Hatching of Echinostoma trivolvis miracidia in response to snail host and non-host chemical cues.

Environmental cues are used by many organisms to time life history transitions and can be important for trematode host location. However, while much is understood about how larval trematodes locate hosts, much less is known about the potential role of host cues in the timing of trematode egg development and hatching. We addressed the potential role of host chemical cues in mediating hatching of Echinostoma trivolvis miracidia by comparing hatching in response to cues from the first intermediate host (the snail Planorbella trivolvis), a non-host snail (the snail Goniobasis proxima), and a non-host invertebrate (earthworm, Lumbricus terrestris). We hypothesized that in the presence of cues from their first intermediate host, E. trivolvis would hatch sooner and would be more synchronized than when host cues were absent. However, we found that hatching was unaffected by our cue treatments. In all treatments, hatching uniformly began at 13 days and was nearly evenly spread over the next 3 weeks.

Tadpole size, cholinesterase activity, and swim speed in four frog species after exposure to sub-lethal concentrations of chlorpyrifos.

While physiological biomarkers exist to verify exposure of amphibians in natural populations to agricultural chemicals, the ecological relevance of changes in these parameters is often difficult to determine. We compare the relationship between tadpole cholinesterase (ChE; a common enzymatic biomarker of exposure to OP pesticides) and measures of size and swim speed in four native North American species of anurans (Hyla chrysoscelis, Rana sphenocephala, Acris crepitans, and Gastrophryne olivacea). We used four environmentally realistic levels (1, 10, 100 and 200microg/l) of a commonly used organophosphate pesticide (OP), chlorpyrifos, and examined tadpole response at the conclusion of 4 days of exposure. We further examined if the presence or absence of pond sediment influenced tadpole responses, and, in two species, we determined how a 12-day exposure influenced responses. We found species-specific differences in response to the pesticide, with H. chrsysoscelis and G. olivacea being most sensitive; however, the levels of inhibition of ChE activity were generally not sufficient to exert an effect on swim speed as we measured it. Generally, tadpole mass was reduced 20-35% in the highest concentration after 4 days of exposure. We found the presence of sediment to influence these responses, although the effects were not consistent among species. Given these differences in ecologically relevant responses, we recommend exercising caution when making generalizations across different anuran amphibian taxa regarding responses to pesticide exposure.

Cholinesterase activity and behavior in chlorpyrifos-exposed Rana sphenocephala tadpoles.

Recent studies have found a correlation between organophosphate (OP) pesticide exposure and declines in amphibian populations. We evaluated the hypothesis that this relationship is driven by behavioral changes in developing larvae. Specifically, we examined how exposure to a common OP pesticide, chlorpyrifos, influenced cholinesterase (ChE) activity, mass, and swim speed in Rana sphenocephala tadpoles. We also determined how the presence of natural pond sediments in exposure chambers influenced response to the pesticide and how mass and survival were affected when tadpoles were exposed to an invertebrate (odonate) predator in addition to the pesticide. Mass and swim speed were measured after 4- and 12-d laboratory exposures to 1, 10, 100, and 200 microg/L of chlorpyrifos in test chambers that either did or did not contain pond sediments. These same parameters also were examined in mesocosms dosed with 200 microg/L of chlorpyrifos to evaluate responses under more environmentally realistic conditions. The effect of the invertebrate predators on survival and/or growth of tadpoles was evaluated in the mesocosm study and in separate laboratory experiments. In laboratory tests, no pesticide-induced mortality was observed; however, tadpole ChE activity in the two highest concentrations was significantly lowered, with a longer exposure duration further decreasing activity (maximum inhibition, 43%). Mass also was lower at higher concentrations, but this effect was not enhanced with longer duration of exposure. Reductions in ChE activity of tadpoles exposed in mesocosms were similar to those observed in laboratory experiments for the first 4 d. Tadpole swim speed and survival in the presence of a predator were not affected, with the latter largely resulting from pesticide-induced predator mortality.