Suchergebnisse

Human biomonitoring (HBM) monitors levels of environmental pollutants in human samples, which often is a topic of concern for residents near industrially contaminated sites (ICSs). Around an ICS area in Menen (Belgium), including a (former) municipal waste incinerator and a metal recovery plant, increasing environmental concentrations of dioxins and polychlorinated biphenyls (PCBs) were observed, causing growing concern among residents and authorities. The local community succeeded in convincing the responsible authorities to investigate the problem and offer research funding. Persistent organic pollutants (POPs) were measured in two consecutive HBM studies (2002-2006 and 2010-2011), in the context of the Flemish Environment and Health Study (FLEHS), as well as in soil and locally produced food. Meanwhile, local authorities discouraged consumption of locally produced food in a delineated area of higher exposure risk. Ultimately, HBM and environmental data enabled tailored dietary recommendations. This article demonstrates the usefulness of HBM in documenting the body burdens of residents near the ICS, identifying exposure routes, evaluating remediating actions and providing information for tailored policy strategies aiding to further exposure reduction. It also highlights the role of the local stakeholders as an example of community-based participatory research and how such an approach can create societal support for research and policy. ; Funding: The HBM studies were conducted within the framework of the Flemish Center of Expertise on Environment and Health (FLEHS 2002–2006 and 2007–2011), funded by the Flemish Government, Department of Environment & Spatial Development, Flemish Planning Bureau for the Environment and Spatial Development (formally: Department of Environment, Nature & Energy); Department of Economics, Science and Innovation and the Flemish Agency for Care and Health. The scienceto-policy process of the HBM results was funded by the Department of Environment & Spatial Development, Flemish Planning Bureau for the Environment and Spatial Development (formally: Department of Environment, Nature & Energy) and the Flemish Agency for Care and Health. The egg study was funded by the Government of Flanders, Department of Environment & Spatial Development, Flemish Planning Bureau for the Environment and Spatial Development (formally: Department of Environment, Nature & Energy); the Flemish Agency for Care and Health and the Flanders Environment Agency. The views expressed herein are those of the author(s) and are not necessarily endorsed by the Flemish Government. Acknowledgments: The authors wish to express their gratitude to the participants of the studies for their cooperation and to the study nurses and study fieldworkers for their contribution to the study. We also thank the SGS laboratory for collection and analysis of the egg samples and Josworld for designing the leaflet on dietary recommendations for consumption of home-produced eggs.

Chronic biological stress may adversely affect adolescents' physical and mental health, but insight in the personal and environmental factors that determine chronic stress is limited. We measured 3-month cumulative hair cortisol concentration (HCC) in 419 adolescents, participating in the Flemish Environment and Health Study. Adolescents' health and lifestyle characteristics, household and neighborhood socio-economic status as well as neighborhood urbanicity were assessed as potential determinants of HCC, using multiple linear regression models. We additionally explored heterogeneity of our results by sex. HCC were significantly higher in boys from densely populated neighborhoods, the association was not significant in girls. Accordingly, boys living outside cities had significantly lower HCC than boys, living in cities. HCC was significantly lower in adolescents with an optimal vitality, a measure of a positive mental health status. In adolescent girls, menarcheal status (pre-/postmenarche) was a significant determinant of HCC. Our findings are the first to suggest that residential urbanicity may have an impact on chronic biological stress in a general population of adolescent boys. ; This paper is based on research conducted within the framework of the Flemish Center of Expertise on Environment and Health (FLEHS 2016-2020), funded by the Government of Flanders, Department of Environment & Spatial Development. VV was supported by a PhD fellowship at the University of Antwerp and VITO, funded by the Flemish Center of Expertise on Environment and Health. We thank the adolescents and their families who participated in FLEHS IV. Without their effort, this study would not have been possible. We thank the field workers from the Provincial Institute of Hygiene and VITO for the sample and data collection.

The 7th amendment to the EU Cosmetics Directive prohibits to put animal-tested cosmetics on the market in Europe after 2013. In that context, the European Commission invited stakeholder bodies (industry, non-governmental organisations, EU Member States, and the Commission's Scientific Committee on Consumer Safety) to identify scientific experts in five toxicological areas, i.e. toxicokinetics, repeated dose toxicity, carcinogenicity, skin sensitisation, and reproductive toxicity for which the Directive foresees that the 2013 deadline could be further extended in case alternative and validated methods would not be available in time. The selected experts were asked to analyse the status and prospects of alternative methods and to provide a scientifically sound estimate of the time necessary to achieve full replacement of animal testing. In summary, the experts confirmed that it will take at least another 7-9 years for the replacement of the current in vivo animal tests used for the safety assessment of cosmetic ingredients for skin sensitisation. However, the experts were also of the opinion that alternative methods may be able to give hazard information, i.e. to differentiate between sensitisers and non-sensitisers, ahead of 2017. This would, however, not provide the complete picture of what is a safe exposure because the relative potency of a sensitiser would not be known. For toxicokinetics, the timeframe was 5-7 years to develop the models still lacking to predict lung absorption and renal/biliary excretion, and even longer to integrate the methods to fully replace the animal toxicokinetic models. For the systemic toxicological endpoints of repeated dose toxicity, carcinogenicity and reproductive toxicity, the time horizon for full replacement could not be estimated.