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Neonicotinoid Pesticides and Bees - The Food and Environment ...

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It is also vital to underst<strong>and</strong> the disease status of individuals used in pesticide assessments since<br />

both the honeybee (Apis mellifera) <strong>and</strong> the bumble-bee (Bombus terrestris) perform poorly in<br />

proboscis extension reflex (PER) memory tests when their immune systems were challenged by<br />

lipopolysaccharide.<br />

Honeybees are the target of a large number of viruses with a total of 18 identified to date. Often<br />

virus vectoring by Varroa, which is a significant stressor in honeybee colonies by feeding on the<br />

haemolymph causes a variety of physical <strong>and</strong> physiological effects on the colony, <strong>and</strong> results in<br />

infections from viruses which are otherwise present as covert infections resulting in severe disease<br />

<strong>and</strong> mortality within the colony. In addition viruses can be transmitted within the colony by<br />

trophallaxis, contact, faeces <strong>and</strong> salivary gl<strong>and</strong> secretions. However to date there are no reports of<br />

interactions between neonicotinoids <strong>and</strong> viruses<br />

Exposure (update EFSA review) including available data from incident monitoring schemes<br />

<strong>Bees</strong> are exposed to pesticides via a number of routes <strong>and</strong> the relative importance of each<br />

depends on the life stage of the insect <strong>and</strong> the mode of application of the pesticide. Adults may be<br />

exposed directly to pesticides through direct overspray or flying through spray drift, by consumption<br />

of pollen <strong>and</strong> nectar (which may contain directly over-sprayed or systemic residues), by contact<br />

with treated surfaces (such as resting on recently treated leaves or flowers), by contact with dusts<br />

generated during drilling of treated seeds, or by exposure to guttation fluid potentially as a source<br />

of water or as dried residues on the surface of leaves. <strong>The</strong> exposure of larvae is primarily via<br />

processed pollen <strong>and</strong> nectar in brood food. Data available in the literature includes residues in<br />

pollen, wax <strong>and</strong> nectar within colonies, pollen <strong>and</strong> nectar residues from plants, in pollen loads on<br />

bees returning to the hives <strong>and</strong> in adult workers. Such data also includes the residues of<br />

veterinary medicines detected <strong>and</strong> the distribution of chemicals around the hive.<br />

<strong>The</strong> routes of exposure of bees to pesticides has been assessed <strong>and</strong> recently reviewed in an<br />

EFSA Scientific Opinion particularly in relation to quantifying uptake <strong>and</strong> extended to include other<br />

non-Apis species where data were available. <strong>The</strong> exposure of bumble bees to pesticides has also<br />

been reviewed <strong>and</strong> showed there are key times in the year when exposure of queens may be<br />

particularly important in determining the fate of a colony.<br />

A review of residues in bees after pesticide applications in the EFSA review (2012) provides<br />

evidence of the exposure of bees to applications aggregated through all routes of exposure, i.e.<br />

through direct overspray, foraging on treated crops <strong>and</strong> consumption of treated food <strong>and</strong> water as<br />

samples were collected over time after exposure. This showed peak residues in the first sample<br />

after application with declines for spray applications over the following week. No data from<br />

systemic seed or soil application field studies were available but residues of imidacloprid <strong>and</strong> its<br />

<strong>Neonicotinoid</strong> pesticides <strong>and</strong> bees Page 7 of 133<br />

Report to Syngenta Ltd

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