Workshop Report 31

SUMMARY

This workshop report summarises a workshop held in Brussels on 26th January 2016 by the ECETOC Human Exposure Data Task Force on the state of the art of consumer exposure assessment science as developed over a period of two years (2013-2015). Over forty exposure experts from industry, academia and regulatory domains came together to: (i) discuss the status of consumer exposure science; (ii) develop consensus on key gaps, and from there, (iii) identify a prioritised research agenda.

Seven presentations provided an overview of (1) The ECETOC Human Exposure Task Force; (2) Robust Exposure Assessment in Refining Risk Assessment; (3) Modelling Total Exposure to Chemicals in Multiple Sources; (4) Presentation of the Task Force’s Landscaping Exercise, summarising available data, sources, models and tools; (5) The case study of phenoxyethanol in household, personal care and cosmetic products; and (6) The case study of solvent use in consumer chemical products. These topics were discussed and debated in detail in two separate discussion sessions. Finally, brainstorm sessions enabled experts to identify consensus on gaps and suggestions on how to move forward.

There was agreement that clear, harmonised guidance on aggregate consumer exposure assessment is required. To this end, delegates from the OECD, JRC, EPA and ECHA offered to discuss future cooperation on this activity within their organisations and to contribute to the Landscaping Document initiated by the ECETOC Task Force. This valuable resource brings together the currently available consumer data, sources, models and tools.

Participants decided that such guidance should include (but not be limited to) the following elements:

  1. Direction on how to determine the most suitable models and data sources for specific aggregate consumer exposure assessments to include decision trees and problem formulation templates. These should have well-stated and validated (as far as is possible) applicability domains with standardised descriptors recognising the unique factors of each model that determines its fitness for purpose. This could include triggering criteria for higher tier aggregate consumer exposure assessment. It was suggested that the OECD provides a platform that could be used to harmonise these data, models, standards and tools across geographies.
  2. Open access and/or commercially available databases on consumer information, including consumer use information and product composition (chemical concentration and presence probability data) across domains.
  3. Direction on how the risk assessor should include a justification narrative (explaining why a particular tool and input data were chosen).
  4. An agreed process to extrapolate the applicability of exposure data in different contexts as a means of ‘gap filling’ in data sparse situations. For example, best practice exists in the occupational setting (Money and Margary, 2002; ECHA, 2012), which could potentially be extended or adapted to consumer settings. Criteria and internationally accepted rating systems would be needed to evaluate the quality of the data and ensure confidence in such approaches.
  5. Assessment of how life cycle perspectives could be applied to help determine the nature of exposures.

Finally, the following three suggestions for future research were developed, and will be discussed during future ECETOC and Cefic LRI management meetings:

  1. Obtaining data on product compositions: this is essential for realistic exposure assessment, particularly when considering aggregate exposure. Without reliable composition data, exposure assessments are based on worst case assumptions giving rise to product restrictions. Questions that need to be answered include: How do we collect, store, share and maintain anonymised product composition data? How do you overcome the barriers to implementing this action across geographies and industry sector groups? Who should lead such an activity?
  2. Developing an agreed process to extrapolate the applicability of exposure data in different contexts. Ideally, exposure assessments are based on actual measurements of population exposures (workers, consumers, the general population), but for many exposure scenarios, data are hard to find. In these cases, exposure must be estimated using models or by reference to data for analogous substances or situations. Currently there is paucity of advice on the circumstances where analogous data might be applied. By contrast, in hazard assessments, processes have been developed to enable data from various sources to be combined. This could be a starting point for a similar approach in exposure assessment.
  3. Developing a framework for exposure assessment of exposure data-poor chemicals that includes quality and weight of evidence assessment. Questions that need answers include: Can the principles that are being developed for quality and weight of evidence of hazard assessment be applied for exposure assessment? How do you overcome the barriers to implementing this action across geographies and industry sector groups? Who should lead such an activity?
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