Time trend of exposure to dechloranes: Plasma samples of German young adults from the environmental specimen bank collected from 1995 to 2017.

Dechloranes, like Dechlorane Plus® are commonly used flame retardants identified by the EU as substances of very high concern (SVHC) because of their persistence and bioaccumulation potential. To characterize the dechlorane exposure of Germans in the last two decades, 180 archived blood plasma samples of the German Environmental Specimen Bank (students aged 20-29 years) collected at six time points between 1995 and 2017 were analyzed for four dechloranes; namely Dechlorane Plus® (syn- and anti-DDC-CO), dechlorane 602 (DDC-DBF), and dechlorane 603 (DDC-Ant). These were quantified using a GC-MS/MS method. Overall, anti- and syn-DDC-CO were detected in 88% and 98% of the samples, whereas DDC-DBF and DDC-Ant were found in 40% and 37% of the samples, respectively. The median (95th percentile) values were 1.0 ng/g lipid weight (l.w.) (3.0 ng/g l.w.). for anti-DDC-CO, 0.6 ng/g l.w (1.9 ng/g l.w.). for syn-DDC-CO, 0.1 ng/g l.w (0.6 ng/g l.w.). for DDC-DBF, and 0.1 ng/g l.w (0.2 ng/g l.w.). for DDC-Ant. The 95th percentile concentrations of the sum of syn- and anti-DDC-CO decreased from 4.2 ng/g l.w. in 1995, to 2.9 ng/g l.w. in 1999, and subsequently increased to 3.7 ng/g l.w. in 2008, and up to 5.9 ng/g l.w. in 2017. A statistically significant decrease with time was observed for DDC-DBF and DDC-Ant, but not for DDC-CO. Our medians found in blood samples in 2017 are similar to those observed in Germany in 2013/14, but higher compared to values reported in other European countries. Overall, more toxicological and monitoring data is needed to better characterize the potential impact on health.

Asbestos between science and myth. A 6,000-year story.

Asbestos was used in making pottery in Eastern Finland from around 4000 B.C. In the ancient era and in the Middle Ages, magic properties were frequently attributed to this mineral. In the first century A.D., the Latin encyclopaedist Pliny the Elder reported in his Historia Naturalis that asbestos protects against all poisonings, particularly that of magicians. Moreover, asbestos was often found in places of worship, in Rome as well as in Athens and in Jerusalem. In the Middle Ages asbestos was identified with some animals, such as the salamander and certain white rodents. With such appearance, the mineral  had a huge success in Western as well as in Eastern literature and the fine arts. Marco Polo (1254-1324) in the Milione tried to deny that asbestos was a salamander. Despite its noxious effects, asbestos continues to be used in much of the world. In the 21st century it seems to be maintaining its quality as a magic stone.

A first European scale multimedia fate modelling of BDE-209 from 1970 to 2020.

The European Variant Berkeley Trent (EVn-BETR) multimedia fugacity model is used to test the validity of previously derived emission estimates and predict environmental concentrations of the main decabromodiphenyl ether congener, BDE-209. The results are presented here and compared with measured environmental data from the literature. Future multimedia concentration trends are predicted using three emission scenarios (Low, Realistic and High) in the dynamic unsteady state mode covering the period 1970-2020. The spatial and temporal distributions of emissions are evaluated. It is predicted that BDE-209 atmospheric concentrations peaked in 2004 and will decline to negligible levels by 2025. Freshwater concentrations should have peaked in 2011, one year after the emissions peak with sediment concentrations peaking in 2013. Predicted atmospheric concentrations are in good agreement with measured data for the Realistic (best estimate of emissions) and High (worst case scenario) emission scenarios. The Low emission scenario consistently underestimates measured data. The German unilateral ban on the use of DecaBDE in the textile industry is simulated in an additional scenario, the effects of which are mainly observed within Germany with only a small effect on the surrounding areas. Overall, the EVn-BTER model predicts atmospheric concentrations reasonably well, within a factor of 5 and 1.2 for the Realistic and High emission scenarios respectively, providing partial validation for the original emission estimate. Total mean MEC:PEC shows the High emission scenario predicts the best fit between air, freshwater and sediment data. An alternative spatial distribution of emissions is tested, based on higher consumption in EBFRIP member states, resulting in improved agreement between MECs and PECs in comparison with the Uniform spatial distribution based on population density. Despite good agreement between modelled and measured point data, more long-term monitoring datasets are needed to compare predicted trends in concentration to determine the rate of change of POPs within the environment.

Stocks and flows of PBDEs in products from use to waste in the U.S. and Canada from 1970 to 2020.

The time-dependent stock of PBDEs contained in in-use products (excluding building materials and large vehicles) was estimated for the U.S. and Canada from 1970 to 2020 based on product consumption patterns, PBDE contents, and product lifespan. The stocks of penta- and octaBDE peaked in in-use products at 17,000 (95% confidence interval: 6000-70,000) and 4,000 (1,000-50,000) tonnes in 2004, respectively, and for decaBDE at 140,000 (40,000-300,000) tonnes in 2008. Products dominating PBDE usage were polyurethane foam used in furniture (65% of pentaBDE), casings of electrical and electronic equipment or EEE (80% of octaBDE), and EEE and automotive seating (35% of decaBDE for each category). The largest flow of PBDEs in products, excluding automotive sector, to the waste phase occurred between 2005 and 2008 at ∼10,000 tonnes per year. Total consumption of penta-, octa-, and decaBDE from 1970 to 2020 in products considered was estimated at ∼46,000, ∼25,000, and ∼380,000 tonnes, respectively. Per capita usage was estimated at 10-250, 10-150, and 200-2000 g·capita(-1)·y(-1) for penta-, octa-, and decaBDE, respectively, over the time span. Considering only the first use (no reuse and/or storage) of PBDE-containing products, approximately 60% of the stock of PBDEs in 2014 or ∼70,000 tonnes, of which 95% is decaBDE, will remain in the use phase in 2020. Total emissions to air of all PBDEs from the in-use product stock was estimated at 70-700 tonnes between 1970 and 2020, with annual emissions of 0.4-4 tonnes·y(-1) for each of penta- and octaBDE and 0.35-3.5 tonnes·y(-1) for decaBDE in 2014.