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Data to support Minucci et al. 2021 Ecological Applications
The U.S. Environmental Protection Agency (USEPA) and U.S. Department of Agriculture (USDA) are developing the VarroaPop+Pesticide model which simulates the dynamics of honey bee colonies and how they respond to multiple stressors, including weather, Varroa mites and pesticides. To evaluate this model, we used Approximate Bayesian Computation to fit field data from an empirical study where honey bee colonies were fed the insecticide clothianidin. Model input data (Minucci 2021a) are available on Figshare: https://doi.org/10.6084/m9.figshare.c.5402901.v1. Scripts (Minucci 2021b) to run this analysis are available on Zenodo: https://doi.org/10.5281/zenodo.4721797. This dataset is associated with the following publication: Minucci, J., R.J. Curry, G. DeGrandi-Hoffman, C. Douglass, K. Garber, and S. Purucker. Inferring pesticide toxicity to honey bees from a field-based feeding study using a colony model and Bayesian inference. ECOLOGICAL APPLICATIONS. Ecological Society of America, Ithaca, NY, USA, 31(8): e02442, (2021).
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Varroapop sensitivity analysis scripts and output
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Code repository for scripts and model output associated with sensitivity analysis of the VarroaPop honeybee hive simulation model. This dataset is associated with the following publication: Kuan, C., G. DeGrandi-Hoffman, R. Curry, K. Garber, A. Kanarek, M. Snyder, K. Wolfe, and T. Purucker. Sensitivity analyses for simulating pesticide impacts on honey bee colonies. ENVIRONMENTAL MODELLING AND SOFTWARE. Elsevier Science Ltd, New York, NY, USA, 376: 15-27, (2018).
Pollen and honeybee neonicotinoid exposure data and analyses
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Data on the presence of corn seed treatment insecticides in bee-collected pollen and increased honey bee mortality associated with corn planting, persistence of the insecticides inside honey bee colonies, and long-term growth of these colonies in central Ohio. We also constructed spatial models, based on empirical data of honey bee foraging and dispersion patterns of planter dust, and landscape compositions, to simulate hypothesized exposure routes via contamination of foraging resources and aerial exposure resulting from flight through localized dust plumes from planters and diffuse dust in the landscape over all resulting from widespread planting activity. Insecticide concentrations under different hypothesized exposure routes were then compared with the observed levels of contamination to evaluate these hypotheses. This dataset is associated with the following publication: Kuan, C., G. DeGrandi-Hoffman, R. Curry, K. Garber, A. Kanarek, M. Snyder, K. Wolfe, and T. Purucker. Sensitivity analyses for simulating pesticide impacts on honey bee colonies. ENVIRONMENTAL MODELLING AND SOFTWARE. Elsevier Science Ltd, New York, NY, USA, 376: 15-27, (2018).
Honey bee (Apis mellifera) and Varroa mite (Varroa destructor) toxicity data
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,Toxicological data generated for Apis mellifera honey bees and an ectoparasitic mite (Varroa destructor) in laboratory toxicity trials are presented. Data were generated over a four-year period by members of the Varroacide Research and Testing Team (VRTT) as part of a foundational grant from the Foundation for Food and Agricultural Research (FFAR). Data may be used to explore toxicological responses of honey bees and Varroa mites to a wide range of natural and synthetic chemical treatments against Varroa infestations in honey bee colonies. Data may be collected and analyzed together with other data sets not generated by VRTT.,,
Using Pop-GUIDE to Assess the Applicability of MCnest for Relative Risk of Pesticides to Hummingbirds
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- Text description of regulatory methods for estimating nectar and pollen concentrations from soil applications and seed treatments; - Table S1: Parameter set for imidacloprid used for simulations to assess the relative risk of neonicotinoid pesticides to hummingbirds. - Table S2: Full sensitivity results for ruby-throated hummingbird exposure to imidacloprid simulation - Table S3: Data used for estimating the Mineau scaling factor for imidacloprid. This dataset is associated with the following publication: Etterson, M., E. Paulukonis, and S. Purucker. Using Pop-GUIDE to Assess the Applicability of MCnest for Relative Risk of Pesticides to Hummingbirds. Ecologies. MDPI, Basel, SWITZERLAND, 4(1): 171-194, (2023).
Mechanistic modeling of insecticide risks to breeding birds in North American agroecosystems
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This dataset provides all parameter values necessary to replicate the TIM/MCnest model analysis reported in the manuscript "Mechanistic modeling of insecticide risks to breeding birds in North American agroecosystems". This dataset is associated with the following publication: Etterson, M., K. Garber, and E. Odenkirchen. Mechanistic modeling of insecticide risks to breeding birds in North American agroecosystems. PLoS ONE. Public Library of Science, CA, USA, 1-23, (2017).
