Apis cerana Is Less Sensitive to Most Neonicotinoids, Despite of Their Smaller Body Mass.

Multiple stressors and interaction between them may be responsible for the decline of global pollinators. Among them, exposure to neonicotinoids has been getting more attention and has been considered as a main stressor. The Western honey bee (Apis mellifera L.) (Hymenoptera: Apidae) and Chinese indigenous honey bee (Apis cerana F.) (Hymenoptera: Apidae) are two managed honey bee species in China. These two species are widely used in beekeeping, and many wild A. cerana is widely spread in forests and contributes to the ecosystem. It is predicated that A. cerana is more sensitive to insecticides than A. mellifera due to their smaller mass. Here, we found that although the body mass of A. cerana is significantly lower than A. mellifera, the sensitivity of the two species to neonicotinoids are not associated with their body mass but depended on the chemical structure of neonicotinoids. To dinotefuran, the two species showed the similar sensitivity. To acetamiprid, A. mellifera was less sensitive than A. cerana. However, to imidacloprid and thiamethoxam, A. mellifera was more sensitive than A. cerana. These results suggested that the sensitivity of honey bees to neonicotinoids is closely associated with the structure of pesticides, but not with body mass of bees. It is also indicated that the hazards of pesticides to the different pollinators could not be inferred from one species to another.

[1]  H. Thompson Extrapolation of acute toxicity across bee species , 2016, Integrated environmental assessment and management.

[2]  S. Buckland,et al.  Neonicotinoids target distinct nicotinic acetylcholine receptors and neurons, leading to differential risks to bumblebees , 2016, Scientific Reports.

[3]  R. Danka,et al.  Genetics, Synergists, and Age Affect Insecticide Sensitivity of the Honey Bee, Apis mellifera , 2015, PloS one.

[4]  R. Nauen,et al.  The global status of insect resistance to neonicotinoid insecticides. , 2015, Pesticide biochemistry and physiology.

[5]  I. Fries,et al.  Seed coating with a neonicotinoid insecticide negatively affects wild bees , 2015, Nature.

[6]  Erin Jo Tiedeken,et al.  Bees prefer foods containing neonicotinoid pesticides , 2015, Nature.

[7]  D. Goulson,et al.  Bee declines driven by combined stress from parasites, pesticides, and lack of flowers , 2015, Science.

[8]  R. Thapa,et al.  Comparative Foraging Behavior of Apis Cerana F. and Apis Mellifera L. in Rapeseed under Cage Condition in Chitwan, Nepal , 2014 .

[9]  C. Downs,et al.  Effects of neonicotinoids and fipronil on non-target invertebrates , 2014, Environmental Science and Pollution Research.

[10]  K. Goka,et al.  Pesticide Residues and Bees – A Risk Assessment , 2014, PloS one.

[11]  A. Fairbrother,et al.  Risks of neonicotinoid insecticides to honeybees , 2014, Environmental toxicology and chemistry.

[12]  F. Sgolastra,et al.  A meta-analysis comparing the sensitivity of bees to pesticides , 2014, Ecotoxicology.

[13]  D. Goulson,et al.  Emerging dangers: deadly effects of an emergent parasite in a new pollinator host. , 2013, Journal of invertebrate pathology.

[14]  J. Ellis,et al.  Gene expression in honey bee (Apis mellifera) larvae exposed to pesticides and Varroa mites (Varroa destructor). , 2012, Journal of insect physiology.

[15]  D. vanEngelsdorp,et al.  Dietary traces of neonicotinoid pesticides as a cause of population declines in honey bees: an evaluation by Hill's epidemiological criteria. , 2012, Pest management science.

[16]  B. Oldroyd,et al.  Differences in foraging and broodnest temperature in the honey bees Apis cerana and A. mellifera , 2012, Apidologie.

[17]  Kelvin Balcombe,et al.  Pollination services in the UK: how important are honeybees? , 2011 .

[18]  D. Biron,et al.  Exposure to Sublethal Doses of Fipronil and Thiacloprid Highly Increases Mortality of Honeybees Previously Infected by Nosema ceranae , 2011, PloS one.

