2025 Annual Report
Annual Report
January 2026 news from the Sec Gen
News

January 2026 news from the Sec Gen

Dear colleagues and friends,As we begin a new year, I would like to thank you for your continued engagement and trust in ECETOC. 2026 promises to be an exciting and dynamic year, and I am pleased...
ECETOC launches Secondee Programme
News

ECETOC launches Secondee Programme

Looking for an extra challenge? A next step to help develop your career? Consider applying for our Secondee Programme!ECETOC is looking for early-career scientists currently working at a member co...
HSSD Tool

HSSD Tool

This software was developed by a consortium of partners to facilitate the uptake of novel approaches to estimate aquatic threshold concentrations (e.g. the concentration at which 5% of the species are exposed above their EC50, HC5).
The Human Exposure Assessment Tools Database (heatDB)

The Human Exposure Assessment Tools Database (heatDB)

heatdb is a public directory of exposure data sources as well as available tools for exposure
NanoApp

NanoApp

ECETOC’s NanoApp is a tool designed to define the boundaries of sets of similar nanoforms and to generate a justification for the REACH registration.
Targeted Risk Assessment (TRA)

Targeted Risk Assessment (TRA)

The Targeted Risk Assessment (TRA) estimates exposures to workers, consumers and the environment that arise during a series of events.
Chronic fish case studies towards an IATA

Chronic fish case studies towards an IATA

Why?Hazard and safety assessments for the pelagic compartment often rely on in vivo studies using a single fish species, raising ethical concerns and uncertainty in terms of extrapolation....
Estimating the environmental release of Synthetic Polymeric Microparticles from Products

Estimating the environmental release of Synthetic Polymeric Microparticles from Products

Why?REACH restriction: SPM use restricted; emissions reporting required by May 2027. Gap: No analytical methods available to measure SPM emissions. Solution: Draft SPERC-based approac...
Case Studies on Reliability and Relevance Considerations during Validation of NAMs

Case Studies on Reliability and Relevance Considerations during Validation of NAMs

Why?Validation of NAMs is often overlooked despite its importance for regulatory use. Traditional validation methods are less suitable for NAMs, which focus on key events rather than apical...
News
01.08.2014

ECETOC publishes report on new information and weight-of-evidence in PBT/vPvB assessment of chemicals

Brussels, 1st August 2014

An ECETOC task force has reviewed the new information and ‘weight-of-evidence’ approach set out in Annex XIII of REACh as amended in 2011, to better assess whether a chemical substance is persistent, bioaccumulative and toxic (PBT), or very persistent /very bioaccumulative (vP/vB). An integrated evaluation strategy is proposed with focus on P and B assessment (on T sufficient guidance exists). In principle, if the available screening information indicates the absence of PBT or vPvB properties, there is no need or obligation for higher-tier assessment and/or further testing. Weight-of-evidence analysis depends on the available information and may include several hypotheses and lines of evidence. Further research is recommended on several topics (endpoints), to fill gaps in knowledge before developing new criteria and specific guidance that allow regulatory conclusions to be drawn, in particular for terrestrial B assessment.

Specifically, it is recommended to confine the PBT assessment primarily to the ‘compartment(s) of concern’ to which most of the substance to be assessed would be initially partitioning. Non-extractable residues (NERs) are strongly bound to sediment or soil and they are not bioavailable, i.e. neither P, B, nor T.

Screening level assessment of the B potential (in the aquatic environment ) is based on the solubility of the substance in water and octanol, its octanol-water and octanol-air partition coefficients, results of in vitro studies and model calculations.

Higher-tier assessment information for B can comprise classical bioconcentration studies in fish, fish dietary biomagnification studies, determination of laboratory and field bioaccumulation factors, field studies on biomagnification and trophic magnification in food chains. The different parameters (‘metrics’) can be normalised based on their fugacity. While the assessment of B in the aquatic environment is usually well defined, terrestrial B assessment is currently compromised by a lack of science-based threshold levels, scarcity of experimental methods and their interpretation.

Organ-specific bioconcentration factors are probably of limited use, depending on the contribution of the respective organ to the total body burden and on the function of the organ. Extrapolation to whole-body may not be possible for certain classes of substances or because of species and organ-specific characteristics.

While human/environmental (bio)monitoring may detect a substance in an organism, the presence per se is no indication of B potential. The latter requires correlating the levels of a substance in an organism with those in the surrounding environment and all potential sources of exposure.

Finally, classical mammalian toxicokinetic studies can inform on the absorption, distribution, metabolism and elimination of a substance, particularly for the assessment of B in terrestrial food chains. Some toxicokinetic models associate the elimination half-life with the B behaviour of a substance.

The document is published as ECETOC Special Report 18: Information to be considered in a weight-of-evidence-based PBT/vPvB assessment of chemicals (Annex XIII of REACH).