First assessment of population exposure to perfluorinated compounds in Flanders, Belgium.

With the objective to evaluate exposure of the population in Flanders (Belgium) to perfluorinated compounds (PFCs), we measured perfluorooctane sulfonate (PFOS) and perfluorooctanoic acid (PFOA) in settled dust in homes and offices, in a selection of food items from local origin, in drinking-water and in human serum. We complemented the data with results from a literature survey. Based on this dataset we calculated intake by children and adults from food, drinking-water, settled dust and soil, and air. Dietary exposure dominated overall intake. For adults, average dietary intake equalled 24.2 (P95 40.9) ng PFOS kg(-1) d(-1) and 6.1 (P95 9.6) ng PFOA kg(-1)d(-1), whereas for children the dietary intake was about 3 times higher. Predicted intake is high when compared to assessments in other countries, and to serum levels from Flanders, but comparable to the intakes published by The European Food Safety Authority (EFSA) in 2008. Intake of PFOS and PFOA remained below the Tolerable Daily Intake.

Accelerated long-term forgetting in temporal lobe but not idiopathic generalised epilepsy.

Temporal lobe epilepsy (TLE) has been associated with the phenomenon of accelerated long-term forgetting (ALF), in which memories are retained normally over short delays but are then lost at an accelerated rate over days or weeks. The causes of ALF, and whether it represents a consolidation deficit distinct from the one associated with forgetting over short delays, remain unclear. In addition, methodological issues have made results of some previous studies difficult to interpret. This study used improved methodology to investigate the role of seizure activity in ALF. Forgetting was assessed in participants with TLE (who have involvement of temporal lobe structures) and idiopathic generalised epilepsy (IGE; in which seizures occur in the absence of identified structural pathology in the temporal lobes). Learning of novel stimuli was matched between patients with TLE, patients with IGE and healthy controls matched for age and IQ. Results indicated that the TLE group showed accelerated forgetting between 30-min and three-weeks, but not between 40-s and 30-min. In contrast, rates of forgetting did not differ between patients with IGE and controls. We conclude that (1) ALF can be demonstrated in TLE in the absence of methodological confounds; (2) ALF is unlikely to be related to the experience of epilepsy that does not involve the temporal lobes; (3) neither seizures during the three-week delay nor polytherapy was associated with ALF.

Accumulation and effects of metals in caged carp and resident roach along a metal pollution gradient.

Metal accumulation and effects on plasma Ca(2+), alanine transaminase (ALT) and fish condition factor were examined in caged carp (Cyprinus carpio) and resident roach (Rutilus rutilus) at four locations along the Grote Nete River system (Belgium). Cadmium and zinc accumulation were found in carp and roach, with highest concentrations at the most contaminated site (dissolved Cd: 1.82 microg/l, Zn: 967 microg/l). On the tissue level, highest cadmium concentrations were measured in kidneys of carp and roach, followed by gills, intestine and liver, while low concentrations were observed in carcass and muscle. For zinc, a similar pattern was observed (intestine>kidney>gills>liver>carcass>muscle). Comparison between species showed higher cadmium concentrations in feral roach, while zinc levels were lower, owing to the high zinc concentrations in control carp. Furthermore, comparison of metal concentrations between two sampling periods (2005 and 2000-2001) revealed a drastic decrease in cadmium concentration in gills, liver and muscle of roach, similar to the reduction in waterborne cadmium concentrations, while differences for zinc were much less pronounced. In addition to metal accumulation, increased metallothionein concentrations (approximately 2x) were found in carp and roach, while no metal-related effects were found on ALT, Ca(2+)or condition factor. However, negative effects on fish community structure, as assessed by the index of biotic integrity (IBI), were found along the pollution gradient and indicated long-term adverse effects of metal pollution.