NF EN 12338

NF EN 12338

October 1998
Standard Cancelled

Water quality - Determination of mercury - Enrichment methods by amalgamation

Le présent document s'adresse aux laboratoires ayant à doser le mercure total, à de faibles concentrations dans les eaux.

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Main informations

Collections

National standards and national normative documents

Publication date

October 1998

Number of pages

25 p.

Reference

NF EN 12338

ICS Codes

13.060.50   Examination of water for chemical substances

Classification index

T90-113-3

Print number

1 - 07/12/2002

European kinship

EN 12338:1998
Sumary
Water quality - Determination of mercury - Enrichment methods by amalgamation

Le présent document s'adresse aux laboratoires ayant à doser le mercure total, à de faibles concentrations dans les eaux.
Standard replaced by (1)
NF EN ISO 12846
June 2012
Standard Current
Water quality - Determination of mercury - Method using atomic absorption spectrometry (AAS) with and without enrichment

<p>ISO 12846:2012 specifies two methods for the determination of mercury in drinking, surface, ground, rain and waste water after appropriate pre-digestion. For the first method, an enrichment step by amalgamation of the Hg on, for example, a gold/platinum adsorber is used. For the second method, the enrichment step is omitted.</p> <p>The choice of method depends on the equipment available, the matrix and the concentration range of interest. Both methods are suitable for the determination of mercury in water. The method with enrichment commonly has a practical working range from 0,01 µg/l to 1 µg/l. The mean limit of quantification (LOQ) reported by the participants of the validation trial was 0,008 µg/l. This information on the LOQ gives the user of ISO 12846:2012 an orientation and does not replace the estimation of performance data from laboratory specific data. It has to be considered that it is possible to achieve lower LOQs with specific instrumentation (e.g. single mercury analysers).</p> <p>The method without enrichment commonly has a practical working range starting at 0,05 µg/l. The LOQ reported by the participants of the validation trial was 0,024 µg/l. It is up to the user, based on the specific application, to decide whether higher concentrations are determined by omitting the enrichment step and/or by diluting the sample(s). The sensitivity of both methods is dependent on the selected operating conditions.</p> <p>Another possibility for the determination of extremely low Hg concentrations down to 0,002 µg/l without pre-concentration is the application of atomic fluorescence spectrometry (see ISO 17852). Specific atomic-absorption mercury analysers allow determinations down to 0,010 µg/l without pre-concentration.</p> <p>In general, the determination of trace concentrations of Hg by AAS (or AFS) is dependent on clean operating conditions in the laboratory and on the use of high-purity chemicals with negligible low-Hg blanks.</p> <p>Note that ISO 12846:2012 may be applied to industrial and municipal waste water after an additional digestion step performed under appropriate conditions and after suitable method validation. A potential sample stability issue (mercury loss) for anaerobic reducing industrial effluents has to be considered thoroughly.</p>

Table of contents
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  • Avant-propos
    3
  • 0 Introduction
    4
  • 1 Domaine d'application
    4
  • 2 Références normatives
    4
  • 3 Interférences générales
    5
  • 4 Dosage du mercure après réduction avec le chlorure d'étain(II) et enrichissement par amalgame
    6
  • 4.1 Gamme de mesure
    6
  • 4.2 Principe
    6
  • 4.3 Interférences
    6
  • 4.4 Réactifs
    6
  • 4.5 Appareillage
    8
  • 4.6 Échantillonnage et prétraitement de l'échantillon
    9
  • 4.7 Méthode de digestion au permanganate peroxodisulfate
    9
  • 4.8 Mode opératoire
    11
  • 4.9 Calculs
    12
  • 4.10 Expression des résultats
    12
  • 4.11 Rapport d'essai
    12
  • 5 Dosage du mercure après réduction avec le tétrahydroborate de sodium et enrichissement par amalgame
    13
  • 5.1 Gamme de mesure
    13
  • 5.2 Principe
    13
  • 5.3 Interférences
    13
  • 5.4 Réactifs
    13
  • 5.5 Appareillage
    14
  • 5.6 Échantillonnage et prétraitement de l'échantillon
    14
  • 5.7 Méthode de digestion au permanganate peroxodisulfate
    14
  • 5.8 Mode opératoire
    16
  • 5.9 Calculs
    16
  • 5.10 Expression des résultats
    16
  • 5.11 Rapport d'essai
    16
  • 6 Données de fidélité
    17
  • Annexe A (informative) Méthode de digestion par ultrasons
    19
  • Annexe B (informative) Méthode de digestion avec un autoclave
    20
  • Annexe C (informative) Méthode de digestion par micro-ondes
    21
  • Annexe D (informative) Bibliographie
    23
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