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Division 1 Scope and definitionsF1

United Kingdom

Original text. Later amendments are not shown.

The samples intended for the official control of the levels of polychlorinated dibenzo-p-dioxins (PCDDs), polychlorinated dibenzofurans (PCDFs), dioxin-like polychlorinated biphenyls (PCBs)f1 and non dioxin-like PCBs in feed shall be taken in accordance with the provisions of Annex I. The quantitative requirements in relation to the control of substances or products uniformly distributed throughout the feed as provided for in point 5.1. of Annex I shall be applied. Aggregate samples thus obtained shall be considered representative for the lots or sublots from which they are taken. Compliance with maximum levels laid down by F2the CMU Regulations shall be established on the basis of the levels determined in the laboratory samples.

For the purposes of this Part B, the definitions laid down in Annex I to Commission Decision 2002/657/ECf2 shall apply.

In addition to those definitions, the following definitions shall apply for the purpose of this Part B:

  • ‘Screening methods’ means methods used for selection of those samples with levels of PCDD/Fs and dioxin-like PCBs that exceed the maximum levels or the action thresholds. They shall allow a cost-effective high sample-throughput, thus increasing the chance to discover new incidents with high exposure and health risks to consumers. Screening methods shall be based on bioanalytical or GC-MS methods. Results from samples exceeding the cut-off value used to check compliance with the maximum level shall be verified by a full re-analysis from the original sample using a confirmatory method.

  • ‘Confirmatory methods’ means methods that provide full or complementary information enabling the PCDD/Fs and dioxin-like PCBs to be identified and quantified unequivocally at the maximum or in case of need at the action threshold. Such methods utilize gas chromatography/high resolution mass spectrometry (GC-HRMS) or gas chromatography/tandem mass spectrometry (GC-MS/MS).

Annotations

Textual amendments

F1

Substituted by Commission Regulation (EU) 2017/771 of 3 May 2017 amending Regulation (EC) No 152/2009 as regards the methods for the determination of the levels of dioxins and polychlorinated biphenyls (Text with EEA relevance).

F2

Words in Annex 5 Pt. B Ch. 1 point 1 substituted (31.12.2022) by The Food and Feed (Miscellaneous Amendments) Regulations 2022 (S.I. 2022/1351), regs. 1(1), 16(6)(a)(i)

Footnotes

f1

Table of TEF (= toxic equivalency factors) for PCDDs, PCDFs and dioxin-like PCBs: WHO-TEFs for human risk assessment based on the conclusions of the World Health Organization (WHO) — International Programme on Chemical Safety (IPCS) expert meeting which was held in Geneva in June 2005 (Martin van den Berg et al., The 2005 World Health Organization Re-evaluation of Human and Mammalian Toxic Equivalency Factors for Dioxins and Dioxin-like Compounds. Toxicological Sciences 93(2), 223–241 (2006)).

Congener TEF value Congener TEF value
Dibenzo-p-dioxins (‘PCDDs’) and Dibenzo-p-furans '(‘PCDFs’) ‘Dioxin-like’ PCBs Non-ortho PCBs + Mono-ortho PCBs
2,3,7,8-TCDD 1
1,2,3,7,8-PeCDD 1 Non-ortho PCBs
1,2,3,4,7,8-HxCDD 0,1 PCB 77 0,0001
1,2,3,6,7,8-HxCDD 0,1 PCB 81 0,0003
1,2,3,7,8,9-HxCDD 0,1 PCB 126 0,1
1,2,3,4,6,7,8-HpCDD 0,01 PCB 169 0,03
OCDD 0,0003 Mono-ortho PCBs
2,3,7,8-TCDF 0,1 PCB 105 0,00003
1,2,3,7,8-PeCDF 0,03 PCB 114 0,00003
2,3,4,7,8-PeCDF 0,3 PCB 118 0,00003
1,2,3,4,7,8-HxCDF 0,1 PCB 123 0,00003
1,2,3,6,7,8-HxCDF 0,1 PCB 156 0,00003
1,2,3,7,8,9-HxCDF 0,1 PCB 157 0,00003
2,3,4,6,7,8-HxCDF 0,1 PCB 167 0,00003
1,2,3,4,6,7,8-HpCDF 0,01 PCB 189 0,00003
1,2,3,4,7,8,9-HpCDF 0,01
OCDF 0,0003

Abbreviations used: ‘ T ’ = tetra; ‘ Pe ’ = penta; ‘ Hx ’ = hexa; ‘ Hp ’ = hepta; ‘ O ’ = octa; ‘ CDD ’ = chlorodibenzodioxin; ‘ CDF ’ = chlorodibenzofuran; ‘ CB ’ = chlorobiphenyl.

f2

Commission Decision 2002/657/EC of 14 August 2002 implementing Council Directive 96/23/EC concerning the performance of analytical methods and interpretation of results ( OJ L 221, 17.8.2002, p. 8 ).