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POLLINATORS POLLINATION AND FOOD PRODUCTION

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THE ASSESSMENT REPORT ON <strong>POLLINATORS</strong>, <strong>POLLINATION</strong> <strong>AND</strong> <strong>FOOD</strong> <strong>PRODUCTION</strong><br />

62<br />

2. DRIVERS OF CHANGE OF <strong>POLLINATORS</strong>,<br />

<strong>POLLINATION</strong> NETWORKS <strong>AND</strong> <strong>POLLINATION</strong><br />

2.3.1.4 Sublethal effects of pesticides on<br />

bees<br />

2.3.1.4.1 Importance of sublethal effects<br />

In addition to the traditional measurements of lethal<br />

effects happening during acute exposure to pesticides,<br />

an increasing number of studies have focused on the<br />

sublethal effects of pesticides on pollinators, since the<br />

1970’s. Sublethal effects are defined as the effects on<br />

individuals that survive exposure (Desneux et al., 2007).<br />

They mainly follow chronic exposure to pesticides, but can<br />

also be a consequence of acute exposure. A pioneering<br />

study by Schricker and Stephen (1970) showed that when<br />

honey bees were exposed to a sublethal dose of parathion,<br />

an organophosphate insecticide, they were unable to<br />

communicate the direction of a food source to other bees.<br />

Using a variety of methods, many studies have shown<br />

the effects of newer classes of insecticides, for instance<br />

pyrethroids (Vandame et al., 1995) and neonicotinoids (Henry<br />

et al., 2012), causing alterations in the navigation of bees<br />

and their orientation to food resources and colony location,<br />

resulting in bee losses. After reviewing the documented<br />

sublethal effects of pesticides on bees, we examine the<br />

Class<br />

Acetylcholinesterase<br />

(AChE) inhibitors<br />

GABA-gated<br />

chloride channel<br />

antagonists<br />

Sodium channel<br />

modulators<br />

Nicotinic<br />

acetylcholine<br />

receptor (nAChR)<br />

agonists<br />

Nicotinic<br />

acetylcholine<br />

receptor (nAChR)<br />

allosteric modulators<br />

Chloride channel<br />

activators<br />

Modulators of<br />

chlordotonal organs<br />

Examples (chemical<br />

subgroup or exemplifying<br />

active ingredient<br />

Organophosphates,<br />

carbamates<br />

Cyclodiene<br />

organochlorines;<br />

phenylpyrazoles<br />

Pyrethroids, pyrethrins;<br />

DDT/methoxychlor<br />

Neonicotinoids; nicotine;<br />

sulfoxaflor; butenolides<br />

Spinosyns<br />

Avermectins, milbemectins<br />

Pymetrozine; flonicamid<br />

Mode of action<br />

Inhibits enzyme which terminates the<br />

action of the excitatory neurotransmitter<br />

acetylcholine at nerve synapses.<br />

Acetylcholine is the major excitatory<br />

neurotransmitter in insects.<br />

Blocks GABA-activated chloride<br />

channel; GABA is the major inhibitory<br />

neurotransmitter in insects<br />

Keep sodium channels open causing<br />

hyperexcitation and in some cases nerve<br />

block. Sodium channels are involved in<br />

the propagation of action potentials along<br />

nerve axons.<br />

Mimic the agonist action of acetylcholine<br />

at nAChR causing hyperexcitation.<br />

Acetylcholine is the major excitatory<br />

neurotransmitter in insects.<br />

Allosterically activate nAChRs causing<br />

hyperexcitation. Acetylcholine is the major<br />

excitatory neurotransmitter in insects.<br />

Allosterically activate glutamate-gated<br />

chloride channels causing paralysis.<br />

Glutamate is an important inhibitory<br />

neurotransmitter in insects<br />

conclusions of the principal reviews on this topic with respect<br />

to the role of sublethal effects of these pesticides in the<br />

decline of bees, and the pollination they provide.<br />

2.3.1.4.2 Range of sublethal effects<br />

An extensive variety of sublethal effects has been<br />

studied, and can be classified into effects at the individual<br />

(physiological and behavioral) and colony levels. We provide<br />

several examples of each detected effect, based on the<br />

principal reviews (Thompson, 2003; Desneux et al., 2007;<br />

Belzunces et al., 2012; Van der Sluijs et al., 2013; Godfray<br />

et al., 2014; Pisa et al., 2014) (see Table 2.3.3).<br />

As shown in Table 2.3.3, there exist a broad variety of<br />

sublethal effects, including individual physiological and<br />

behavioral effects as well as colony-level effects. Most of<br />

these effects have been shown with the honey bee, and<br />

most of the recent studies look at neonicotinoid insecticides<br />

effects. Despite this research, important gaps of knowledge<br />

remain; for example: 1) most studies have been carried<br />

out with honey bees, a few with the bumble bee, Bombus<br />

terrestris, but very few with other social or solitary bee<br />

species (Sandrock et al., 2014) (Table 2.3.3, Figure 2.3.6).<br />

TABLE 2.3.2<br />

Examples of classes. Mode of action and toxicity of insecticides acting on nerve/muscle targets (from IRAC MoA Classification<br />

v7.3 February 2014 http://www.irac-online.org/documents/moa-classification/?ext=pdf)<br />

Stimulate chlordotonal proprioceptors<br />

by an unknown mechanism; impairs fine<br />

motor control, resulting in disruption<br />

of feeding and other behaviours of<br />

Hemiptera and certain other insects<br />

application rate<br />

+ 10’s g ai/ha<br />

++ 100’s of g ai/ha<br />

Example honeybee<br />

LD50 µg a.i. (active<br />

ingredient)/bee*<br />

++ Dimethoate 0.1<br />

+ Fipronil 0.004<br />

(oral lowest)<br />

+ Deltamethrin 0.0015<br />

(contact lowest)<br />

+ Thiacloprid 17.3<br />

(oral lowest)<br />

Imidacloprid 0.0037<br />

(oral lowest)<br />

+ Spinosad 0.0036<br />

(contact lowest)<br />

+ Abamectin 0.002<br />

(contact)<br />

+ Pymetrozine >117<br />

(oral lowest)<br />

* toxicity data from http://www.agritox.anses.fr/php/fiches.php

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