I'm no expert on this topic but these studies below seem convincing even if they were done by the 
chemical industry. Perhaps the experiments are flawed ....anyone care to comment? OR does 
anyone have data that shows opposite conclusions? 

From what I can determine corn and cotton in the US are the most likely large plots of 
Imidacloprid treated crops in the USA.  While the material has other labeled uses corn and cotton 
appear to be the big tonnage.  Thus I don't find the hand wringing and speculation swirling 
around Imidacloprid very convincing especially when the corn & cotton belt in the USA has been 
quite absent from any large unexplained bee losses aka CCD.



This paper is from Bayer

Uptake, translocation and metabolism of imidacloprid in plants 

http://www.bulletinofinsectology.org/pdfarticles/vol56-2003-035-040sur.pdf

Conslusions

More than 15 studies with imidacloprid have been car- 
ried out concerning uptake, translocation and metabo- 
lism in various plant species mainly after foliar, soil or 
seed treatment. The uptake after soil or seed treatment is 
about 5% of the applied dose and the a.s. shows good 
acropetal mobility within the xylem and poor basipetal 
translocation within the phloem. Three principal meta- 
bolic pathways of imidacloprid in plants were identified 
showing a quick degradation of the a.s., especially after 
seed or soil application. The findings of the metabolism 
studies show a clear and consistent picture. It can be 
concluded that in nearly all crops the metabolic pathway 
of imidacloprid runs via the same three routes and re- 
sults in qualitative and quantitative similar composition 
of the metabolic spectrum. All identified metabolites 
still contain the 6-chloropicolyl moiety of imidacloprid. 
Hence, the relevant residue to be analysed in field resi- 
due trials can be defined as the sum of imidacloprid and 
its metabolites containing the 6-chloropicolyl moiety, 
expressed as imidacloprid. 

The nature of the residue in bee-relevant matrices of 
oilseeds (sunflower nectar and pollen) was determined 
to consist of the parent compound imidacloprid only. 
Field residue trials with imidacloprid after seed-dressing 
of sunflower, corn and rape revealed that no residues 
above the limit of quantitation of the residue analytical 
method were present in pollen and nectar. 


an older study from Bayer with similar results

http://www3.interscience.wiley.com/cgi-bin/abstract/77005622/ABSTRACT

Abstract
In a greenhouse metabolism study, sunflowers were seed-treated with radiolabelled imidacloprid 
in a 700 g kg-1 WS formulation (Gaucho® WS 70) at 0.7 mg AI per seed, and the nature of the 
resulting residues in nectar and pollen was determined. Only the parent compound and no 
metabolites were detected in nectar and pollen of these seed-treated sunflower plants (limit of 
detection <0.001 mg kg-1). In standard LD50 laboratory tests, imidacloprid showed high oral 
toxicity to honeybees (Apis mellifera), with LD50 values between 3.7 and 40.9 ng per bee, 
corresponding to a lethal food concentration between 0.14 and 1.57 mg kg-1. The residue level 
of imidacloprid in nectar and pollen of seed-treated sunflower plants in the field was negligible. 
Under field-growing conditions no residues were detected (limit of detection: 0.0015 mg kg-1) in 
either nectar or pollen. There were also no detectable residues in nectar and pollen of sunflowers 
planted as a succeeding crop in soils which previously had been cropped with imidacloprid seed-
treated plants.
Chronic feeding experiments with sunflower honey fortified with 0.002, 0.005, 0.010 and 0.020 
mg kg-1 imidacloprid were conducted to assess potential long-term adverse effects on honeybee 
colonies. Testing end-points in this 39-day feeding study were mortality, feeding activity, 
wax/comb production, breeding performance and colony vitality. Even at the highest test 
concentration, imidacloprid showed no adverse effects on the development of the exposed bee 
colonies. This no-adverse-effect concentration of 0.020 mg kg-1 compares with a field residue 
level of less than 0.0015 mg kg-1 ( =  limit of detection in the field residue studies) which clearly 
shows that a sunflower seed dressing with imidacloprid poses no risk to honeybees. This 
conclusion is confirmed by observations made in more than 10 field studies and several tunnel 
tests




and a French study

Experimental study on the toxicity of imidacloprid given in syrup to honey bee (Apis mellifera) 
colonies

http://www3.interscience.wiley.com/cgi-bin/abstract/109630841/ABSTRACT

ABSTRACT
Two groups of eight honey bee colonies were fed with two different concentrations of 
imidacloprid in saccharose syrup during summer (each colony was given 1 litre of saccharose 
syrup containing 0.5 µg litre-1 or 5 µg litre-1 of imidacloprid on 13 occasions). Their 
development and survival were followed in parallel with control hives (unfed or fed with 
saccharose syrup) until the end of the following winter. The parameters followed were: adult bee 
activity (number of bee entering the hive and pollen carrying activity), adult bee population level, 
capped brood area, frequency of parasitic and other diseases, mortality, number of frames with 
brood after wintering and a global score of colonies after wintering. The only parameters linked to 
feeding with imidacloprid-supplemented saccharose syrup when compared with feeding with 
non-supplemented syrup were: a statistically non-significant higher activity index of adult bees, a 
significantly higher frequency of pollen carrying during the feeding period and a larger number of 
capped brood cells. When imidacloprid was no longer applied, activity and pollen carrying were 
re-established at a similar level for all groups. Repeated feeding with syrup supplemented with 
imidacloprid did not provoke any immediate or any delayed mortality before, during or following 
the next winter, whereas such severe effects are described by several French bee keepers as a 
consequence of imidacloprid use for seed dressing in neighbouring cultures. In any case, during 
the whole study, mortality was very low in all groups, with no difference between imidacloprid-fed 
and control colonies. Further research should now address several hypotheses: the troubles 
described by bee keepers have causes other than imidacloprid; if such troubles are really due to 
this insecticide, they may only be observed either when bees consume contaminated pollen, when 
no other sources of food are available, in the presence of synergic factors (that still need to be 
identified), with some particular races of bees or when colonies are not strong and healthy. 
Copyright © 2004 Society of Chemical Industry

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