Abstract

Most agricultural soils are expected to be contaminated with agricultural chemicals. As the exposure to pesticides can have adverse effects on non-target organisms, avoiding contaminated areas would be advantageous on an individual level, but could lead to a chemical landscape fragmentation with disadvantages on the metapopulation level. We investigated the avoidance behavior of juvenile common toads (Bufo bufo) in response to seven pesticide formulations commonly used in German vineyards. We used test arenas filled with silica sand and oversprayed half of each with different pesticide formulations. We placed a toad in the middle of an arena, filmed its behavior over 24 hours, calculated the proportion of time a toad spent on the contaminated side and compared it to a random side choice. We found evidence for the avoidance of the folpet formulation Folpan® 500 SC, the metrafenone formulation Vivando® and the glyphosate formulation Taifun® forte at maximum recommended field rates for vine and a trend for avoidance of Wettable Sulphur Stulln (sulphur). No avoidance was observed when testing Folpan® 80 WDG (folpet), Funguran® progress (copper hydroxide), SpinTorTM (spinosad), or 10% of the maximum field rate of any formulation tested. In the choice-tests in which we observed an avoidance, toads also showed higher activity on the contaminated side of the arena. As video analysis with tracking software is not always feasible, we further tested the effect of reducing the sampling interval for manual data analyses. We showed that one data point every 15 or 60 minutes results in a risk of overlooking a weak avoidance behavior, but still allows to verify the absence/presence of an avoidance for six out of seven formulations. Our findings are important for an upcoming pesticide risk assessment for amphibians and could be a template for future standardized tests.

Highlights

  • About 40% of the area of the European Union is agriculturally used [1], making agriculture the dominant type of landscape in many regions

  • The control-test revealed neither a preference for any cardinal direction (i north = 49.2%, interquartile range (IQR) = 30.0–71.9%; Wilcoxon test vs. 50%: V = 72, p = 0.860; i west = 51.2%, 29.9–61.9%; V = 74, p = 0.782; n = 16 in all tests) nor for the side orientated to the wall (i wall = 39.4%, 26.6–69.6%; V = 63, p = 0.821) or to the other arena (i arena = 41.9, 28.7–52.2%; V = 44, p = 0.231) over 24 hours

  • The reduction of the sampling interval did not result in significant differences in the proportion of time spent on the contaminated side, with the exception of tpest_60 in Taifun1 forte

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Summary

Objectives

We aimed to minimize the variance of the body weight within an experimental run

Methods
Results
Conclusion
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