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Non-target effects of neonicotinoid seed treatments; mortality of coccinellid larvae related to zoophytophagy

Third and fourth instar Harmonia axyridis Pallas larvae feed directly on corn seedlings; therefore they may be at risk if the seedlings are chemically treated. Neonicotinoids are broad-spectrum systemic insecticides that are frequently applied to corn seeds prior to planting to protect seedlings from early-season root and leaf-feeding. In this study, H. axyridis larvae were exposed for 360 min to corn seedlings that had been grown from seeds treated with either thiamethoxam or clothianidin. Neurotoxic symptoms (trembling, paralysis, and loss of coordination) were observed in 72% of the H. axyridis larvae; recovery following neurotoxic symptoms rarely occurred (7%). Starvation of larvae for 48 h prior to seedling exposure may increase tissue consumption; however, there was no difference in the number of starved or satiated larvae that displayed neurotoxic symptoms and died. Neurotoxic symptoms and larval mortality were significantly more likely to occur if larvae were exposed to seedlings grown from seeds treated with neonicotinoids compared to the control. In addition, clothianidin resulted in significantly greater larval mortality (80%) compared to thiamethoxam (53%). Symptoms and mortality were rarely observed if seedlings were not treated with a neonicotinoid seed treatment (3% and 3%, respectively). Coccinellids are abundant in agroecosystems in which neonicotinoid seed treatments are likely to be applied. Therefore, the use of neonicotinoids may have negative effects on these non-target species if early-season leaf-feeding occurs in the field.

Adverse effects of soil applied insecticides on the predatory coccinellid Hippodamia undecimnotata

We studied, under laboratory conditions, the possible effects of sublethal doses of two soil applied insecticides (carbofuran and imidacloprid) on development, survival and fecundity of the predator Hippodamia undecimnotata. For studies, predator fed upon Aphis fabae that was reared on Vicia faba plants treated with the systemic carbofuran and imidacloprid. Survival of immature stages in insecticides treatments (67.6% and 52.2%, for carbofuran and imidacloprid, respectively) was lower than control (77.4%). Both insecticides did not affect significantly total immature developmental time, while carbofuran caused a significant reduction of adult weight. Adult average longevity was significantly higher for the control than the insecticides treatments. Moreover, females oviposited fewer eggs in both insecticide treatments than the control (33% and 55% reduction in average fecundity for imidacloprid and carbofuran, respectively). Population increase parameters were also adversely affected by insecticides application. The importance of the adverse effect of sublethal doses of systemic insecticides on designing and management of insects’ pests are discussed.

Acute and delayed effects of thiacloprid on seven freshwater arthropods

Ecotoxicological risk assessment of contaminants often is based on toxicity tests with continuous-exposure profiles. However, input of many contaminants (e.g., insecticides) to surface waters typically occurs in pulses rather than continuously. Neonicotinoids are a new group of insecticides, and little is known about their toxicity to nontarget freshwater organisms and potential effects on freshwater ecosystems. The aim of the present research was to assess effects of short-term (24-h) exposure to the neonicotinoid insecticide thiacloprid, including a postexposure observation period. A comparison of several freshwater insect and crustacean species showed an increase of sensitivity by three orders of magnitude in the following order: Daphnia magna < Asellus aquaticus = Gammarus pulex < Simpetrum striolatum < Culex pipiens = Notidobia ciliaris = Simulium latigonium, with median lethal concentrations (LC50s) of 4,400, 153, 190, 31.2, 6.78, 5.47, and 5.76 μg/L, respectively (postexposure observation 11–30 d). Thiacloprid caused delayed lethal and sublethal effects, which were observed after 4 to 12 d following exposure. Reduction in LC50s found when postexposure observation was extended from 1 d to a longer period (11–30 d) was up to >50-fold. Hence, delayed effects occurring after short-term exposure should be considered in risk assessment. The 5% hazardous concentration (HC5) of thiacloprid obtained in the present study (0.72 μg/L) is more than one order of magnitude below the currently predicted worst-case environmental concentrations in surface water. Concerning the selection of test organisms, we observed that the widely employed test organism D. magna is least sensitive among the arthropods tested and that, for neonicotinoid insecticides, an insect like the mosquito C. pipiens would be more suitable for predicting effects on sensitive species.

