GB/T 5750.5-2023Standard examination methods for drinking water—Part 5: Inorganic nonmetallic indices (English PDF)
生活饮用水标准检验方法 第5部分:无机非金属指标
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Issued by
SAMR; SAC
Level / Type
National · Recommended
Issue date
March 17, 2023
Implementation date
October 1, 2023
Scope
GB/T 5750.5-2023 is the English-translated version of 生活饮用水标准检验方法 第5部分:无机非金属指标.
GB/T 5750.5-2023 is the Chinese standard "Standard examination methods for drinking water—Part 5: Inorganic nonmetallic indices".
Its scope clause reads: This document describes the determination of sulfate, chloride, fluoride, cyanide, nitrate (in N), sulfide, phosphate, (in N) nitrite (in N), iodide, perchlorate in drinking water and water source water sulfate, chloride, fluoride, cyanide (isonicotinic acid - Vishwakarma spectrophotometric method, isonicotinic acid - barbiturate spectrophotometric method), nitrate (in N ), sulfide, phosphate, ammonia (as N) sub-certainty (as N) iodide determination method.
This document applies to the determination of inorganic non-metallic indicators in drinking water and (or) water source water. Its clauses include normative reference documents; terms and definitions; sulfate; chloride; fluoride; compounds; nitrate (as n); n,n-diethyl-p-phenylenediamine spectrophotometric method; phosphate; ammonia (as n).
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Document preview — GB/T 5750.5-2023
National Standard of the People's Republic of China
- ICS
- 13.060
- Classification
- C 51
- Replacing
- GB/T 5750.5-2006
Issued by: State Administration for Market Regulation; Standardization Administration of the PRC
Contents
- Foreword
- Introduction
- 1 Scope
- 2 normative reference documents
- 3 Terms and definitions
- 4 Sulfate
- 5 Chloride
- 6 Fluoride
- 7 compounds
- 8 Nitrate (as N)
- 9 N,N-diethyl-p-phenylenediamine spectrophotometric method
- 10 Phosphate
- 11 ammonia (as N)
- 12 nitrite (in N)
- 13 Iodide
- 14 Perchlorate
1 Scope
This document describes the determination of sulfate, chloride, fluoride, cyanide, nitrate (in N), sulfide, phosphate, (in N) nitrite (in N), iodide, perchlorate in drinking water and water source water sulfate, chloride, fluoride, cyanide (isonicotinic acid - Vishwakarma spectrophotometric method, isonicotinic acid - barbiturate spectrophotometric method), nitrate (in N ), sulfide, phosphate, ammonia (as N) sub-certainty (as N) iodide determination method.
This document applies to the determination of inorganic non-metallic indicators in drinking water and (or) water source water
2 normative reference documents
The following documents constitute the essential provisions of this document through the normative references in the text. Among them, note the date of the reference document, only the date of the corresponding version applies to this document; do not note the date of the reference document, its latest version (including all the revision of the list) applies to this document.
GB/T 5750.1 standard test methods for drinking water Part 1: General Provisions
GB/T 5750.3 standard test methods for drinking water Part 3: Quality control of water quality analysis
GB / T6682 analysis of laboratory water specifications and test methods
3 Terms and definitions
GB / T 5750.1 and GB / T 5750.3 defined terms and definitions apply to this document
4 Sulfate
4.1 Barium sulfate turbidimetric method
4.1.1 Minimum detection mass concentration
The minimum detection mass of this method is 0.25mg, if the 50mL water sample is taken to determine the minimum detection mass concentration of 5mg / L. This method is applicable to the determination of sulfate mass concentration of less than 40mg / L water samples. Stirring speed, time, temperature and reagent addition method can affect the determination of barium sulfate turbidimetric method, therefore requires strict control of the operating conditions consistent.
5 Chloride
5.1 Silver nitrate volumetric method
5.1.1 Minimum detection mass concentration
The minimum detection mass of this method is 0.05mg, if 50mL sample is taken to determine the minimum detection mass concentration of 1.0mg / L. Australide and iodide can cause the same reaction, and the mass of the equivalent of chloride into the results. Sulfide, sulfite, thiosulfate and more than 15mg / L of oxygen consumption can interfere with the determination of this method. Sulfite and other interference can be removed by hydrogen peroxide treatment. Higher oxygen consumption of water samples can be treated with potassium permanganate or steamed dry after ashing.
6 Fluoride
6.1 ion selective electrode method
6.1.1
The minimum detection mass concentration of this method is 2g, if the 10mL water sample is measured, the minimum detection mass concentration of 0.2mg/L. Chromaticity, turbidity and more interfering substances can be directly determined by this method. In order to eliminate the interference of OH~ on the determination, the pH value of the measured water sample is controlled at 5.5~6.5.
