Gl. Reeves, An experimental design for outdoor water/sediment studies using C-14-labelled pesticides, HUMAN AND ENVIRONMENTAL EXPOSURE TO XENOBIOTICS, 1999, pp. 181-187
Annex VI to Directive 91/414/EEC requires evaluation of the possibility of
a plant protection product reaching non-target areas under proposed use con
ditions, where it must be shown that the environment is adequately protecte
d prior to authorisation. This process uses fate and behaviour information
on the active substance from Annex II. Subsequently a risk assessment is ma
de in Annex III by comparing environmental concentrations with ecotoxicolog
ical end-points for non-target organisms, and demonstrating acceptable safe
ty margins.
Surface water must be considered where exposure may occur via spray-drift d
uring application or from soil run-off. The laboratory studies (with C-14-p
esticide) used in the assessment are hydrolysis, aqueous photolysis and wat
er/sediment, which investigate the route and rate of degradation of the act
ive substance under controlled conditions, and identify major degradates fr
om chemical or biological routes. However, laboratory degradates may not al
ways be relevant under field conditions, e.g. photolysis in surface water m
ay be reduced by turbidity or enhanced by indirect photolysis, or sediment
sorption may reduce the availability of residues. Presently, no semi-field
approach exists for carrying out a higher tier test. This paper describes m
ethodology for an outdoor water/sediment study using C-14-pesticide and pre
sents data for an experimental fungicide, designated Compound X.