To assess potential PCB153-associated human health effects and risks, it is necessary to model past exposure. PCB153 blood concentrations, obtained from the AMAP biomonitoring programme, in Inuit women covering the years 1994-2006 at Disko Bay, 1999-2005 at Nuuk, and 1992-2007 at Nunavik were used to extrapolate body burden and exposure to the whole lifespan of the population by the one-compartment toxicokinetic model. By using risk characterisation modelling, calculated Hazard Quotients were higher than 1 between the years 1955 and 1987 for the 90th population percentile and during 1956-1984 for the 50th population percentile. Cancer risk for overall exposure of PCB153 ranged from 4.6×10(-5) to 1.8×10(-6) for the 90th percentile and 3.6×10(-5) to 1.4×10(-10) for the 50th percentile between 1930 and 2049, when central estimates or upper-bound slope factors were applied. Cancer risk was below 1×10(-6) for the same time period when a lower slope factor was applied. Significant future research requirements to improve health risk characterisation include, among others, larger sample sizes, better analytical accuracy, fewer assumptions in exposure assessment, and consequently, a better choice of the toxicity benchmark used to develop the hazard quotient.
Keywords: ADD; ADME; AMAP; AhR; Arctic Monitoring and Assessment Programme; BMDL; BMI; CAR; CR; CSF; Cancer risk; HQ; Hazard quotient; Health outcomes; IRIS; Integrated Risk Information System; LADD; POPs; PXR; RfD; Toxicokinetic modelling; US-EPA; United States Environmental Protection Agency; absorption, distribution, metabolism and excretion; aryl hydrocarbon receptor; average daily dose; benchmark dose level; body mass index; cancer risk; cancer slope factor; constitutive androstane receptor; hazard quotient; lifetime average daily dose; persistent organic pollutants; pregnane X receptor; reference dose.
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