Agricultural adjuvants: Acute mortality and effects on population growth rate of Daphnia pulex after chronic exposure

Acute and chronic toxicity of eight agricultural adjuvants (Bond(R), Kinetic((R)), Plyac(R), R-11(R), Silwet L-77(R), Sylgard 309(R), X-77(R), and WaterMaxx(R)) to Daplinia pulex were evaluated with 48-h acute lethal concentration estimates (LC50) and a 10-d population growth-rate measurement, the instantaneous rate of increase (r(i)). Based on LC50, the order of toxicity was R-11 > X-77 = Sylgard 309 - Silwet L-77 > Kinetic > Bond > Plyac > WaterMaxx; all LC50 estimates were higher than the expected environmental concentration (EEC) of 0.79 mg/L, indicating that none of these adjuvants should cause high levels of mortality in wild D. D. pulex populations. Extinction. defined as negative population growth rate, occurred after exposure to 0.9 mg/L R-11, 13 mg/L X-77. 25 mg/L Kinetic, 28 mg/L Silwet. IS mg/L Sylgard, 450 mg/L Bond. 610 mg/L Plyac, and 1,600 mg/L WaterMaxx. Concentrations that caused extinction were substantially below the acute LC50 for R-11, Kinetic, Plyac, X-77, and Bond. The noobservable-effects concentration (NOEC) and lowest-observable-effects concentration (LOEC) for the number of offspring per surviving female after exposure to R-11 were 0.5 and 0.75 mg/L, respectively. The NOEC and LOEC for population size after exposure to R-11(R) were 0.25 and 0.5 mg/L, respectively. Both of these values were lower than the EEC, indicating that R- 11 does have the potential to cause damage to D. pulex Populations after application at recommended field rates. The wide range of concentrations causing extinction makes it difficult to generalize about the potential impacts that agricultural adjuvants might have on aquatic ecosystems. Therefore, additional Studies that examine effects on other nontarget organisms and determine residues in aquatic ecosystems may be warranted.