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Database: 365,228(8 Aug 2026)
halogenated acetic acids acetic acids water quality haloacetic acids gas chromatography introduction background 10288-2016+xg1-2020 test method aerosol optical depth remote sensing verification technical specifications analysis polypropylene melt-blown nonwoven materials
HJ 758-2015 in English

HJ 758-2015 in English

VALID

Water quality - Determination of haloacetic acids - Gas chromatography

  • Issued on:2015-10-22
  • Implemented on:2015-12-01
  • File Format:PDF
  • Delivery:Via email within 1~3 business days
Price(USD): $330.00
$321.00
Standard No: HJ 758-2015
Document status: VALID
Title in English: Water quality - Determination of haloacetic acids - Gas chromatography
Title in Chinese: 水质 卤代乙酸类化合物的测定 气相色谱法
Language: English
File Format: Electronic (PDF)
Delivery: Via email within 1~3 business days
Issued on: 2015-10-22
Implemented on: 2015-12-01
Professional Classification: HJ-Environment
Related Keywords: halogenated acetic acids
acetic acids
water quality
haloacetic acids
gas chromatography introduction background
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本标准规定了测定水中卤代乙酸类化合物的气相色谱法。
本标准适用于地表水、地下水、生活污水和工业废水中一氯乙酸、一溴乙酸、二氯乙酸、
三氯乙酸、一溴一氯乙酸、一溴二氯乙酸、二溴乙酸、一氯二溴乙酸和三溴乙酸共九种卤代乙酸类化合物的测定。
当取样量为40 ml 时,本方法的检出限为2 μg/L,测定下限为8 μg/L。


Introduction

Background and significance of the standard

As a supporting technical specification for the Environmental Protection Law of the People's Republic of China, this standard establishes a systematic detection method for 9 halogenated acetic acids in water for the first time, filling the gap in my country's monitoring standards in this field. Its release and implementation has important regulatory value for the prevention and control of drinking water disinfection by-product pollution.


Core principle of the method

The gas chromatograph-electron capture detector (GC-ECD) system is used to convert halogenated acetic acids into methyl halogenated acetic acid esters for detection through extraction with methyl tert-butyl ether (MTBE) under acidic conditions and derivatization with sulfuric acid and methanol. The key steps include:

StepsConditional parametersQuality control points
Derivatization50℃±2℃ water bath for 120minTime temperature deviation ≤10min/2℃
Chromatographic separationDual column system (14% cyanopropylphenyl/5% phenyl stationary phase)Relative retention time deviation ≤2%
Detection limit2μg/L (sampling volume 40ml)Blank value

Key technological innovations

1. Anti-interference design: Eliminate the interference of organic pollutants through pH adjustment-n-hexane pre-extraction, and monitor the recovery rate of the substitute 2-bromobutyric acid throughout the process (required to be 70-130%)

2. Double internal standard system: Use 1,2,3-trichloropropane as a quantitative internal standard, and add it before derivatization to ensure process control


Implementation tips

  1. Experimental safety: All operations must be carried out in a fume hood, and protective equipment must be worn when contacting reagents such as MTBE and concentrated sulfuric acid
  2. Derivatization control: Strictly control the derivatization temperature (50±2℃) and time (120±10min). Exceeding the temperature limit will cause the recovery rate to drop by more than 15%
  3. Chromatographic maintenance: It is recommended to replace the liner after every 200 injections, and the purity of the ECD detector tail gas must be ≥99.999%

Method Validation Data

Validation by 6 laboratories showed that for a spike concentration of 160μg/L, the recoveries of the nine target substances in industrial wastewater were 90.8-97.6%, and the inter-laboratory RSD was ≤14%. The repeatability limit of the typical compound trichloroacetic acid (TCAA) was 27μg/L.

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