POPs
Transcription
POPs
Welcome from the RECETOX Centre Scientific challenges connected with the Stockholm Convention Ivan Holoubek RECETOX, Masaryk University, Brno, CR holoubek@recetox.muni.cz; http://recetox.muni.cz RECETOX WORKSHOP Identifying the research needs in the global assessment of toxic compounds ten years after the signature of the Stockholm Convention. Brno, Czech Republic, 22-24/05/2011 1 2 3 4 5 6 RECETOX research team 15 teachers and professors 20 Ph.D. researchers 50 Ph.D. students 10 senior researchers and postdocs 6 technical and administrative http://recetox.muni.cz stuff 7 RECETOX POPs Research topics and areas of experties Fundamental research in the field of POPs Global, regional trends – distribution, monitoring New types of pollutants – anthropogenic, natural Development of sampling and analytical methods Measurements/monitoring vs. modelling Environmental transformations Mechanisms of harmful effects 8 Persistent Organic Pollutants (POPs) POPs: ☺ The group of most fascinating (Prof. K. C. Jones - scientific approach) pollutants Ghost of the past, devilish rest of human activities (Terry Bidlemann - public feelling) God creates 90 elements, man round 17, but Devil only one – chlorine – Otto Hutzinger 9 Persistent organic pollutants Persistent H Cl C Cl CCl3 Bioaccumulation Toxicity Long-range transport 10 Scientific challenges Results of the SETAC Workshop on Science-based guidance for the Evaluation and identification of PBTs and POPs SETAC Pellston Workshop “Science-Based Guidance and Framework for the Evaluation and Identification of PBTs and POPs”, Jan 27-Feb 1, 2008, Pensacola FL 11 Conclusions and recommendations • While the existing frameworks for evaluation of POPs/PBTs provide adequate flexibility to introduce additional, new and emerging scientific evidence into the processes the science has advanced significantly • Specific guidance is in need of updating and clarification: • Assessment of persistence with respect to overall Pov • identification and assessment of degradation products and bound residues • Use of trophic magnification factors and/or BMFs in both air and water breathing organisms • Greater use of in vitro test information and bioaccumulation models • tiered approach is recommended for ecotoxicity to ensure that all of the same endpoints are considered in each assessment, • use of tissue body residues rather than media concentrations • on the most appropriate environmental measurement approaches for new candidate POPs, and on how to create a weight of evidence based on such data • There is also a need to: • Develop coupled models describing environmental fate, bioaccumulation and LRT potential • Consider of new partitioning mechanisms such as those observed for ionizable chemicals • recognize and communicate uncertainties associated with both quantitative and qualitative elements of risk profiles for candidate POPs 12 Tools of the SC New chemicals evalution procedure – POPRC Effectiveness evaluation – monitoring as a one from tools Prevention of releases Disposal and remediation Other 13 Properties of persistent organic pollutants (POPs) Persistency: Half time in water > 2 months Half time in soil > 6 months Half time in sediments > 6 months Air - half time > 2 days Bioacumulation: Biological concentration factor for water biotop > 5000 Log Kow >5 14 Key POPs words 15 What we have ?? SC legal tool Old POPs New POPs Potential POPs Procedure for assessment (POPRC) – tool for new POPs evaluation Efectiveness evaluation and monitoring as one of the tools BAT/BEP Other Guidances – Dioxin Toolkit Global networks, alliances… 16 New POPs evaluation Physical-chemical properties Environmental-chemical properties Fate - How well do we understand the fate of POPs ? Transport, exchange processes, equilibria Environmental distribution Study of environmental processes - Laboratory experiments - Field experiments – Monitoring - Modelling Transformations, properties of degradation products Exposure, accumulation Effects Risks ? 17 Long-range transport elucidation Evaluation tools Estimation of meteorological, hydrological, oceanographic conditions during the transport event (e.g, air mass back trajectories) Physico-chemical properties and characterisation Compound pattern elucidation Assessment of concentration levels including ratio evaluation between different contaminant types Transport and fate modeling 18 Scientific topics Source of POPs – emissions, real occurrence Environmental fate Physical-chemical properties – for models Environmental-chemical properties Transport Exchanges, equilibria Transformation Degradation products and their properties Accumulation, bioaccumulation, bioavailability Toxicity of POPS and degradation products Toxic interactions 19 POPs in the environment – old, new, potential What happens after ??? Effectiveness evaluation – monitoring in selected compartments Matrices, sampling tools, analysis, evaluation, visualisation, interpretation POPs, waste, contaminated sites Fate and effects Exposure Toxic interactions Effects of real mixtures 20 Toxicity of degradation products 21 Toxic interactions Risk assessment of combined exposure to multiple chemicals: A WHO/IPCS framework. M.E. (Bette) Meek, Alan R. Boobis, Kevin M. Crofton, Gerhard Heinemeyer, Marcel Van Raaij, Carolyn Vickers Regulatory Toxicology and Pharmacology xxx (2011) xxx–xxx Prospective and Retrospective Environmental Risk Assessment of Mixtures Moving from Research to Regulation 3rd SETAC Europe, Special Science Symposium, 2-3 February 2011, Hotel Marivaux, Brussels, UNEP/POPS/POPRC.6/5 Persistent Organic Pollutants Review Committee Sixth meeting, Geneva, 11–15 October 2010 Technical work: intersessional work on toxic interactions Summary of intersessional work on toxic interactions Case-study 2 - High volume POPs in environmental matrices on a long range scale Ecotoxicological issues Marco Vighi and Sara Villa 22 Toxicity of environmental mixtures Questions identified during past meetings What additional information is needed to assist the Committee with the issue of toxic interactions in its deliberations? • • • • • What specific information on persistent organic pollutant interactions should be included in a risk profile? • • • What would be the possible implications of interactive effects of persistent organic pollutants for the application of the precautionary approach described in Annex E? What guidance on the preparation of a risk profile should the Committee provide regarding consideration of interactive effects? • • Answers suggested by the co-chairs Understanding of toxicological and ecotoxicological effects of less-explored new compounds such as brominated flame retardants or perfluorinated compounds; Understanding of effects of complex chemical mixtures; Studies of vulnerable and keystone species such as arctic gulls, polar bears or ringed seals; Characterization of links between exposures and/or biomarkers (e.g., immune parameters, hormone levels) with the effects in populations; Understanding of persistent organic pollutant effects in the context of additional stressors and parameters (other anthropogenic activities, parasite and micropathogen infections, food scarcity, sensitive developmental stages, climate change, etc.). Information concerning additive or antagonistic and synergistic effects; Toxicological effects of environmental mixtures connected with actual environmental levels; Ecotoxicological effects of environmental mixtures of chemicals; If no or only limited information is available from field or laboratory studies, potential additive or synergic effects could be considered as interactive effects. Risk assessment guidance on combined exposure to multiple chemicals with the definition of relevant endpoints of 23 multiple effects.