Beneficial organisms like the honey bee, Apis mellifera L. (Hymenoptera: Apidae), are heavily affected by pest control practices that incorporate insecticides. Safer alternatives as the spinosad-based formulation GF-120 have been developed to overcome this issue. Though both the low concentration of spinosad and the ultra-low-volume application rate of GF-120 are supposed to have a low acute toxicity in honey bee foragers, to our knowledge such claims have not been explicitly proven. We thus carried out a series of experiments to assess the effect of GF-120, malathion, and Spintor (spinosad) on honey bee foragers when applied at two concentrations (80 and 1,500 ppm) and two application rates (low density rate [LDR]—80 drops of 5 mm diameter per square meter; high density rate [HDR]—thousands of 200 -µm-diameter droplets per square meter). Interestingly, the three pesticides caused low mortality on foragers when applied at LDR-80, LDR-1,500, or HDR-80. However, HDR-1,500 caused a very high mortality. Based upon these results, we developed a computer program to estimate the average number of foragers that are exposed at LDR and HDR. We found that more foragers receive a lethal dose when exposed at HDR than at the other rates. Our results support the hypothesis that the impact of GF-120 and malathion upon honey bees is minimal when applied at LDR and that computer simulation can help greatly in understanding the effects of pesticides upon nontarget species.

Stingless bees (Apidae, Meliponini) are key pollinators in natural and agricultural Pantropical environments. Current human activities, however, threaten their populations, making it urgent to assesstheir abundance and genetic status. By a population genetics approach, we calculated the genetic diversity and estimated the number of wild colonies of two stingless bee species, Trigona nigerrima (Cresson) and T. corvina (Cockerell) in southern Mexico. Allele richness ranged from 10 to 19 (mean ± SD = 14 ± 3.5) for both species. Expected heterozygosity ranged 0.88-0.93 for T. corvina and 0.82-0.92 for T. nigerrima. The estimated number of colonies estimated was 25 on average for T. corvina and 21 for T. nigerrima. According to our results populations of both species seem not to be in danger. We also show that genetic tools can be extremely useful for colony density estimation for stingless bees as it is for bumble bees and honey bees.

Agroecosystem management commonly involves the use of pesticides. As a result, a heterogeneous landscape is created, in which suitable and unsuitable spaces are defined by the absence/presence of pesticides. In this study, we explored how foragers of the honey bee, Apis mellifera L., adapt to such context. We specifically evaluated the effect of GF-120, a spinosad-based fruit fly toxic bait, on the allocation of foragers between food sources under the hypothesis that foragers will move from food sources with GF-120 to food sources without it. We thus carried out three experiments: in experiment 1, a group of foragers was trained to collect honey solution from a feeder; next, this feeder offered a GF-120/honey solution. A minority of foragers continued collecting the GF-120/honey solution. In experiment 2, we trained two groups of foragers from a colony to two food sources equally rewarding. Next, GF-120 was added to one of the food sources. We found that the majority of foragers moved from the GF-120-treated feeder to the feeder without GF-120 and that the minority that continued visiting the GF-120-treated feeder did not collect the GF-120/honey solution. In a third experiment, we wanted to know if foragers in an experimental setup as in experiment 1 would perform waggle dances: none of the foragers that collected GF-120/honey were observed dancing. Our results emphasize the importance of "food refuges" for non-target species, since they minimize the impact of agrochemicals upon them.