Pesticides linked to bee decline

The UK Government and retailers are under pressure to impose a ban on sale of pesticides linked to bee population decline following new research which groups call a 'growing body of evidence'. Environmental groups including the Soil Association and Buglife are making a renewed call for an end to the use of neonicotinoid pesticides, which are among the most commonly used pesticides worldwide, after a new study linked them to a decline in bee populations.

Minute quantities of imidacloprid may induce bee decline in the long run

For many years environmental groups and beekeepers´ organizations have been pushing for a ban on neonicotinoid pesticides which are linked to bee decline across the world. In a recent study, The toxicity of neonicotinoid insecticides to arthropods is reinforced by exposure time, the Dutch toxicologist Henk Tennekes demonstrates that the long-term risks associated with the insecticides imidacloprid and thiacloprid are far greater than hitherto thought. Honeybees, bumblebees and many other insects are being slowly poisoned to death by these persistent insecticides. Small doses accumulate over time, meaning that there is no safe level of exposure. The study was published on the 23rd of July 2010 in the journal Toxicology (online).

The toxicity of neonicotinoid insecticides to arthropods is reinforced by exposure time

There is a very important shift in our understanding of the risk of neonicotinoid insecticides. Their risk may increase exponentially over time, rendering even very small amounts of neonicotinoids much more toxic than previously realized. Dutch researcher Dr. Henk Tennekes, with Dr. Francisco Sanchez-Bayo of Australia, have recently published a review article in the Journal of Environmental & Analytical Toxicology: "Time-Dependent Toxicity of Neonicotinoids and Other Toxicants: Implications for a New Approach to Risk Assessment" (attached). Their starting point is the Druckrey–Küpfmüller equation dt^n = constant (where d = daily dose and t = exposure time-to-effect, with n>1) for chemical carcinogens. The Druckrey–Küpfmüller equation established in the early 1960s explains why toxicity may occur after prolonged exposure to very low toxicant levels. In essence, this equation states that the total dose required to produce the same effect decreases with decreasing exposure levels, even though the exposure times required to produce the same effect increase with decreasing exposure levels. Druckrey and Küpfmüller inferred in the late 1940s that if both receptor binding and the effect are irreversible, exposure time would reinforce the effect. Recently, similar dose–response characteristics have been established for the toxicity of the neonicotinoid insecticides imidacloprid and thiacloprid to arthropods. Imidacloprid was the first highly effective insecticide whose mode of action has been found to derive from almost complete and virtually irreversible blockage of postsynaptic nicotinic acetylcholine receptors (nAChRs) in the central nervous system of insects. Imidacloprid mimics the action of acetylcholine, but unlike acetylcholine, imidacloprid is not deactivated by acetylcholinesterase and thus persistently activates nAChRs. Chronic exposure of insects to imidacloprid therefore leads to cumulative and virtually irreversible blockage of nAChRs in their central nervous system, which play roles in many cognitive processes.
An example of the consequences for insects in the case of imidacloprid is given in Table 5 (attached). Since imidacloprid and other neonicotinoid insecticides have time-dependent effects on arthropods, the risk of foraging worker bees feeding on tiny levels of residues becomes an issue that cannot and should not be ignored. In the example shown here, 50% of worker bees would die within 7-12 days if feeding on a field where 11% of plants have residues of imidacloprid in the specified range (Table 5). By contrast, standard hazard quotients (HQ) for dietary NOEL of 20 microgram per Litre are misleading because they suggest that imidacloprid poses no danger to honey bees. Given that honey bee workers can live up to a few months in winter time the NEC (No Effect Concentration) for imidacloprid is estimated as close to zero, which means that any residue concentration found in pollen will have a lethal effect provided there is sufficient time of exposure.

