The Effects of Crop Protection Pesticides on Honey Bee Forager Survival
Honey bees (Apis mellifera) account for most of the approximately $16 billion in bee pollination services contributed annually to agriculture in the United States (Calderone 2012, Zhu et al. 2015). Among the many crops pollinated by honey bees is almond, which relies almost entirely on honey bees for pollination (Klein et al. 2012). The almond industry in California produces about 80 percent of the almonds consumed worldwide (Klein et al. 2012) and employs approximately 60 percent of all managed honey bee hives to provide pollination services during the crop’s bloom in mid to late winter (Sumner & Boriss 2006). In protecting almond orchards from various pests and pathogens, heavy chemical treatments are employed during bloom (Bosch and Blas 1994). Despite their ubiquitous use, the effects on honey bee health of the various pesticides used repeatedly in almond orchards are not well understood. In particular, only a handful of studies looking at the effects on honey bees of fungicide formulations in almonds have been reported to negatively impact brood survival and induce sub-lethal effects on thermoregulation in adult workers (Mussen 2013, Mussen et al. 2004, Vandamme and Belzunces 1998). In addition, synergistic effects of select fungicides and insecticides on worker and colony mortality have been reported (Pilling and Jepson 1993, Johnson et al. 2013). Recently, an examination of various pesticides including insecticides, a fungicide and a herbicide in other crop systems such as cotton, rice and corn, revealed significant negative impacts of these chemicals on worker survival (Zhu et al. 2015). Because honey bees exhibit age-based division of labor, only workers over 21 days of age, serve as foragers (Huang and Robinson 1996, Abou-Shaara 2014). Therefore foragers, as the only workers that spend time outside the hive, comprise the age group susceptible to direct exposure to agro-chemical applications or contact with residues left over from such applications.
Goals and Objectives
Our main aim is to examine if crop protection pesticides used in almond orchards affect honey bee forager survival. To accomplish our goal we will work in collaboration with Dr. Clint Hoffmann of the US Department of Agriculture – Agriculture Research Service (USDA-ARS). The objectives, null hypotheses (H0) and alternative hypotheses (HA) are outlined as follows:
Objective 1. To examine the effects of commercially available almond protection fungicides iprodione, Pristine®, Quadris® and their synergisms on honey bee forager survival
H0: Exposure to these fungicides, individually and in various combinations, does not affect forager survival
HA: Exposure to these fungicides, individually and in various combinations, significantly decreases forager survival
Objective 2. To assess the effects of the insect growth regulator (IGR) insecticides buprofezin, flubendiamide, diflubenzuron, methoxyfenoizide, pyriproxofen and their synergisms (when applied in various combinations) on honey bee forager survival
H0: Exposure to these IGRs, individually and in various combinations, does not affect forager survival
HA: Exposure to these IGRs, individually and in various combinations, significantly decreases forager survival
Objective 3. To examine the effects of the herbicides carfentrazone, oxyfluorfen, glufosinate and their synergisms (when applied in various combinations) on honey bee forager survival
H0: Exposure to these herbicides, individually and in various combinations, does not affect forager survival
HA: Exposure to these herbicides, individually and in various combinations, significantly decreases forager survival
Honey bee forager exposure to select pesticides (fungicides, IGRs and herbicides) used in almond orchards during bloom will be conducted through the use of a wind tunnel/atomizer setup adjusted to a wind-speed of 2.9 m/s. Foragers will be collected from the research apiary at the Texas A&M University Riverside Campus, pesticide exposure will occur at the Aerial Application Technology Laboratory of the USDA-ARS located at the Riverside Campus
Honey bee foragers will be collected from designated hives where bees occupying frames containing food resources, devoid of brood, will be selected for collection. Such frames will be targeted due to a higher incidence of older bees, including foragers, which take on tasks involving food collection and unloading rather than brood maintenance, the task of younger workers. The bees on the appropriate frames will then be gently brushed off the frame into bioassay cages composed of a circular cardboard frame, holding rings and mesh side panels. Approximately 40-50 foragers will be loaded into each bioassay cage with 6-10 bioassay cages allocated to each experimental group.
Bioassay cages loaded with foragers will be divided into distinct groups consisting of a control group and several treatment groups formulated to test the individual and combined effects of select pesticides in each treatment group. Labeled bioassay cages will then be loaded one at a time onto a holding fork near one end of the wind tunnel chamber. A nitrogen tank will serve to propagate pesticides diluted in water and sprayed at concentrations corresponding to the label dose of each select pesticide. Approximately 10 ml of each pesticide solution will be loaded into a twin fluid atomizer located near the opposing end of the wind tunnel chamber. A 10 ml syringe will be used to transfer the pesticide solution through a plastic tube attached directly to the atomizer. The aforementioned nitrogen tank and wind tunnel fans will then be activated to propel pesticide solution through the atomizer for approximately 5 seconds for each application. The bioassay cage will then be removed from the holding fork and the atomizer will be cleansed with acetone before the next bioassay cage is loaded. This process will be repeated for all bioassay cages allocated to each treatment group, the control group bioassay cages will be loaded into the wind tunnel but will be spared pesticide exposure, they will instead be sprayed with water propagated through the atomizer.
