efsa-opinion-chromium-food-drinking-water
efsa-opinion-chromium-food-drinking-water
efsa-opinion-chromium-food-drinking-water
You also want an ePaper? Increase the reach of your titles
YUMPU automatically turns print PDFs into web optimized ePapers that Google loves.
Chromium in <strong>food</strong> and <strong>drinking</strong> <strong>water</strong><br />
percentage of conversion from Cr(III) (LOD of 0.4 µg/L) to Cr(VI) (LOD of 0.04 µg/L) increased<br />
from 5.9 % to 9.3 % with increase of the concentration of Cr(VI) and Cr(III) from 1 to 100 µg/L,<br />
while the reverse conversion from Cr(VI) to Cr(III) was observed within a range between 0.9 % and<br />
1.9 %. The equilibrium constant for the conversion was found to be independent of the initial<br />
concentrations of Cr(III) and Cr(VI) and in the range of 1.0 (at pH 3) to 1.8 (at pH 10).<br />
3.2.3. Analytical quality assurance: performance criteria, reference materials, validation and<br />
proficiency testing<br />
Some performance criteria (limits of detection and quantification (LOD/LOQ), method bias and<br />
recovery, measurement uncertainties and analytical quality assurance) for the determination of total<br />
<strong>chromium</strong> and <strong>chromium</strong> species content in <strong>food</strong> are laid down in the EN 13804, 2013. The LOD and<br />
LOQ will vary with the analytical technique, the sample mass, the laboratory and the <strong>food</strong> matrix.<br />
For the determination of <strong>chromium</strong> in <strong>water</strong> intended for human consumption, EU Council Directive<br />
98/83/EC indicates that the performance characteristics for the method of analysis used must, as a<br />
minimum, be capable of measuring concentrations equal to the parametric value with a trueness,<br />
precision and limit of detection that must not exceed 10 % of the parametric value (i.e. 5 μg/L).<br />
To demonstrate the trueness (i.e. systematic error) and precision (i.e. random error) of trace element<br />
data, one of the important criteria is the reporting of correct (and precise) data for the <strong>chromium</strong><br />
content of certified reference materials that closely match the matrix of the samples under<br />
investigation (Jorhem, 2004). Several standard or certified reference materials (SRMs and CRMs) are<br />
available for total <strong>chromium</strong> (Appendix B, Table B1). There is a current need for CRMs certified for<br />
different <strong>chromium</strong> species in <strong>water</strong> and other <strong>food</strong>stuffs.<br />
Two fully validated, European standardised methods are available for the determination of total<br />
<strong>chromium</strong> in <strong>food</strong> by graphite furnace atomic absorption spectrometry (GFAAS) after pressure<br />
digestion wih a LOQ of about 0.04 to 0.16 mg/kg according to the sample weight (EN 14083:2003) or<br />
by atomic absorption spectrometry (FAAS or GFAAS), but GFAAS is recommended) after ash drying<br />
(EN 14082:2003). Four standardised methods are available for the determination of total <strong>chromium</strong> in<br />
<strong>water</strong> by flame or graphite furnace atomic absorption spectrometry (FAAS or GFAAS (EN 1233:1996<br />
or ISO 9174:1998, EN ISO 15586: 2004), by inductively coupled plasma optical emission<br />
spectrometry (ICP-OES) (EN ISO 11885:2009) or mass spectrometry (ICP-MS) (EN ISO 17294-<br />
2:2003). Similar sensitivity can be obtained by GFAAS, ICP-OES and ICP-MS methods (LOD of<br />
0.5 µg/L).<br />
No standardised methods are available for determination of Cr(VI) in <strong>food</strong> while two methods are<br />
suitable for various types of <strong>water</strong> and based on colorimetric reactions with 1,5-diphenylcarbazide.<br />
Namely, the continuous flow analysis (CFA) and spectrometric detection method<br />
(EN ISO 23913:2006) and the photometric method (EN ISO 18412:2006) can be applied for <strong>drinking</strong><br />
<strong>water</strong> in the concentration range of 2 to 20 µg/L and 2 to 50 µg/L, respectively.<br />
A number of proficiency testing schemes (PTS) are regularly organised by several providers for total<br />
<strong>chromium</strong> in <strong>food</strong> and for both total <strong>chromium</strong> and Cr(VI) in <strong>water</strong> to demonstrate and maintain<br />
analytical quality assurance. However, no PTS are available for Cr(VI) in <strong>food</strong>.<br />
Between 2010 and 2012, Food Analysis Performance Assessment Scheme (FAPAS) organized several<br />
proficiency tests on the determination of total <strong>chromium</strong> in <strong>food</strong> e.g. in infant cereal (FAPAS ® reports<br />
07183, 07165), infant formula (FAPAS ® report 07177, 07159), soft drinks (FAPAS ® report 07155)<br />
and milk powder (FAPAS ® report 07138). The results indicate that most of the participating<br />
laboratories, although applying different methods, are capable of reliably analysing total <strong>chromium</strong><br />
(range 67-98 % satisfactory results, 42 to 60 participants) at the level of interest.<br />
Between 2012 and 2013, FAPAS organized several proficiency tests on the determination of total<br />
<strong>chromium</strong> in potable <strong>water</strong> (LEAP ® Scheme reports CHEM107, 109, 111V2 and 112). 88-95 % of<br />
17 to 25 participants obtained satisfactory results at the level of interest (range 9.91-41.4 µg/L).<br />
EFSA Journal 2014;12(3):3595 30