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Cette étude prolonge un travail de recherche sur la signification des noms des parties du corps humain (Npc) (Bertin, 2018). On s'intéresse à la construction illustrée par Colin a le front de venir à cette réunion (NPV). Après un inventaire des Npccompatibles avec NPV, on procède à une analyse sémantique : d'une part, on cerne le sens de NPV (en se focalisant sur la contribution du Npc) et, d'autre part, on tire profit de cette première étape pour l'analyse sémantique des Npceux-mêmes.

A QuEChERS extraction method followed by HPLC-MS/MS analysis was developed to simultaneously analyze chlordecone and its metabolite chlordecol in animal livers. The overall method was validated with accuracy profiles according to the French Standard NF V03-110 and European Union guidelines. The validation was performed on bovine, ovine and porcine liver samples. Linearity, matrix effect, accuracy, within-laboratory repeatability, specificity, LOQ, Q/q relative ion intensities, and uncertainty were reported. Recoveries were between 70% and 120%. LOQs of 1.36 µg chlordecone kg-1 and 2.50 µg chlordecol kg-1 of fresh liver were found. Twelve contaminated livers of bovine, ovine and porcine origin from the French West Indies or samples from in vivo studies were analyzed. In these liver samples from contaminated animals, chlordecone was quantified at concentrations higher than the maximum residue limit and chlordecol in very low amounts in all the samples. In addition, these results confirm that chlordecone can be metabolized in ruminant species.

Chlordecone (CLD) is a Persistent Organic Pollutant used between 1972 until 1993 in the French West Indies (FWI). Due to its persistence and extensive application, a quarter of the total local agricultural acreage is still moderate to heavily polluted. In consequence, livestock may be contaminated at various levels. This is a major public health concern, particularly for local consumers. In order to better understand the fate of CLD in livestock organisms, in vivo studies are required. There is no information available about its metabolism and elimination in ruminants, common livestock in the FWI. To be able to monitor the fate of chlordecone and its metabolites in livestock and to assess if the compounds could be released in the environment, urinary and fecal samples were logically targeted. In order to reach this goal, robust and validated analytical methods are required. For this purpose, Quick, Easy, Cheap, Effective, Rugged, and Safe (QuEChERS) extraction methods were validated to analyze CLD and its metabolites in the urine and feces. The analysis was carried using liquid phase chromatography with tandem mass spectrometry and validated according to French standard NF V03-110 and SANTE guidelines. Matrix effect, Accuracy, within-laboratory repeatability, specificity, Q/q relative ion intensities and uncertainty were reported. Recoveries between 70% and 120% were obtained from urine and feces. The limits of quantification (LOQ) in urine samples were 0.1 μg CLD L−1, 0.1 μg total CLD (CLD and its conjugates)·L−1, 1.3 μg CLDOH L−1 and 2.4 μg total CLD (chlordecol and its conjugates) L−1 of urine. LOQ in fresh feces were 3.2 μg CLD kg−1 and 5.8 μg CLDOH kg−1. Contaminated urinary and fecal samples from ewes were analyzed to confirm the relevance of the methods. In urine, CLD and conjugated CLDOH could be quantified whereas only free CLD and free CLDOH were found in feces. These methods are essential for future toxicokinetic studies and also to estimate the environmental contamination.