Monitoring Forager Survival.
Following the application of pesticide treatments foragers in each bioassay cage will be transferred to a correspondingly labeled plastic containment unit (~1 quart in volume) containing strips of wax foundation attached to the side and bottom of the unit. A wide brimmed funnel will be placed over a containment unit then one of the holding rings on a bioassay cage will be removed to facilitate transfer. The bioassay cage will then be secured over the funnel and one of the mesh side panels will be removed allowing foragers in the bioassay cage to migrate into the containment unit. Each containment unit will then be gently shaken and a lid swiftly placed over the containment unit securing the foragers within. This process will be repeated until all foragers in each bioassay cage have been transferred to corresponding containment units. A pair of 1.5 ml Eppendorf tubes will be inserted into pre-made holes in the lid of each containment unit. The Eppendorf tubes will serve as feeders and water dispensers. Feeder tubes will be loaded with approx. 1 ml of sugar syrup composed of a 50:50 mixture of water and sucrose, water dispensing tubes will be loaded with approx. 1 ml of water. The containment units will be kept in an incubator set at 34.5oC and ~75% relative humidity. Each containment unit will be monitored on a daily basis, the first day will include two checks one 8 hours after treatment, to monitor any acute effects of the treatment, and a second 24 hours after treatment. The units will be checked every 24 hours for the following nine days and the number of bee deaths will be compiled and compared for each experimental group to assess the potential effects of exposure to various pesticides and pesticide combinations on forager survival
Preliminary Results and Future Goals
Thus far we have tested the effects of the fungicides iprodione, Pristine® and Quadris® on honey bee forager survival. Our initial results seem to indicate that iprodione, applied at variations of the label rate, significantly impacts forager survival compared to untreated groups (Fig. 1). Analysis of these select fungicides is ongoing and we intend to expand our study to include select insect growth regulators and herbicides used in almond orchards. Looking beyond our assessment of forager survival, we also aim to investigate larger colony-wide effects. Studies examining the effects of fungicides on brood survival have specifically implicated contaminated pollen as the source of transmission of toxic substances to bee larvae (Mussen 2013, Mussen et al. 2004). While we anticipate a measurable impact on forager survival resulting from exposure to various pesticides, such studies reveal the potential for foragers to inadvertently contribute to colony decline regardless of the harmful effects they may incur. In future exposure trials we will seek to further assess the interaction between pesticide exposure and forager survival as well as the dynamic of potential forager introduction of toxic substances into the hive.
Fig. 1. Effects of Iprodione variants and synergisms on forager survival
Abou-Shaara HF. 2014. The foraging behaviour of honey bees, Apis mellifera: a review.
Veterinarni Medicina (59): 1–10
Bosch J and Blas M. 1994. Foraging behaviour and pollination efficiency of Osmia cornuta and
Apis mellifera on almond (Hymenoptera, Megachilidae and Apidae). Applied
Entomology and Zoology (29): 1-9.
Calderone NW. 2012. Insect pollinated crops, insect pollinators and US agriculture: Trend
analysis of aggregate data for the period 1992–2009. PLoS ONE 7: e37235.
Huang ZY and Robinson GE. 1996. Regulation of honey bee division of labor by colony age
demography. Behav. Ecol. Sociobiol. (39) : 147–158.
Johnson RM, Purcell EG. 2013. Effect of ‘Bee-Safe’ insecticides and fungicides on honey
bee queen development and survival. Poster presented at 2nd International Conference on Pollinator Biology, Health and Policy, Aug. 14–17, 2013, Pennsylvania State University
Klein AM, Brittain C, Hendrix SD, Thorp R, Williams N and Kremen C. 2012. Wild pollination
services to California almond rely on semi-natural habitat. J. Appl. Ecol. (49): 723–732
Mussen EC. 2013. Problems with almond bloom sprays. University of California Cooperative
Mussen EC, Lopez JE and Peng CYS. 2004. Effects of selected fungicides on growth and
development of larval honey bees, Apis mellifera L. (Hymenoptera: Apidae). Environ. Entomol. (33): 1151-1154
Pilling ED and Jepson PC. 1993. Synergism between EBI fungicides and a pyrethroid insecticide
in the honeybee (Apis mellifera). Pesticide Science (39): 293-297
Sumner DA and Boriss H. 2006. Bee-conomics and the Leap in Pollination Fees. Foundation of
Agricultural Economics 9-11.
Vandamme R and Belzunces LP. 1998. Joint actions of deltamethrin and azole fungicides on
honey bee thermoregulation. Neurosci. Letters (251): 57-60.
Zhu YC, Adamcyzk J, Rinderer T, Yao J, Danka R, Luttrell R and Gore J. 2015. Spray Toxicity
and Risk Potential of 42 Commonly Used Formulations of Row Crop Pesticides to Adult Honey Bees (Hymenoptera: Apidae). J. Econ. Entomol. DOI: 10.1093/jee/tov269.