New ECETOC expert report: Advancing OECD TG 309 biodegradation testing
390508

New ECETOC expert report: Advancing OECD TG 309 biodegradation testing

A new expert meeting report is now available on the ECETOC website exploring how OECD TG 309 can be made more robust and environmentally relevant for chemical persistence assessment. The report ref...
We’re Hiring: Join the ECETOC Team as a Trainee!
390494

We’re Hiring: Join the ECETOC Team as a Trainee!

Are you passionate about science, regulatory toxicology, and making a real-world impact at the intersection of industry, academia, and policy? ECETOC is excited to announce that we’re looking for a...
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.
TRA Task Force – Worker branch

TRA Task Force – Worker branch

Why? The Worker TRA Task Force has been active since 2019, delivering projects that advance the scientific basis of the Worker Targeted Risk Assessment (TRA) tool. Its overarching objective is to e...
Immunotoxicity assessment: Addressing Challenges and Advancing Methodologies [Workshop → Task Force]​

Immunotoxicity assessment: Addressing Challenges and Advancing Methodologies [Workshop → Task Force]​

Why?Regulatory assessment of immunotoxic properties of chemicals is a complex and challenging task​ Limited regulatory guidance exists​ Lack of industry and regulatory knowledge​...
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....
Technical Report
29.05.1994

TR 059 – Testing for Worker Protection

TR 059 : Testing for Worker Protection | April 1994

A practical approach to risk assessment for occupational exposure standard setting and practical guidance on requirements for animal and human data are given in this report. The various types of OEL, the way in which health may be affected by exposure and the processes used by authorities and company specialists when setting OELs are explained. A step-wise process of data acquisition is described for deciding which substances may require an OEL, for developing OELs and for modifying these in the light of knowledge and experience to produce more definitive limits. In this document OELs initially set are termed 'provisional' while those which have been subject to review are termed 'revised' OELs. Development of OELs is a dynamic process; no OEL can be said to be a final, definitive standard.

While health risks need to be assessed from available animal and human data for each substance and preparation used in the workplace, an OEL will need to be set for a relatively small proportion of these, since many will not become airborne and adequate control of others will be achieved by control of the more major workplace contaminants. Chemical and physical properties are listed which, together with knowledge of the way substances are likely to be handled, stored, transported and disposed of, are of value in deciding if an OEL should be set.

Before studies are planned, any industrial experience with the substance or similar substances should be examined, as should structure-activity relationships for new substances. Information on the acute toxicity, irritancy, sensitising ability, genotoxic activity and short-term, repeated dose toxicity is required before setting a provisional OEL. This information may demonstrate that further toxicological studies are required before a provisional OEL can be set.

Since animal and other experimental studies can never guarantee freedom from adverse effects on health, workplace atmospheric monitoring and health monitoring are recommended when new materials are introduced into the workplace. The design of such studies would need to be determined on a case-by-case basis. Information so gained may confirm the adequacy of the provisional OEL or may indicate the need to set a revised OEL. The need for a revised OEL may also become apparent from data sought by competent EC authorities, from advances in medical knowledge and from workplace experience. Major changes in the use of a substance may also necessitate the setting of a revised OEL. This may necessitate the performance of further studies in animals and man.

The setting of OELs should be carried out on a case-by-case basis by professionally competent groups. Unnecessary standardisation of the process should be resisted. When completed, the data on which an OEL has been based and the considerations which have led to the actual figures should be made freely available.