title: Variation in the level of protection afforded to birds and crustaceans exposed to different pesticides under standard risk assessment procedures.
abstract: First-tier risk assessment for pesticides is often based on the quotient of the toxicity divided by the predicted environmental concentration or dose. This ratio is compared to a fixed assessment factor (AF) to decide whether the pesticide is to be allowed on the market or whether further research is needed. Often, a high value (e.g., the 90th percentile) is assumed for the predicted environmental concentration, and the lowest available value is chosen to represent toxicity; yet, the real level of protection is not known. Therefore, it is also not known whether the first tier is conservative enough or too conservative. By using 2 large toxicity databases and assuming a log-logistic species sensitivity distribution for each pesticide, the percent of species not covered by the AF is estimated in the scenario, where exposure is at the maximum level allowable in the first tier. In the case of crustaceans, the median estimate of the fraction of species not covered by the AF of 100 in the first-tier scenario is 3.4%, on average, for 72 pesticides. In other words, on average, 3.4% of the crustacean species will be exposed above their median lethal concentration (LC50) and median lethal dose (LD50) value in 10% of receiving surface waters that receive the maximum allowable exposure to an individual pesticide. The estimated level of protection varies widely between pesticides. For 10% of the pesticides, the estimated fraction of species not covered is ≥10% (maximum=41.4%). For 28% of the pesticides, 99.9% of the species will have the assumed level of protection. For birds, the median estimate of the fraction of species exposed above their median lethal dose for the first-tier scenario (AF=10) is 3.0% on average, when the AF is applied to the lower of the toxicity values for the 2 standard test species. For 11% of the pesticides, the median estimate is ≥10% (maximum=15.7%). When the AF is applied instead to the geometric mean of the toxicity values for the 2 standard species, the median estimate of the fraction of species not covered by the AF is increased to 7.4% on average; for 31% of the pesticides, this fraction is ≥10% (maximum=33.4%). This variation in the level of protection should be considered when defining the assumptions, assessment factors, and decision criteria in regulatory risk assessment.
authors.affiliation: National Institute of Public Health and the Environment (RIVM), PO Box 1, 3720 BA Bilthoven, The Netherlands. robert.luttik@rivm.nl
authors.forename: Robert
authors.initials: R
authors.lastname: Luttik
authors.forename: Andy
authors.initials: A
authors.lastname: Hart
authors.forename: Willem
authors.initials: W
authors.lastname: Roelofs
authors.forename: Peter
authors.initials: P
authors.lastname: Craig
authors.forename: Pierre
authors.initials: P
authors.lastname: Mineau
mesh_terms: D000818:Animals; D001717:Birds; D003247:Conservation of Natural Resources / Q000379:methods*; D003445:Crustacea / Q000187:drug effects*; D004781:Environmental Exposure / Q000009:adverse effects*; D004784:Environmental Monitoring / Q000592:standards*; D010573:Pesticide Residues / Q000633:toxicity*; D018570:Risk Assessment / Q000592:standards
chemical_list: D010573:Pesticide Residues