Abstract
For nitrate we have here below text extracts of an ISO method and also the requirements in the directive for nitrate.
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- 1.
98/83/EC, of 3 November 1998, on the quality of water intended for human consumption.
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Appendices
Exercise 1: Establishing Traceability in Analytical Chemistry
- 1. :
-
Specifying the analyte and measurand
Analyte | Nitrate |
Measurand | Nitrate in drinking water, rain water, ground water and surface water |
Units | mg L−1 |
- 2. :
-
Choosing a suitable measurement procedure with associated model equation
Measurement procedure | EN ISO 10304-1 Water quality – Water quality – Determination of dissolved anions by liquid chromatography of ions – Determination of bromide, chloride fluoride, nitrate, nitrite, phosphate and sulphate. | ||
Type of calibration | Standard curve | Standard addition | Internal standard |
Model equation
The concentration of nitrate, C, is calculated by:
where A, B1 and B0 are measured area of the sample chromatographic peak, slope of the linear least square calibration curve and calculated blank. Slope of the linear least square calibration curve B1 and calculated blank B0 are calculated from equations:
where Ci and Ai are concentration of reference solution on ith level (C1, …, Ci, …, Cn) and areas of chromatographic peaks of ith reference solution (A1, …, Ai, …, An), respectively.
- 3. :
-
List the input quantities according to their influence on the uncertainty of the result of the measurement (first the most important ones). At this point, your judgement should be based on your previous experience only
1 | Uncertainty of concentration of reference solutions |
2 | Uncertainty of volumes |
3 | Uncertainty of weighing |
4 | – |
5 | – |
- 4. :
-
List the reference standards needed and state the information regarding traceability of the reference value
For the analyte
1 | Name/ChemicalFormula/producer: | NIST Standard Reference Material 3185 ‘Nitrate anion solution’ |
2 | Name/ChemicalFormula/producer: | – |
For the other input quantities
1 | Quantity/Equipment/calibration: e.g. mass/balance/calibrated by NMI, U = xx (k = 2), see also data yellow sheet | Volume/calibrated glassware and pipettes/with established traceability |
2 | Quantity/Equipment/calibration: | Mass/calibrated balance/with established traceability |
3 | Quantity/Equipment/calibration: | Â |
4 | Quantity/Equipment/calibration: | Â |
- 5. :
-
Estimating uncertainty associated with the measurement
Are all important parameters included in the model equation? | Yes | No |
Other important parameters are: | Matrix effects |
- 6. :
-
How would you prove traceability of your result?
1 | Analysis of matrix CRM |
2 | Participation in a proficiency testing scheme (Aquacheck,…) |
3 | – |
- 7. :
-
Any other comments, questions …
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Exercise 2: Single Laboratory Validation of Measurement Procedures
2.1 Part I: General Issues
- 1. :
-
Specify the measurement procedure, analyte, measurand and units
The measurement procedure | Measurement procedure is based on EN ISO 10304-1 Water quality – Determination of dissolved fluoride, chloride, nitrite, orthophosphate, bromide, nitrate and sulphate ions, using liquid chromatography of ions – Part I: Method for water with low contamination |
Analyte | nitrate |
The measurand | Nitrate in drinking water |
Unit | mg L−1 |
- 2. :
-
Specify the scope
Matrix | Drinking water |
Measuring range | >0.1 mg L−1 |
- 3. :
-
Requirement on the measurement procedure
Intended use of the results | Â | ||
Mark the customer’s requirements and give their values | Parameters to be validated | Value requested by the customer | |
| LOD | 5 mg L−1 | |
| LOQ | Â | |
| Repeatability | Â | |
| Within-lab reproducibility | 5 mg L−1 | |
| Trueness | Â | |
| Measurement uncertainty | 5 mg L−1 | |
| Other-state | Â |
- 4. :
-
Origin of the Measurement Procedure
 |  | Validation |
---|---|---|
New In-House Method |
| Full |
Modified Validated Method |
| Partial |
Official Standard Method |
| Confirmation/Verification |
2.2 Part II: Parameters to be Validated
- 5. :
-
Selectivity/Interference/Recovery
Where yes, please give further information e.g. which CRM, reference method
| CRM/RM: analysis of available CRM or RM |
Further information: Promochem QCP 051 – Anions | |
| Spike of pure substance |
spiking of samples with pure substances and calculation of recovery | |
| Compare with a reference method |
. | |
| Selectivity, interferences |
. | |
| Test with different matrices |
. | |
| Other – please specify |
. |
- 6. :
-
Measuring range
| Linearity |
| Upper limit |
| LOD |
| LOQ |
- 7. :
-
Spread – Precision
| Repeatability |
| Reproducibility (within Lab) |
| Reproducibility (between Lab) |
- 8. :
-
Robustness
| Variation of parameters |
- 9. :
-
Quality Control
| Control charts |
| Participation in PT schemes |
- 10. :
-
Other parameters to be tested
| Working range and testing of homogeneity of variances |
| R square |
| Residual standard deviation |
| Standard deviation of the analytical procedure |
| Coefficient of variation of the analytical procedure |
| Measurement uncertainty |
2.3 Part III: Some Calculations and Conclusions
- 11. :
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Calculation of parameters requested by the customer
Parameters requested to be validated | Calculations | |||
---|---|---|---|---|
| LOD | LOD = 0.5 mg L−1 | ||
Calculations | ||||
Abl (aver) | 33,869 | |||
Sbl | 915.4294 | |||
ALOD = Abl + 3Sbl | 36615.29 | |||
LOD | 0.5 mg L−1 | |||
| LOQ | Â | ||
| Repeatability | Â | ||
| Within-lab reproducibilty | s = 0.06 mg L−1 | ||
Calculations | ||||
c (aver) | 5.40 | |||
s | 0.06 mg L−1 | |||
| Trueness | R = 1.005 Significant test was used to show that R is not significantly different from 1 | ||
| Measurement uncertainty | Â | ||
| Other-please state | Â |
- 12. :
-
Does the analytical procedure fulfil the requirement(s) for the intended use?
