the hue of this test water as a standard, and as shown in the drawing, circular reference hue plates were made by arranging these continuously. (Refer to the drawing) Next, COD Mn unknown artificial sewage COD source aqueous solution is used as a test water
10 ml of the sample was sampled, the same reagent as above was added thereto, and the sample was colored under the same conditions. As a result, a purple color was obtained, and the COD Mn of this sample water was judged to be 10 ppm from the reference hue plate. On the other hand this artificial wastewater
When the COD source aqueous solution was measured by the method described in JIS K0102, COD Mn was 9.8 ppm, which was almost the same as the measured value of the present invention.

実施例2〜7 実施例1において、試薬として表2に示した化合物を
所定の割合に混合したものを用い、同様の操作を繰り返
し行ったところ、いずれの実施例においても、検水に実
施例1と全く同じ着色変化が観察され、CODを測定する
試薬として使用できることを確認された。
Examples 2 to 7 In Example 1, a mixture of the compounds shown in Table 2 in a predetermined ratio was used as a reagent, and the same operation was repeated. The same color change as in 1 was observed, confirming that it can be used as a reagent for measuring COD.

比較例1 実施例1において、試薬として2,4−ジアミノジフェ
ニルアミンを除いたものを用いた以外は、すべて実施例
1と同様の操作を行って各検水の着色状況を観察したと
ころ、表3に示したとおりであった。
Comparative Example 1 The same operation as in Example 1 was performed except that the reagent except 2,4-diaminodiphenylamine was used as the reagent in Example 1, and the color condition of each test water was observed. It was as shown in.

この試験の結果CODMn値2〜25ppmの範囲では、検水の
色相に全く差がなく、この間のCODMnは測定不能と認め
られた。
As a result of this test, in the COD Mn value range of 2 to 25 ppm, there was no difference in the hue of the test water, and it was recognized that COD Mn during this period could not be measured.

実施例8 COD源を含むサンプルとして小型浄化槽処理水を用
い、水で希釈し、CODMnとして5,10,15,20,30,40,50,60,
80ppmの検水をそれぞれ調整した。それぞれの検水10ml
に過マンガン酸カリウム0.62mg、リン酸三ナトリウム64
mg、2,4−ジアミノジフェニルアミン0.04mgを加え、室
温(25℃)に4分間放置し、その時点での各検水の着色
状態は表4に示したとおりであった。
Example 8 Small septic tank treated water was used as a sample containing a COD source, diluted with water, and COD Mn was set to 5,10,15,20,30,40,50,60,
80 ppm test water was adjusted respectively. 10 ml of each test water
0.62 mg of potassium permanganate, trisodium phosphate 64
mg, 2,4-diaminodiphenylamine (0.04 mg) was added, the mixture was allowed to stand at room temperature (25 ° C.) for 4 minutes, and the coloring state of each test water at that time is as shown in Table 4.

この検水の色相を基準として、透明性合成樹脂からな
る基準色相板を9枚作成し、円形状の基準色相板に製作
した。
Nine reference hue plates made of a transparent synthetic resin were prepared on the basis of the hue of this test water, and the reference hue plates were circular.

次に、CODMn未知の小型浄化槽処理水を検水とし、こ
れに前記と同様にして各々の試薬を加え、室温(25℃)
4分間放置したところ、検水は青紫を呈し、基準色相板
からこの検水のCODMnは30ppmと判定した。他方JIS K01
02に記載されている方法によって、この検水のCODMn
測定すると33ppmであり、両者はほぼ一致していた。
Next, COD Mn unknown small septic tank treated water was used as test water, and each reagent was added to it in the same manner as above, and room temperature (25 ° C)
When left for 4 minutes, the test water exhibited bluish purple, and the COD Mn of the test water was judged to be 30 ppm from the standard hue plate. On the other hand, JIS K01
When the COD Mn of this sample water was measured by the method described in 02, it was 33 ppm, and both were almost the same.

比較例2 実施例8において試薬として2,4−ジアミノジフェニ
ルアミンを除いた以外は、実施例8と同様の条件で処理
を行って検水の着色状態を観察したところ、表5に示し
たとおりであった。
Comparative Example 2 The coloring state of the test water was observed by treating under the same conditions as in Example 8 except that 2,4-diaminodiphenylamine was removed as a reagent in Example 8, and the results are shown in Table 5. there were.

この結果、CODMn5〜40ppmの範囲では、着色の色相に
全く差がなくこの間のCODMnは測定できないことがわか
った。
As a result, it was found that in the range of COD Mn 5-40 ppm, there was no difference in the hue of coloring, and COD Mn during this period could not be measured.

実施例9 COD源を含むサンプルとしてケーキを製造する某菓子
製造メーカーの排水処理施設の処理水(CODMn50ppm)を
用い、水で希釈し、CODMnとして5,10,15,20,30,40,50pp
mの検水をそれぞれ調整した。
Example 9 Using treated water (COD Mn 50 ppm) of a wastewater treatment facility of a confectionery manufacturer that manufactures a cake as a sample containing a COD source, it was diluted with water to obtain COD Mn of 5,10,15,20,30, 40,50pp
The water samples of m were adjusted respectively.

