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In the determination of contaminants (dioxins, polychlorinated biphenyls, polyaromatic hydrocarbons), cell-based assays are useful methods for screening purposes: they are mainly characterized by high sample throughput and lower costs than the Mass Spectrometry (MS)-based methods. Although cell-based assays can be sensitive enough for the determination of dioxins and related substances in agreement with the presently tolerable limits in food and feed (Regulation No. 2375/2001/EC and Directive 2003/57/EC respectively), their lack of specificity make their use rather questionable in control laboratories. In this paper, we present and compare results obtained from the analysis of a limited number of feed samples by both gas chromatography-high resolution mass spectrometry (GC-HRMS) and cell-based assay (DR-CALUX: dioxin responsive-chemically activated luciferase gene expression) methods. The DR-CALUX screening led to less than 10% false non-compliant and no false compliant results. In addition, there is a good correlation between GC-HRMS and DR-CALUX data. However, these preliminary results have to be confirmed on a larger number of samples to demonstrate that total toxic equivalent (TEQ), including dioxins, furans and dioxin-like polychlorobiphenyls (PCBs) can be monitored in feed and food with a cell-based assay. Presented at AOAC Europe/Eurachem Symposium March 2005, Brussels, Belgium  相似文献   
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European legislation laid down maximum tolerable levels of dioxin in feed and food as well as analytical method requirements. In order to face with large monitoring programs, it was foreseen in the EU strategy to integrate screening methods, using either a qualitative (screening) approach, or a quantitative approach. In this study, dioxin results obtained using the Dioxin Responsive Chemical-Activated LUciferase gene eXpression (DR-CALUX®) cell-based assay (quantitative approach), were compared with gas chromatography–high resolution mass spectrometry (GC–HRMS) analyses data. Instead of using World Health Organization–toxic equivalent factor (WHO–TEF), the comparison was based on the assessment of relative effective potencies (REPs) for each congener of the 17 toxic 2,3,7,8-polychlorodibenzo-p-dioxins/furans (PCDD/Fs) and 12 dioxin-like polychlorobiphenyls (DL-PCBs). According to published data, DR-CALUX®-REP evaluated here appear similar to WHO–TEF for PCDD/Fs while lower values were observed for DL-PCBs.

We analyzed two “home made” contaminated fat samples, displaying both the same WHO–toxic equivalent quantities (WHO–TEQ) concentration (12 pg WHO–TEQ g−1). They were spiked with either a low or a high amount of DL-PCBs. In both cases, the DR-CALUX® measured concentration (picogram 2,3,7,8 tetrachlorodibenzo-p-dioxin (TCDD) eq. g−1) corresponded to the PCDD/Fs WHO–TEQ concentration only. A good agreement was nevertheless found between the DR-CALUX® measurements and the recalculated DR-CALUX®-TEQ contents (using DR-CALUX®-REP instead of WHO–TEF), demonstrating that the observed response was due, in both cases, to the addition of the responses of the standards added to the fat. By contrast, in real contaminated samples (feed or cod liver samples), DR-CALUX® measured concentrations were similar to WHO–TEQ GC–HRMS measured concentrations. But, depending on the PCDD/Fs and DL-PCBs congener content, the DR-CALUX® measured concentrations were either lower or higher than calculated DR-CALUX®-TEQ contents, demonstrating that possible co-extracted contaminants contributed to the CALUX response.

Owing to these divergences, the quantitative determination of dioxin-like content in food and feed using CALUX as screening method is questionable, except for samples displaying constant congener patterns, in which cases, correction factors could be applied.  相似文献   

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