Skip to main content

Measurement of Concentration of Nitrate in Drinking Water

  • Chapter
  • First Online:
Traceability, Validation and Measurement Uncertainty in Chemistry: Vol. 3

Abstract

For nitrate we have here below text extracts of an ISO method and also the requirements in the directive for nitrate.

This is a preview of subscription content, log in via an institution to check access.

Access this chapter

Chapter
USD 29.95
Price excludes VAT (USA)
  • Available as PDF
  • Read on any device
  • Instant download
  • Own it forever
eBook
USD 79.99
Price excludes VAT (USA)
  • Available as EPUB and PDF
  • Read on any device
  • Instant download
  • Own it forever
Softcover Book
USD 99.99
Price excludes VAT (USA)
  • Compact, lightweight edition
  • Dispatched in 3 to 5 business days
  • Free shipping worldwide - see info
Hardcover Book
USD 109.99
Price excludes VAT (USA)
  • Durable hardcover edition
  • Dispatched in 3 to 5 business days
  • Free shipping worldwide - see info

Tax calculation will be finalised at checkout

Purchases are for personal use only

Institutional subscriptions

Notes

  1. 1.

    98/83/EC, of 3 November 1998, on the quality of water intended for human consumption.

Author information

Authors and Affiliations

Authors

Corresponding author

Correspondence to Andreja Drolc .

Editor information

Editors and Affiliations

1 Electronic Supplementary Material

Below is the link to the electronic supplementary material.

Supplementary material 1 (PPT 176 kb)

Supplementary material 2 (XLS 104 kb)

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:

$$C_{{}} = \frac{{A - B_{0} }}{{B_{1} }}$$

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:

$$B_{1} = \frac{{\sum\limits_{i = 1}^{n} {(C_{i} - \bar{C}) \cdot (A_{i} - \bar{A})} }}{{\sum\limits_{i = 1}^{n} {(C_{i} - \bar{C})^{2} } }}$$
$$B_{0} = \bar{A} - B_{1} \cdot \bar{C}_{{}}$$
$$\bar{A} = \frac{1}{n}\sum\limits_{i = 1}^{n} {A_{i} }$$
$$\bar{C}_{{}} = \frac{1}{n}\sum\limits_{i = 1}^{n} {C_{i} }$$

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:

 

4

Quantity/Equipment/calibration:

 
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 …

--------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------

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

 

Mark the customer’s requirements and give their values

Parameters to be validated

Value requested by the customer

LOD

5 mg L−1

LOQ

 

Repeatability

 

Within-lab reproducibility

5 mg L−1

Trueness

 

Measurement uncertainty

5 mg L−1

Other-state

 
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. :

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

 

Repeatability

 

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

 

Other-please state

 
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:

$$C_{{NO_{3} }} = \frac{{A - B_{0} }}{{B_{1} \cdot R}}$$

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:

$$B_{1} = \frac{{\sum\limits_{i = 1}^{n} {(C_{i} - \bar{C}) \cdot (A_{i} - \bar{A})} }}{{\sum\limits_{i = 1}^{n} {(C_{i} - \bar{C})^{2} } }}\quad \quad B_{0} = \bar{A} - B_{1} \cdot \bar{C}_{{}}$$
$$\bar{A} = \frac{1}{n}\sum\limits_{i = 1}^{n} {A_{i} } \quad \quad \bar{C} = \frac{1}{n}\sum\limits_{i = 1}^{n} {C_{i} }$$
$$R = \frac{{c_{observed} - c_{matrix} }}{{c_{spiked} }}$$

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

–

 
$$\begin{aligned} \frac{{u\left( {B_{1} \times \bar{C}} \right)}}{{B_{1} \times \bar{C}}} & = \sqrt {\left( {\frac{{u(B_{1} )}}{{B_{1} }}} \right)^{2} + \left( {\frac{{u(\bar{C})}}{{\bar{C}}}} \right)^{2} } = \sqrt {\left( {\frac{831}{112837}} \right)^{2} + \left( {\frac{0.016}{3.4770}} \right)^{2} } \\ & = \sqrt {5.4237 \times 10^{ - 5} + 2.1175 \times 10^{ - 5} } = \sqrt {7.5412 \times 10^{ - 5} } \\ \end{aligned}$$
$$u(B_{1} \times \bar{C}) = 112837 \times 3.4770 \times \sqrt {7.5412 \times 10^{ - 5} } = 3407$$
$$u(B_{0} ) = \sqrt {u(\bar{A})^{2} + u(B_{1} \times \bar{C})^{2} } = \sqrt {146^{2} + 3407^{2} } = 3410$$
6. :

Calculate the value of the measurand, using the model equation

$$C_{{NO_{3} }} = \frac{{A - B_{0} }}{{B_{1} \cdot R}}\quad \quad {\text{C}}_{\text{NO3}} = 5.4\,{\text{mg}}\,{\text{L}}^{ - 1}$$
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

$$\begin{aligned} \frac{u\left( c \right)}{c} & = \sqrt {\left( {\frac{{u(B_{1} )}}{{B_{1} }}} \right)^{2} + \left( {\frac{u(R)}{R}} \right)^{2} + \left( {\frac{{u(A - B_{0} )}}{{A - B_{0} }}} \right)^{2} } = \sqrt {\left( {\frac{831}{112837}} \right)^{2} + \left( {\frac{0.01}{1}} \right)^{2} + \left( {\frac{5425.54}{594350 + 14967}} \right)^{2} } \\ & = \sqrt {23.35235 \times 10^{ - 5} } \\ \end{aligned}$$
$$u(A - B_{0} ) = \sqrt {u(A)^{2} + u(B_{0} )^{2} } = \sqrt {4220^{2} + 3410^{2} } = 5425.54$$
$$u(c) = 0.015281475 \times 5.4 = 0.082\,{\text{mg}}\,{\text{L}}^{ - 1}$$

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)

Rights and permissions

Reprints and permissions

Copyright information

© 2019 Springer Nature Switzerland AG

About this chapter

Check for updates. Verify currency and authenticity via CrossMark

Cite this chapter

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

Download citation

Publish with us

Policies and ethics