Pharmacokinetic model of dioxin and furan levels in adipose tissue from sawmill work involving chlorophenate fungicides

Concentrations of PCDD/PCDFs in plasma of subjects living in the vicinity of a hazardous waste incinerator: follow-up and modeling validation

In 2007, the concentrations of polychlorinated dibenzo-p-dioxins and dibenzofurans (PCDD/PCDFs) were determined in plasma of non-occupationally exposed subjects living near the only hazardous waste incinerator (HWI) in Spain (Constantí, Tarragona County, Catalonia). These data were compared with the levels found in two previous surveys performed in 1998 (baseline) and 2002. The current mean PCDD/PCDF concentration in plasma was 9.36pg I-TEQg(-1) of lipid (range: 1.76-23.44pg I-TEQg(-1) of lipid). It means a significant reduction of the mean PCDD/PCDFs levels in plasma in comparison to the concentrations found in 1998 and 2002 (27.01 and 15.70pg I-TEQg(-1) of lipid, respectively). This important decrease agrees well with the notable reduction in the dietary intake of PCDD/PCDFs recently noted for the population of the same area (210.1pg I-TEQd(-1), 63.8pgWHO-TEQd(-1), and 27.8pgWHO-TEQd(-1), in 1998, 2002 and 2007, respectively). The current data were also used to predict theoretical PCDD/PCDF concentrations in plasma by executing a single-compartment empirically-based pharmacokinetic model on the basis of the daily intake of these pollutants by the local population.

Secondary exposure to dioxins through exposure to PCP and its derivatives

This study discusses the potential exposure of occupational workers and general consumers in the European Union (EU) to polychlorinated dibenzo-p-dioxins (PCDDs) and polychlorinated dibenzofurans (PCDFs) caused by exposure to pentachlorophenol (PCP) and its derivatives. A synthesis of reported exposure data relating exposure to PCP and its derivatives in an occupational setting has indicated that the PCDD/F intake for exposure in the 1990s averaged over a lifetime is likely to be in the order of 0.02-1 pg I-TEQ kg-1 bw day-1 with actual exposures more likely to occur at the lower end of the range, around the median of 0.16 pg I-TEQ kg-1 bw day-1. Workers who have experienced past exposure to PCP and its derivatives especially in the early to mid 1980s, will have been subjected to higher exposures to PCDD/Fs due to the generally higher concentrations of PCDD/Fs in PCP products at that time. Exposure to PCP and its derivatives via the food chain is judged to be the most significant intake route of PCDD/Fs into consumers. The ingestion of milk and dairy products obtained from cows grazed on pasture dressed with sewage sludge has the potential to raise the average daily intake of PCDD/Fs via the diet by about 40% if all foods consumed derived from sludge amended soil. To the extent quantifiable, exposure to PCP in an occupational setting contributed approximately 16% as a median to the overall background exposure to PCDD/Fs, while for consumers this contribution ranged from 2 to 60% depending on the exposure to sludge amended foods.