7 compounds
7.1 Isonicotinic acid - Vishnu ketone spectrophotometric method
7.1.1
The minimum detectable mass concentration of this method is 0.1g, if 250L water sample is taken for evaporation, the minimum detectable mass concentration is 0.002mg/L. Oxidants such as residual chlorine can destroy cyanide, and 0.1g/L sodium sulfite or less than 0.1g/L sodium thiosulfate can be added to the water sample to remove the interference.
7.1.2 Principle
In the solution of pH=7.0, the cyanide is transformed into cyanuric chloride by chloramine T, and then interacted with isonicotinic acid-ketone (1-phenyl-3-methyl-5-viologen ketone) to produce blue dye for colorimetric quantification.
8 Nitrate (as N)
8.1 Muscimol spectrophotometric method
8.1.1 Minimum detection mass concentration
The minimum detection mass of this method is 0.5g of nitrate (in N), if 1.0 water samples are taken to determine the minimum detection mass concentration of 0.5mg / L.
Nitrite is positive interference with this method, the use of sulfamic acid money to remove: chloride is negative interference with this method, the use of silver sulfate to eliminate sulfide
9 N,N-diethyl-p-phenylenediamine spectrophotometric method
9.1.1 Minimum detection mass concentration
The minimum detection mass of this method is 1.0g, if the 50mL water sample is taken for determination, the minimum detection mass concentration is 0.02g/L.
9.1.2
Principle of sulfide and N,N-diethyl-p-phenylenediamine and ferric chloride to produce a stable blue color, colorimetric quantification at 665nm
9.1.3 Reagent
10 Phosphate
10.1 Phosphorus key blue spectrophotometric method
10.1.1 Minimum detection mass concentration
This method is suitable for the determination of phosphate (HPOF) mass concentration of less than 10mg / L of water samples.
10.1.2 Principle
In a strongly acidic solution of phosphate and acid money to generate phosphorus key heteropolyacid, can be reduced by reducing agents (stannous chloride, etc.) to produce a blue complex, when the phosphate content is low, its color intensity is proportional to the phosphate content.
10.1.3 Reagents
11 ammonia (as N)
11.1 Nah reagent spectrophotometric method
11.1.1 Minimum detectable mass concentration
The minimum detection mass of this method is 1.0g of nitrogen (in N) If a 50L water sample is taken for determination, the minimum detection mass concentration is
0.02mg/L.
12 nitrite (in N)
12.1 diazo coupling spectrophotometry
12.1.1 Minimum detection mass concentration
The minimum detection mass of this method is 0.05g of nitrite (in N) If 50L water samples are taken to determine the minimum detection mass concentration of 0.001mg / L.
Trichloramine in water produces red interference. Iron, lead plasma can produce precipitation caused by interference. Copper ions play a catalytic role in the decomposition of diazo salts to low results. Colored ions have interference.
13 Iodide
13.1 Sulfuric acid pavement catalytic spectrophotometry
13.1.1 Minimum detection mass concentration
Iodide content in the range of 0g / L ~ 20g / L, the minimum detection quality of this method is 2.4ng (to count) if 2.0mL water samples are taken to determine the minimum detection quality concentration of 1.2g / L; g / L ~ 200g / L range detection method minimum detection quality of 1.6ng (to count), if 0.3mL water samples are taken to determine the minimum detection quality concentration of 5.3g / L.
This method is suitable for the determination of iodide in the low concentration range of 0g/L~20g/L and in the high range of g/L~200g/L
14 Perchlorate
14.1 ion chromatography - hydroxide system drenching solution
14.1.1 Minimum detection mass concentration
This method is only used for the determination of perchlorate in domestic drinking water.
......
This preview omits tables, figures, formulas and parts of the technical clauses. The complete document — 50 pages — is available in the English PDF.
Referenced standards
Cited by
- GB 16005-2025Determination and classification of the endemic areas of iodine deficiency disorders
- GB/T 46659-2025Control of water-borne iodine excess areas and iodine excess endemic areas
- GB/T 42868-2023Technical condition for marine reclaimed-water reused treatment equipment
- GB/T 5750.6-2023Standard examination methods for drinking water—Part 6: Metal and metalloid indices
- GB 5749-2022Standards for drinking water quality
- GB/T 41837-2022Hot spring service—Hot spring water quality requirement
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Editions of GB/T 5750.5
| Edition | Title | Revision | Status |
|---|---|---|---|
| GB/T 5750.5-2023 | Standard examination methods for drinking water—Part 5: Inorganic nonmetallic indices | current edition | Current |
| GB/T 5750.5-2006 | Standard examination methods for drinking water—Part 5: Inorganic nonmetallic indices | previous edition | Superseded |
This page sells the current edition, GB/T 5750.5-2023. Earlier editions are listed for reference only.
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Related Standards
GB/T 5750.10-2006 — Standard examination methods for drinking Water -- Disinfection by-products parameters
GB/T 5750.10-2023 — Standard examination methods for drinking water—Part 10: Disinfection by-products indices
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