Pesticides fingered in UK honeybee wipeout - Further suspicion falls on neonicotinoids

A new study appears to have confirmed suspicions that the neonicotinoid group of pesticides is in part responsible for the dramatic decline in UK honeybee numbers, the Telegraph reports. Insect research charity Buglife and the Soil Association "brought together a number of peer-reviewed pieces of research" which demonstrate that neonicotinoids "damage the health and life cycle of bees over the long term by affecting the nervous system". Matt Shardlow, Buglife chief exec, said: “Other countries have already introduced bans to prevent neonicotinoids from harming bees. This is the most comprehensive review of the scientific evidence yet and it has revealed the disturbing amount of damage these poisons can cause." Peter Melchett, director of the Soil Association, added: “The UK is notorious for taking the most relaxed approach to pesticide safety in the EU. Buglife’s report shows that this puts at risk pollination services vital for UK agriculture."

Parallel Declines in Pollinators and Insect-Pollinated Plants in Britain and the Netherlands

Despite widespread concern about declines in pollination services, little is known about the patterns of change in most pollinator assemblages. By studying bee and hoverfly assemblages in Britain and the Netherlands, we found evidence of declines (pre-versus post-1980) in local bee diversity in both countries; however, divergent trends were observed in hoverflies. Depending on the assemblage and location, pollinator declines were most frequent in habitat and flower specialists, in univoltine species, and/or in nonmigrants. In conjunction with this evidence, outcrossing plant species that are reliant on the declining pollinators have themselves declined relative to other plant species. Taken together, these findings strongly suggest a causal connection between local extinctions of functionally linked plant and pollinator species.

The decline of the Kentish Plover in the Dutch Delta relates to insect decline and surface water contamination with imidacloprid

The population of the Kentish Plover Charadrius alexandrinus in the Netherlands has declined from 700-900 pairs in 1973-1977 to 180-210 pairs in 2008, three-quarters of which were breeding in the Dutch Delta area. Reproductive success of the Kentish Plover in the Delta area in 2000-2005 was on average only 0.39 chicks per pair per year, which is far too low to sustain the population. The most recently recorded (2007-2008) decline of the Kentish Plover population in the Delta area (estimated at 144 pairs in 2008) can be attributed to a large extent to changes in the breeding populations in the Grevelingen lake area, which showed a decline from 91 pairs in 2007 to 59 pairs in 2008. In its most important breeding area (Slikken van Flakkee) there was a decline from 62 pairs in 2007 to 32 pairs in 2008, which coincides with recent decline of the Red-listed bumblebee Bombus muscorum in this area (several dozens were sighted in 2005, but only 1 in 2009) and possibly other wild bee species as well. In addition, there is evidence of insecticide (imidacloprid and carbendazim) contamination of surface water in 2007 on the island of Goeree-Overflakkee, i.e. in the vicinity of the Slikken van Flakkee, at levels that are bound to be toxic to insects.

The decline of the Whinchat and Northern Wheatear on Dutch heath land relates to decline of ground beetles

The Dwingelderveld National Park, located in the province of Drenthe in the north-eastern part of the Netherlands, is a heath and woodland reserve of 3,700 hectares, with 1500 ha of wet heath land, which makes it the largest wet heath land in western Europe. Sjouke van Essen surveyed the ground beetles (Coleoptera : Carabidae ) on 38 locations in the Dwingelderveld reserve in 1991 and 2008, in exactly the same manner, and observed a massive decline in the number of caught ground beetles, from 45,000 (94 species) in 1991 to 15,000 (79 species) in 2008. Within the same period there was a dramatic decline of the insectivorous Whinchat Saxicola rubetra (from 35 pairs in 1989 to 6-14 pairs in 1998-2003) and Northern Wheatear Oenanthe oenanthe (from 33 pairs in 1993 to just 3 in 2003) in the Dwingelderveld reserve.