Abstract

The potential risk that two closely related insecticides, spinetoram and spinosad, posed to three Cladoceran species, Ceriodaphnia dubia, Daphnia pulex, and D. magna was determined using two approaches, the USEPA Risk Quotient method and the Delay in Population Growth Index (DPGI). Results of the RQ method showed that spinetoram posed a risk to all three species, but spinosad posed a risk only to C. dubia. The DPGI analysis showed that exposure to spinetoram resulted in populations of all three species being delayed ≥ 3 generation times. Exposure to the LC50 and the lower 95% CL resulted in delayed populations while exposure to the upper 95% CL concentration of spinetoram resulted in no recovery of any of the three species over the course of the modeling exercise (88 d). Exposure to the lower and upper 95% Cl and the LC50 of spinosad resulted in C. dubia populations being delayed ≥ 3 generations. D. pulex populations were not negatively affected after exposure to spinosad. D. magna populations were delayed ≥ 3 generations, but only after exposure to the upper 95% Cl of spinosad. These results illustrate that although the EPA risk quotient method indicated that spinetoram posed a risk to all three species and that spinosad only posed a risk to C. dubia, the DPGI showed that D. magna would be negatively affected by spinosad and none of the three species would reach a predetermined number of individuals after exposure to the upper 95% CL of spinetoram. Because the DPGI uses the 95% Cl as well as the LC50 in its calculation and produces a measure of population growth it provides more detailed information in terms of the potential risk of pesticides to populations than the RQ method.

Highlights

  • A central concern in risk assessment is accurately characterizing the effects of toxicants on different organisms – and using this characterization to effectively and accurately predict how different species will react to different toxicants

  • Results of the risk quotient (RQ) method showed that spinetoram posed a risk to all three species, but spinosad posed a risk only to C. dubia

  • D. magna populations were delayed > 3 generations, but only after exposure to the upper 95% Cl of spinosad. These results illustrate that the EPA risk quotient method indicated that spinetoram posed a risk to all three species and that spinosad only posed a risk to C. dubia, the Delay in Population Growth Index (DPGI) showed that D. magna would be negatively affected by spinosad and none of the three species would recover after exposure to the upper 95% CL of spinetoram

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Summary

Introduction

A central concern in risk assessment is accurately characterizing the effects of toxicants on different organisms – and using this characterization to effectively and accurately predict how different species will react to different toxicants. Differences exist among species in various demographic vital rates such that some species reach sexual maturity quickly, have many broods and offspring, and have a short life span (e.g. rats) and other species take a long time to reach sexual maturity, have long life spans, and few offspring (e.g. elephants). These differences in vital rates make some species less susceptible to stress than others (Stark et al 2004). Several studies have shown that differences in vital rates among even closely related species can result in different population outcomes after exposure to toxicants (Stark et al 2004; Banks et al 2010, 2011, 2014, 2017)

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