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Natural variation in insecticide resistance among zooplankton populations

Insecticide resistance is a well-studied phenomenon that we have know about since the pioneering work of A.L. Melander in 1914.  The vast majority of this work has been done on pest species due to the monetary incentive behind ensuring the efficacy of the insecticide in question, but we also know that non-target species are also inadvertently exposed to these chemicals.  My first studies examined patterns of natural variation in insecticide resistance among zooplankton populations collected far from and near agriculture.  In these studies, we used laboratory LC50 tests (which determine the concentration of a chemical required to cause 50% mortality of your test population) to test for variation to a commonly applied insecticide and correlated this data with the amount of agriculture surrounding each individual pond.

Community-wide effects of insecticide resistance in zooplankton assemblages

Moving from the smaller-scale, single species toxicity tests, my next area of research involved crossing experimental communities with different zooplankton populations that differed only in the naturally-occurring population level resistance to a commonly applied insecticide (see above experiment).  In this experiment, we set up identical communities and only manipulated the genetics of the zooplankton within each experimental community by adding the same number of zooplankton but from different ponds where we had already determined that there was naturally-occurring variation to the insecticide in question.  Other similar community studies usually do not manipulate the population genetics of their zooplankton and stock all communities with the same clone or set of clones to limit the amount of variation within experimental communities.  However, this does not reflect what we see in nature as some populations of zooplankton are naturally more resistant to insecticides due to their close proximity to nearby agricultural fields.  Whereas communities with sensitive zooplankton (that may be naive to these chemicals) are subjected to dramatic trophic cascades through the loss of zooplankton and subsequent phytoplankton blooms, communities with resistant zooplankton are almost entirely buffered from the adverse effects of insecticides.

Cross-resistance to insecticides in zooplankton and its community-wide effects

Often when target pest species evolve resistance to a particular agrochemical, they also develop resistance to other chemicals with similar chemical structures or modes of action (i.e. how an insecticide kills or inactivates the pest species).  Cross-resistance, however, is far less often studied in non-target organisms.  We have tested the resistance of naturally-occurring populations of Daphnia pulex that we know varied in their resistance to chlorpyrifos (an organophostphate insecticide),  to a number of other insecticides with similar or different modes of action.   After running a series of smaller laboratory LC50 studies to determine if there was evidence of cross-resistance, we used the same populations that we had been working with in previous community studies.  Again, we set up identical aquatic communities and only manipulated the genetics of the zooplankton within each communities.  The communities were crossed with various concentrations of 5 different insecticides.  This was the largest experiment ever conducted by the Relyea lab as we were monitoring 200 individual aquatic communities for roughly 3 months.

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