Data from: Adapting overwintering honey bee (Apis mellifera L.) colony management in response to warmer fall temperatures associated with climate change
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,The data represent estimates of honey bee colony sizes expressed as combs (frames) of adult bees and combs of brood (eggs, larvae and pupae). Colony sizes were estimated by dividing combs into one-tenth sections and counting the number covered with bees or brood on both sides of a comb. The values from each comb were summed and used as an estimate of combs with bees or brood for each colony. During pre-cold storage measurement in October, colonies were comprised of two deep Langstroth hive boxes. Temperatures were below 10o C so the one-tenth of the comb area method for comb evaluations was not used. Instead, estimates of adult bee populations were made by tilting the top hive body forward on the pallet and frames with at least 75% bee coverage on the top and bottom of the comb were counted as a comb of bees. In the lower hive body, adult populations were estimated from adult bees covering the top of the combs. Combs with bees were totaled for the colony as an estimate of colony size. Estimates of Varroa mites (Varroa destructor Anderson & Trueman) per 100 adult bees were made using approximately 300 worker bees per colony that were brushed from brood comb into jars containing 50 ml of 70% ethanol. Mites were counted by vigorously shaking the sample jars, and pouring the bees and alcohol into a strainer positioned over a pan. The mites that went through the strainer and into the pan were counted. Bees in the strainer also were examined for mites. All the bees in the sample were counted to estimate mites per 100 bees. Nosema (Vairimorpha (Microsporidia: Nosematidae) spore counts per colony were based on samples of 20 bees per colony. Samples were placed in a test tube containing ultra-pure water and homogenized for 5s. Samples equilibrated in 30-60 s, and the supernatant was removed from the center of the sample in the test tube (clear area) and placed into a 1.5ml Eppendorf tube. Spores per colony was estimated by transferring a 15 µl sample of supernatant to a hemocytometer, and examining it using a compound microscope at 400x with phase-contrast lighting. Nosema spores were counted in 16 small squares within five larger squares. The final spore count was calculated by multiplying the hemocytometer counts by 50,000. Fat body metrics (weight and lipid and protein concentrations) are based on pooled samples of 10 bees per colony. Fat bodies were removed by placing an adult worker bee onto a block of dry ice, and removing the abdomen. The entire gut was removed and the remaining abdominal carcass with fat body attached was rinsed to remove remaining gut contents and blotted dry. Fat body weight was estimated after drying the abdominal carcass at 60oC for four days. Fat body protein concentration was estimated with a BCA Protein Assay kit. Samples were analyzed in triplicate and read in a microplate reader at a wave length of 562nm. The absorbance values of blank wells were subtracted from each standard and sample. Protein concentration (µg/µl) was estimated using the absorbance and standard curve. Lipid concentrations were estimated by placing the fat body sample into a tube containing a 2:1 mixture of chloroform:methanol (1 ml) along with 210 µl of 0.25% KCI. The sample was vortexed, and centrifuged at 2,000 rpm for 15 min. The bottom chloroform layer was removed and placed into a 2ml glass screw cap vial. Serial dilutions of corn oil dissolved in chloroform were prepared to construct a standard curve for lipid concentrations. The negative control consisted of 100 µl of chloroform. Samples, standards, and the negative control were dried to completion for approximately 1.5h. Dried samples were reacted with 182 µl of concentrated sulfuric acid at 100oC for 15 min and 1478 µl of vanillin-phosphoric acid for 15 min in the dark at room temperature. Each of the negative controls, standards, and samples (100µl) were plated in triplicate and read using a spectrophotometer at 525nm. The average absorbance value for the negative control
Data used in analyses for "A comparison of pollen and syrup exposure routes in Bombus impatiens microcolonies: implications for pesticide risk assessment"
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Data used in "A comparison of pollen and syrup exposure routes in Bombus impatiens microcolonies: implications for pesticide risk assessment". This dataset is associated with the following publication: Weitekamp, C., R. Koethe, and D. Lehmann. A comparison of pollen and syrup exposure routes in Bombus impatiens (hymenoptera: apidae) microcolonies: implications for pesticide risk assessment. ENVIRONMENTAL ENTOMOLOGY. Entomological Society of America, Lantham, MD, USA, 51(3): 613-620, (2022).
Raw data for imidacloprid effects on native bees
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,Field and Lab data regarding the effects of 4 sublethal concentrations of a neonicotinoid insecticide (Imidacloprid) on honey bees and about a dozen native bee species.,,