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Viviamo ormai in un mondo di plastica; moltissimi oggetti che usiamo tutti i giorni sono fatti di plastica. Il problema è che la plastica si degrada con molta difficoltà e, invece di essere correttamente riciclata e riutilizzata, viene spesso abbandonata nell’ambiente e finisce in mare. Le microplastiche, piccoli frammenti di plastica, possono essere ingerite dagli organismi acquatici e, attraverso la catena alimentare, possono arrivare direttamente nel nostro piatto. Spesso questi frammenti plastici accumulano e veicolano contaminanti chimici, tra cui gli interferenti endocrini, che possono alterare il sistema ormonale e avere effetti sulla salute degli animali, uomo incluso. Gli studi dei ricercatori si stanno focalizzando proprio per cercare di capire l’impatto delle microplastiche sulle singole cellule e sugli organismi interi.

The 3T3-L1 murine pre-adipocyte line is an established cell culture model for screening Metabolism Disrupting Chemicals (MDCs). Despite a need to accurately identify MDCs for further evaluation, relatively little research has been performed to comprehensively evaluate reproducibility across laboratories, assess factors that might contribute to varying degrees of differentiation between laboratories (media additives, plastics, cell source, etc.), or to standardize protocols. As such, the goals of this study were to assess interlaboratory variability of efficacy and potency outcomes for triglyceride accumulation and pre-adipocyte proliferation using the mouse 3T3-L1 pre-adipocyte cell assay to test chemicals. Ten laboratories from five different countries participated. Each laboratory evaluated one reference chemical (rosiglitazone) and three blinded test chemicals (tributyltin chloride, pyraclostrobin, and bisphenol A) using: 1) their Laboratory-specific 3T3-L1 Cells (LC) and their Laboratory-specific differentiation Protocol (LP), 2) Shared 3T3-L1 Cells (SC) with LP, 3) LC with a Shared differentiation Protocol (SP), and 4) SC with SP. Blinded test chemical responses were analyzed by the coordinating laboratory. The magnitude and range of bioactivities reported varied considerably across laboratories and test conditions, though the presence or absence of activity for each tested chemical was more consistent. Triglyceride accumulation activity determinations for rosiglitazone ranged from 90 to 100% across test conditions, but 30–70 % for pre-adipocyte proliferation; this was 40–80 % for triglyceride accumulation induced by pyraclostrobin, 80–100 % for tributyltin, and 80–100 % for bisphenol A. Consistency was much lower for pre-adipocyte proliferation, with 30–70 % active determinations for pyraclostrobin, 30–50 % for tributyltin, and 20–40 % for bisphenol A. Greater consistency was observed for the SC/SP assessment. As such, working to develop a standardized adipogenic differentiation protocol represents the best strategy for improving consistency of adipogenic responses using the 3T3-L1 model to reproducibly identify MDCs and increase confidence in reported outcomes. Over-arching project supported by grants [R01 ES016099 to HMS; R00 ES030405 to CDK] from the National Institute of Environmental Health Sciences (NIEHS); University of Turin; European Union's Horizon 2020 research and innovation program under grant agreement GOLIATH No. 825489; Brunel University London; NIEHS (1K22ES026208 and R01ES027863); NIEHS (Z0ES102785); Spanish Institute of Health Carlos III (grant FIS-PI16/01812).