Parameter | Value requested by the customer (the same as stated in question 3) | Value obtained during validation | The requirement is fulfilled Yes/No |
---|---|---|---|
LOD | 5 mg L−1 | 0.5 mg L−1 |  |
LOQ | – | – |  |
Repeatability | – | – |  |
Within-lab reproducibility | 5 mg L−1 | 0.06 mg L−1 |  |
Trueness | 5 mg L−1 | 0 (R = 1) |  |
 Measurement uncertainty | – | – |  |
Other | – | – |  |
The analytical procedure is fit for the intended use:
Yes No
For Measurement Uncertainty and Traceability refer to the corresponding sheets.
Exercise 3: Building an Uncertainty Budget
- 1. :
-
Specify the measurand and units
Measurand | Nitrate in drinking water |
---|---|
Unit | mg L−1 |
- 2. :
-
Describe the measurement procedure and provide the associated model equation
Measurement procedure:
Concentration of nitrate in water is measured by liquid chromatography (calibration curve).
For the final result, recovery is taken into account.
Model equation:
where A, B1, B0 and R are measured area of the sample chromatographic peak, slope of the linear least square calibration curve, calculated blank and method recovery, respectively. Slope of the linear least square calibration curve B1 and calculated blank B0 are calculated from eqns:
where Ci and Ai are concentration of reference solution on ith level (C1, …, Ci, …, Cn) and areas of chromatographic peaks of ith reference solution (A1, …, Ai, …, An), respectively.
- 3. :
-
Identify (all possible) sources of uncertainty
| Uncertainty of concentration of reference solutions |
| Uncertainty of measurements of peak area |
| Method bias |
| Matrix effect |
| Other: |
| Other: |
- 4. :
-
Evaluate values of each input quantity
Input quantity | Value | Unit | Remark |
---|---|---|---|
A | 594,350 | – |  |
B0 | −14,967 | – |  |
B1 | 112,837 | – |  |
R | 1 | – |  |
\(\bar{C}\) | 3.4770 | mg L−1 |  |
\(\bar{A}\) | 377,367 | – |  |
- 5. :
-
Evaluate the standard uncertainty of each input quantity
Input quantity | Standard uncertainty | Unit | Remark |
---|---|---|---|
A | 4220 | – |  |
B0 | 3410 | – |  |
B1 | 831 | – |  |
R | 0.01 | – |  |
\(\bar{C}\) | 0.016 | mg L−1 |  |
\(\bar{A}\) | 146 | – |  |
- 6. :
-
Calculate the value of the measurand, using the model equation
- 7. :
-
Calculate the combined standard uncertainty (u c ) of the result & specify units
Using: Mathematical solution; Spreadsheet Approach; Commercial Software
Input quantity | Value | Standard uncertainty | Unit | Remark |
---|---|---|---|---|
A | 594,350 | 4220 | – | Included in the MU data sheet |
B0 | −14967 | −130 | – | To be calculated by the participants (for details see xls green sheet) |
B1 | 112,837 | 831 | – | Included in the MU data sheet |
R | 1 | 0.01 | – | Included in the MU data sheet |
u(c) = 0.082 mg L−1
- 8. :
-
Calculate expanded uncertainty (U c ) & specify the coverage factor k and the units
\({\mathbf{U}}_{{\mathbf{c}}} = {\mathbf{0}}.{\mathbf{2}}\,{\text{mg}}\,{\text{L}}^{ - 1} \,\,({\mathbf{k}} = {\mathbf{2}})\)
- 9. :
-
Analyse the uncertainty contribution & specify the main three input quantities contributing the most to U c
1 | Method recovery |
2 | Calibration curve |
3 | Measurement of the peak area of the sample |
- 10. :
-
Prepare your Uncertainty Budget Report
3.1 Addendum I: Measurement Uncertainty Calculation: Spreadsheet Approach (Excel)
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Drolc, A. (2019). Measurement of Concentration of Nitrate in Drinking Water. In: Hrastelj, N., Bettencourt da Silva, R. (eds) Traceability, Validation and Measurement Uncertainty in Chemistry: Vol. 3. Springer, Cham. https://doi.org/10.1007/978-3-030-20347-4_2
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DOI: https://doi.org/10.1007/978-3-030-20347-4_2
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