Figure 2. Imidacloprid is transformed in the environment into a number of different compounds, several of which are more toxic to honey bees than imidacloprid itself.4 havioral abnormalities. However, several of the imidacloprid metabolites are equally or more toxic to honey bees. Imidacloprid (Compound A in Figure 2) is transformed through a Type 1 process to 5-hydroxyimidacloprid (Compound B), followed by transfor(Compound C).2 While the hydroxy metabolite B is less toxic than the parent imidacloC is 1.6 times as toxic as imidacloprid to honey bees.3 Toxic transformation products are also a concern with the other neonicotinoids. The insecticide thiamethoxam, for example, is readily converted to clothianidin through a Type 2 process in the environment (Figure 3).5, 6 Also a registered pesticide active ingredient, the clothianidin degradate is more acutely toxic to honey bees than the thiamethoxam parent based on LD50 values. When considering how long a compound lasts in the hive, soil or water, it is important to account for the persistence of both the parent and the degradates. If both the parent and the degradate are highly persistent, the exposure risks remain high for longer than one would predict based on the persistence of the parent compound alone. Unfortunately, information on persistence and toxicity of degradates is not available for many pesticides. US EPA only recently started requiring pesticide manufacturers to submit information on the toxicity of degradates to honey bees, and still does not require submission of persistence data. clothianidin. 666 Figure 4. Keep in mind the message of - When it comes to assessing the scope of a pesticide problem, analysis of plants, pollen, nectar, bees, brood, wax, honey, soil, and water can provide useful information. However, if a full accounting of toxicity is desired, it is important that the analysis also include the transformation products of pesticides that degrade to form more toxic chemicals. Unfortunately, inclusion of degradates is not routine in the “multi-residue screen” provided by most analytical labs. Even the labs that do include the degradates often cannot detect low levels.7 What this means for beekeepers is that a lab analysis report with “ND” (no detection) for the parent compound does not necessarily mean that there were no transformation compound” is a different message than “We didn’t look for it,” so it is important to know what the lab is capable of before sending a sample out for analysis. A recent study shows the pitfalls of analyzing for only the parent compound. Researchers measured the spatial and temporal distribution of imidacloprid after injection into apple trees, focusing only on imidacloprid and not including the toxic metabolites.8 While the study did provide useful data on imidacloprid distribution in apple trees over time, the authors cannot draw any conclusions about the overall toxicity of the apple trees to both pest and pollinating insects be- mean it is not present in the sample. cause they did not measure concentrations of the toxic metabolites. In contrast, another study focused on measuring levels of imidiacloprid and its metabolites over time in forests treated for the hemlock wooly adelgid.9 The researchers found that imidicloprid concentrations peaked 12 months after treatment, but imidaincreased over time and were the highest at the end of the study, 36 months after treatment. The study author also found that the than imidacloprid to the hemlock woolly adelgid. Conclusions A pesticide active ingredient is not the only source of toxicity and, as it degrades over time, the transformation products can contribute to adverse effects. As shown for the neonicotinoids imidacloprid, thiamethoxam and clothianidin, some degradation products are even more toxic to honey bees than the parent active ingredient. As a result, degradation of pesticides in contaminated plants, water and hive materials may not necessarily decrease the risks associated with honey bee exposure to these substances. To gain a more complete picture of the pesticide impacts on bees, it is equally important to measure the concentrations of active ingredients and toxic transformation products. Footnotes 1 Ministry of Agriculture. Environmental Protection – Environmental Fate. British Columbia Ministry of Agriculture. http:// www.agf.gov.bc.ca/pesticides/c_2.htm. 2 Nauen R, Tietjen K, Wagner K, Elbert A. 1998. Imidacloprid against Myzus persicae and Aphis gossypii (Homoptera: Aphididae). Pestic. Sci. 52: 53–57. 3 Suchail S, Guez D, Belzunces LP. 2001. American Bee Journal 4 5 Discrepancy Between Acute and Chronic Toxicity Induced by Imidacloprid and its Metabolites in Apis Mellifera. Environ. Toxicol. Chem. 20: 2482–2486. Reported LD50 values for a single pesticide may vary among multiple studies of bees used as well as other experimental factors. US EPA. 2011. Registration Review: Problem Formulation for the Environmental Fate, Ecological Risk, Endangered Species and Drinking Water Exposure Assessments for Thiamethoxam. US Environmental Protection Agency, December 13, 2011. http://www.regulations. June 2014 6 7 8 gov/#!documentDetail;D=EPA-HQOPP-2011-0581-0003. US EPA. 2011. Registration Review: Problem Formulation for the Environmental Fate and Ecological Risk, Endangered Species, and Drinking Water Exposure Assessments of Clothianidin. US Environmental Protection Agency, December 13, 2011. http://www.regulations.gov/#!documentDetail;D=EPAHQ-OPP-2011-0865-0003. to obtain in pure form for the lab to create standards of known concentration. Reeb PD, Vandervoort C, Garavaglia 9 T, Cregg BM, et al. 2014. Spatial and temporal distribution of trunk-injected imidacloprid in apple tree canopies: Distribution of trunk-injected imidacloprid in apple tree canopy. Pest Management Science n/a–n/a; doi:10.1002/ps.3747. Coots CI, Spatial, temporal, and tritrophic distribution of imidacloprid, on hemlock woolly adelgid, Adelges tsugae Annand, (Hemiptera: Adelgidae). PhD Thesis, Univer- sity of Tennessee, Knoxville, TN (2012). http:// trace.tennessee.edu/cgi/viewcontent. cgi?article=2772&context=utk_ graddiss 667
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