それぞれの検水10mlに過マンガン酸カリウム0.62mg、
リン酸三ナトリウム64mg、2,4−ジアミノジフェニルア
ミン0.04mgづつを加え、室温(23℃)に4分間放置し、
その時点での各検水の着色状態は表6に示したとおりで
あり、実施例8で求めたCODMn値と検水の色相との関係
は全く同じであった。
0.62 mg of potassium permanganate in 10 ml of each test water,
Add 64 mg of trisodium phosphate and 0.04 mg of 2,4-diaminodiphenylamine, leave at room temperature (23 ° C) for 4 minutes,
The coloring state of each test water at that time is as shown in Table 6, and the relationship between the COD Mn value obtained in Example 8 and the hue of the test water was exactly the same.

従って、実施例8で作成した円形状の基準色相板を本
実施例でも用いた。
Therefore, the circular reference hue plate prepared in Example 8 was also used in this example.

次にCODMn未知のこの菓子製造メーカーの排水処理水
を検水とし、これに前記と同様にして各々の試薬を加
え、室温(23℃)4分間放置したところ、検水は青緑を
呈し、基準色相板からこの検水のCODMnは40ppmと判定し
た。他方JISK0102に記載されている方法により、この検
水のCODMnを測定すると38ppmであり、両者はほぼ一致し
ていた。
Next, the treated wastewater of this confectionery manufacturer unknown to COD Mn was used as test water, and each reagent was added to this as described above, and it was left at room temperature (23 ° C) for 4 minutes. The COD Mn of this test water was determined to be 40 ppm from the reference hue plate. On the other hand, when the COD Mn of this sample water was measured by the method described in JIS K0102, it was 38 ppm, and both were almost the same.

発明の効果 この発明によれば、検水の化学的酸素要求量を迅速且
つ簡便な操作で測定することができ、屋外、河川等のよ
うに加熱や滴定等の操作ができない場所においても、即
時に測定できるなど実践面の効果は多大である。
EFFECTS OF THE INVENTION According to the present invention, the chemical oxygen demand of the test water can be measured by a quick and simple operation, and it can be immediately used even in a place where the operation such as heating or titration cannot be performed outdoors, such as in a river. Practical effects such as measurement can be significant.

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

図面は本発明における基準色相板の一例を示す平面図で
ある。
The drawing is a plan view showing an example of the reference hue plate in the present invention.

Claims (3)

(57)【特許請求の範囲】(57) [Claims] 【請求項1】過マンガン酸カリウム、水溶性塩基性物質
及びジフェニルアミン−4−スルフォン酸あるいは2,4
−ジアミノジフェニルアミンを必須成分として含む試薬
を検水に加え、検水の着色状態を比色することを特徴と
する化学的酸素要求量の測定方法。
1. Potassium permanganate, a water-soluble basic substance and diphenylamine-4-sulfonic acid or 2,4.
A method for measuring a chemical oxygen demand, which comprises adding a reagent containing diaminodiphenylamine as an essential component to test water and comparing the colored state of the test water.
【請求項2】連続的な色相変化を有する基準色相板を用
いて、検水の着色状態を比色する請求項(1)に記載の
方法。
2. The method according to claim 1, wherein the coloring state of the test water is compared by using a reference hue plate having a continuous hue change.
【請求項3】過マンガン酸カリウム、水溶性塩基性物質
及びジフェニルアミン−4−スルフォン酸あるいは2,4
−ジアミノジフェニルアミンを必須成分として含むこと
を特徴とする化学的酸素要求量の測定用試薬。
3. Potassium permanganate, water-soluble basic substance and diphenylamine-4-sulfonic acid or 2,4
-A reagent for measuring chemical oxygen demand, which comprises diaminodiphenylamine as an essential component.
JP1283653A 1989-10-30 1989-10-30 Chemical oxygen demand measuring method and measuring reagent Expired - Lifetime JP2532952B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP1283653A JP2532952B2 (en) 1989-10-30 1989-10-30 Chemical oxygen demand measuring method and measuring reagent

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP1283653A JP2532952B2 (en) 1989-10-30 1989-10-30 Chemical oxygen demand measuring method and measuring reagent

Publications (2)

Publication Number Publication Date
JPH03144348A JPH03144348A (en) 1991-06-19
JP2532952B2 true JP2532952B2 (en) 1996-09-11

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DE10035911A1 (en) * 2000-07-21 2002-02-07 Abb Research Ltd Method and sensor for monitoring liquids
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CN104515769B (en) * 2014-11-27 2017-10-20 宁波大地化工环保有限公司 A kind of quick measure high-chloride wastewater COD method
CN114018905A (en) * 2021-09-28 2022-02-08 神美科技有限公司 Kit for rapidly detecting water quality COD (chemical oxygen demand), preparation method and use method thereof

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Chem.Listy.,(1969),63(10),P.1148−52

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