ISO 12846:2012
Current
The latest, up-to-date edition.
Water quality — Determination of mercury — Method using atomic absorption spectrometry (AAS) with and without enrichment
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French, English
18-04-2012
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.
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).
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.
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.
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.
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.
DevelopmentNote |
Supersedes ISO/DIS 12846, ISO 16590 and ISO 5666. (04/2012)
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DocumentType |
Standard
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Pages |
16
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PublisherName |
International Organization for Standardization
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Status |
Current
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Supersedes |
Standards | Relationship |
NF EN ISO 12846 : 2012 | Identical |
NBN EN ISO 12846 : 2012 | Identical |
NEN EN ISO 12846 : 2012 | Identical |
NS EN ISO 12846 : 2012 | Identical |
I.S. EN ISO 12846:2012 | Identical |
PN EN ISO 12846 : 2012 | Identical |
SN EN ISO 12846:2012 | Identical |
UNI EN ISO 12846 : 2013 | Identical |
SS-EN ISO 12846 : 2012 | Identical |
UNE-EN ISO 12846:2012 | Identical |
BS EN ISO 12846:2012 | Identical |
EN ISO 12846:2012 | Identical |
DIN EN ISO 12846:2012-08 | Identical |
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I.S. EN 12926:2015 | CHEMICALS USED FOR TREATMENT OF WATER INTENDED FOR HUMAN CONSUMPTION - SODIUM PEROXODISULFATE |
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BS EN 897:2012 | Chemicals used for treatment of water intended for human consumption. Sodium carbonate |
UNE-EN 12926:2015 | Chemicals used for treatment of water intended for human consumption - Sodium peroxodisulfate |
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BS EN 12926:2015 | Chemicals used for treatment of water intended for human consumption. Sodium peroxodisulfate |
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EN 896:2012 | Chemicals used for treatment of water intended for human consumption - Sodium hydroxide |
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BS EN 16811-2:2016 | Winter service equipment and products. De-icing agents Calcium chloride and Magnesium chloride. Requirements and test methods |
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UNE-EN 16711-1:2016 | Textiles - Determination of metal content - Part 1: Determination of metals using microwave digestion |
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DIN EN 897:2013-02 | CHEMICALS USED FOR TREATMENT OF WATER INTENDED FOR HUMAN CONSUMPTION - SODIUM CARBONATE |
BS EN 901:2013 | Chemicals used for treatment of water intended for human consumption. Sodium hypochlorite |
BS EN 900:2014 | Chemicals used for treatment of water intended for human consumption. Calcium hypochlorite |
BS EN 1197:2014 | Chemicals used for treatment of water intended for human consumption. Monozinc phosphate solution |
BS EN 12672:2008 | Chemicals used for treatment of water intended for human consumption. Potassium permanganate |
BS EN 15002:2015 | Characterization of waste. Preparation of test portions from the laboratory sample |
EN 13176:2015 | Chemicals used for treatment of water intended for human consumption - Ethanol |
EN 1197:2014 | Chemicals used for treatment of water intended for human consumption - Monozinc phosphate solution |
DIN EN 900:2000-03 | CHEMICALS USED FOR TREATMENT OF WATER INTENDED FOR HUMAN CONSUMPTION - CALCIUM HYPOCHLORITE |
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EN 12672:2016 | Chemicals used for treatment of water intended for human consumption - Potassium permanganate |
EN 13194:2015 | Chemicals used for treatment of water intended for human consumption - Acetic Acid |
UNE-EN 15030:2013 | Chemicals used for treatment of water intended for human consumption - Silver salts for intermittent use |
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ISO 5667-3:2012 | Water quality Sampling Part 3: Preservation and handling of water samples |
ISO 5667-1:2006 | Water quality Sampling Part 1: Guidance on the design of sampling programmes and sampling techniques |
ISO 8466-2:2001 | Water quality — Calibration and evaluation of analytical methods and estimation of performance characteristics — Part 2: Calibration strategy for non-linear second-order calibration functions |
ISO 5725-2:1994 | Accuracy (trueness and precision) of measurement methods and results Part 2: Basic method for the determination of repeatability and reproducibility of a standard measurement method |
ISO 3696:1987 | Water for analytical laboratory use — Specification and test methods |
ISO 8466-1:1990 | Water quality Calibration and evaluation of analytical methods and estimation of performance characteristics Part 1: Statistical evaluation of the linear calibration function |
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