[19]  J. Frazier,et al.  High Levels of Miticides and Agrochemicals in North American Apiaries: Implications for Honey Bee Health , 2010, PloS one.

[20]  F. Hu,et al.  Sensitivities of three bumblebee species to four pesticides applied commonly in greenhouses in China , 2010 .

[21]  A. Klein,et al.  Importance of pollinators in changing landscapes for world crops , 2007, Proceedings of the Royal Society B: Biological Sciences.

[22]  D. Abrol,et al.  Contact Toxicity of Some Insecticides to Honeybee Apis mellifera (L) and Apis cerana (F.) , 2005 .

[23]  J. Devillers,et al.  Comparative toxicity and hazards of pesticides to Apis and non-Apis bees. A chemometrical study , 2003, SAR and QSAR in environmental research.

[24]  S. Buckingham,et al.  Neonicotinoids: insecticides acting on insect nicotinic acetylcholine receptors. , 2001, Trends in pharmacological sciences.

[25]  J. G. Scott,et al.  Cytochromes P450 and insecticide resistance. , 1999, Insect biochemistry and molecular biology.

[26]  T. Rinderer,et al.  Comparative Toxicities of Four Topically Applied Insecticides to Africanized and European Honey Bees (Hymenoptera: Apidae) , 1986 .

[27]  K. Ulm,et al.  Influence of pollen feeding and physiological condition on pesticide sensitivity of the honey bee Apis mellifera carnica , 1983, Oecologia.

[28]  S. Jain,et al.  Evaluation of pesticide toxicity at their field recommended doses to honeybees, Apis cerana and A. mellifera through laboratory, semi-field and field studies. , 2015, Chemosphere.

[29]  J. P. V. D. Sluijs,et al.  Effets des néonicotinoïdes et du fipronil sur les invertébrés , 2015 .

[30]  Selvisabhanayakam,et al.  PHYSICO-CHEMICAL ANALYSIS OF HONEY OF APIS CERANA INDICA AND APIS MELLIFERA FROM DIFFERENT REGIONS OF ANANTNAG DISTRICT, JAMMU & KASHMIR , 2013 .

[31]  Daniela Laurino,et al.  Toxicity of neonicotinoid insecticides on different honey bee genotypes , 2013 .

[32]  Luo Shudong Evaluation the Toxicity of Five Pesticides to Two Species of Bumblebees , 2013 .

[33]  Z. Huang Pollen nutrition affects honey bee stress resistance , 2012 .

[34]  G. Trewartha,et al.  Opus: University of Bath Online Publication Store Open Peer Review , 2012 .

[35]  Daniela Laurino,et al.  ACUTE ORAL TOXICITY OF NEONICOTINOIDS ON DIFFERENT HONEY BEE STRAINS , 2010 .

[36]  Luo Shu-dong Evaluation the Oral Toxicity of Four Pyrethroids Pesticides to Bombus hypocrita , 2009 .

[37]  Ji Rong From introduced species to invasive species-a case study on the Italian bee Apis mellifera L. , 2003 .

[38]  G. Robinson,et al.  Juvenile hormone in adult eusocial Hymenoptera: gonadotropin and behavioral pacemaker. , 1997, Archives of insect biochemistry and physiology.

[39]  G. Robinson,et al.  Regulation of honey bee division of labor by colony age demography , 1996, Behavioral Ecology and Sociobiology.

[40]  R. S. Chandel,et al.  Effects of diflubenzuron and penfluron on workers of Apis cerana indica F and Apis mellifera L , 1995 .

[41]  Van der Steen,et al.  Method development for the determination of the contact LD50 of pesticides for bumble bees (Bombus terrestris L.) , 1994 .

[42]  F. Ruttner,et al.  EXPERIMENTAL ANALYSIS OF REPRODUCTIVE INTERSPECIES ISOLATION OF APIS MELLIFERA L. AND APIS CERANA FABR , 1983 .