In order to realise EU legislation, the environmental risk of new and exist
ing chemical substances has to be assessed. The methods for risk assessment
are laid down in the Technical Guidance Documents TGD (EC 1996A). Basicall
y, risk assessment consists of a comparison of predicted environmental conc
entrations (exposure assessment) and concentrations which may cause adverse
effects (effect assessment). With the European Union System for the Evalua
tion of Substances EUSES (EC 1996B) a decision support system is available
which integrates the models presented in the TGD into a Windows 95/NT-based
software product. Meanwhile, EUSES has attained a far reaching and extensi
ve use in governments, industry, and research institutes.
For exposure assessment, various exposure models (regression equations, sim
ple generic models, multimedia compartment models) are used. One of the obj
ectives is to investigate the validity of model calculations and evaluate u
ncertainty in models and data arising in model application. Scientific just
ification of underlying equations, limitations, and respective software are
tested and checked for possible errors. The project consists of several wo
rk packages: comprehensive data collection and evaluation, conceptual valid
ation, model simulations, sensitivity and uncertainty analyses, comparison
of model results with measured values (numerical validation), appropriatene
ss of models (operational validation), comparison with alternative models,
and software evaluation. It is determined for which substances and for whic
h environmental segments the models deliver realistic values. Within this p
roject, exposure assessments are carried out for different substances which
represent a wide variety of physical-chemical properties. Substances of in
terest are those which are used in many products or chemical processes and
which are frequently found in the environment. Due to their relatively good
data availability, typical and well-known pollutants such as dioxins and P
CBs are also investigated. For validation studies, in particular to compare
measured concentrations with predicted ones, spatially and temporally cohe
rent data sets must be available. Thus, before starting the project, an env
ironmental segment of regional scale had to be chosen. The German state of
North Rhine-Westphalia (approximately 34 000 km(2)) was selected as an envi
ronmental segment of regional scale.